Search PubMed⌕ Search

SEARCH · Search PubMed

Results for “Simazine”

Search indexed PubMed citations on genomics, clinical trials, systematic reviews and public health. Explore titles, authors and supplied subject terms, then open the PubMed record.

Quote a phrase for an exact phrase match. Source license links do not imply unrestricted reuse.

At least 37 records · Page 2Linked to original sources

Simazine biodegradation in soil: analysis of bacterial community structure by in situ hybridization.

Pesticide and nitrate contamination of soil and groundwater from agriculture is an environmental and public health concern worldwide. Simazine, 6-chloro-N2,N4-diethyl-1,3,5-triazine-2,4-diamine, is a triazine herbicide used in agriculture for selective weed control with several types of crops and it is frequently applied to soils receiving N-fertilizers. Degradation experiments were performed in the laboratory to assess whether the biodegradation of simazine in soil may be influenced by the presence of urea. Simazine degradation rates under different experimental conditions (presence/absence of urea, microbiologically active/sterilized soil) were assessed together with the formation, degradation and transformation of its main metabolites in soil. Simazine degradation was affected by the presence of urea, in terms both of a smaller half-life (t(1/2)) and of a higher amount of desethyl-simazine formed. The soil bacterial community was also studied. Microbial abundances were determined by epifluorescence direct counting. Moreover in situ hybridization with rRNA-targeted fluorescent oligonucleotide probes was used to analyze the bacterial community structure. Fluorescent in situ hybridization (FISH) was used to detect specific groups of bacteria such as the alpha,beta,gamma-subdivisions of Proteobacteria, Gram-positive bacteria with a high G + C DNA content, Planctomycetes, Betaproteobacterial ammonia-oxidizing bacteria and nitrifying bacteria. The presence of the herbicide and/or urea affected the bacterial community structure, showing that FISH is a valuable tool for determining the response of bacterial populations to different environmental conditions.

Bacteria↗

Atrazine and simazine degradation in Pennisetum rhizosphere.

The ability of rhizosphere of four plant species to promote the degradation of charcoal-fixed atrazine and simazine in cement blocks of a long-term contaminated soil when mixed with a normal soil at 1:1 ratio was tested. Of the four selected plants viz., rye grass (Lolium perenne), tall fescue (Festuca arundinacae), Pennisetum (Pennisetum clandestinum) and a spring onion (Allium sp.) used in this study, only P. clandestinum was able to survive in herbicide contaminated soil while other plants died within few days after germination/transplanting. Both atrazine and simazine were degraded at a faster rate in contaminated soil planted to P. clandestinum than in unplanted soil. Within 80 days, nearly 45% and 52% of atrazine and simazine, respectively, were degraded in soil planted to P. clandestinum while only 22% and 20% of the respective herbicide were degraded in the unplanted soil. During 80-day experimental period, both microbial biomass and soil dehydrogenase activity were significantly increased (7-fold) in soil planted to P. clandestinum over that in unplanted soil. The suspension of contaminated rhizosphere soil, planted to P. clandestinum exhibited an exceptional capability to degrade both atrazine (300 microg) and simazine (50 microg) in a mineral salts medium over that of non-rhizosphere soil suspension. Results indicate that P. clandestinum, a C4 plant, may be useful for remediation of soils contaminated with atrazine and simazine.

Atrazine↗

Controlled release of the herbicide simazine from computationally designed molecularly imprinted polymers.

The present study describes the development of materials suitable for environmental control of algae. Molecularly imprinted polymers (MIPs) were used as simazine carriers able to provide the controlled release of simazine into water. Three polymers were designed using computational modelling. The selection of methacrylic acid (MA) and hydroxyethyl methacrylate (HEM) as functional monomers was based on results obtained using the Leapfrog algorithm. A cross-linked polymer made without functional monomers was also prepared and tested as a control. The release of simazine from all three polymers was studied. It was shown that the presence of functional monomers is important for polymer affinity and for controlled release of herbicide. The speed of release of herbicide correlated with the calculated binding characteristics. The high-affinity MA-based polymer released approximately 2% and the low-affinity HEM-based polymer released approximately 27% of the template over 25 days. The kinetics of simazine release from HEM-based polymer show that total saturation of an aqueous environment could be achieved over a period of 3 weeks and this corresponds to the maximal simazine solubility in water. The possible use of these types of polymers in the field of controlled release is discussed.

Eukaryota↗

Persistence of simazine and terbuthylazine in a semiarid soil after organic amendment with urban sewage sludge.

The persistence of two herbicides, simazine and terbuthylazine, and appearance of their principal dealkylated chloro-s-triazine metabolites have been studied in agricultural soil after the addition of urban sewage sludge as organic amendment. Both herbicides and metabolites were monitored during long-term laboratory incubation (140 days) and analyzed by gas chromatography with a nitrogen-phosphorus detector (GC-NPD). Residues were confirmed by gas chromatography with a mass selective detector (GC-MSD). A sonication microextraction method was used to extract the compounds. The organic amendments used were urban sewage sludge and the humic fraction of this sludge, to increase the organic matter content of the soil from 1% to 2%. For both compounds, simazine and terbuthylazine, the degradation began earlier in the amended soils. Simazine showed a higher dissipation rate than terbuthylazine, the percentage of the former at the end of the experiment being lower than 2% in all cases, while for terbuthylazine the corresponding percentage ranged from 5% to 46%. Organic amendment, mainly its humic fraction, caused a certain stabilization of terbuthylazine in the soil, but did not greatly influence the residual amount of simazine at the end of the experiment. The periodic aeration of the soil caused a greater degradation in the case of terbuthylazine. Only mono-deethylsimazine and deethylterbuthylazine were isolated from the soil during the time the experiment lasted, while the di-deethylated metabolite of simazine was not found.

Agriculture↗

Homogenous catalyzed ozonation of simazine. Effect of Mn(II) and Fe(II).

Simazine, [2-chloro, 4,6-bis(ethylamino)-1,3,5-s-triazine], a common herbicide typically found in surface and ground water was ozonised by using catalytic amounts of Mn(II) and Fe(II). An optimum value for metal concentration was found in the process. Some inhibition of the simazine degradation rate was observed when these metals were added above the optimum concentration. The pH of the reaction media played a significant role in the simazine oxidation rate. Thus, an increase in simazine conversion was observed when the pH was raised from 5 to 9. However, the catalytic effect of added manganese was negligible at the highest pH used in this study (pH 9). The beneficial influence of Fe(II) was also observed when utilising the combination of ozone and hydrogen peroxide. Contrarily, Mn(II) presented a negative influence on simazine conversion when using this oxidation technology.

Catalysis↗

Influence of soil properties on bioaccumulation of 14C-simazine in earthworms Eisenia foetida.

The toxicity of pesticides has been evaluated by several methods including tests with earthworms in both artificial and natural soils treated with the compounds. The ecological niches of earthworms make them good bioindicators of soil contamination. The bioaccumulation of 14C-simazine (6-chloro-N2-N4-diethyl- 1,3,5-triazine-2,4-diamine) was evaluated in earthworms (Eisenia foetida) maintained during three months in two substrates with different physical-chemical characteristics. The substrates were treated with 3.0 mg and 330 kBq of 14C-simazine kg(-1) substrate. Results indicated that worms did not influence simazine dissipation in both substrates as indicated by similar recoveries and with no statistical differences with and without earthworms. The radiocarbon recoveries were 86.8 and 95.3%, respectively in the substrates with lower and higher organic matter contents with earthworms, and 91.0 and 107.4% in the same substrates without worms. However, in earthworms the recoveries were statistically higher when they were maintained in the substrate with lower amount of organic matter (0.89%) than from the higher one (0.33%). Consequently, 14C-simazine bioconcentration factor (BCF) was also greater in the substrate with lower organic matter (6.89+/-1.55) than in the substrate with higher organic matter content (0.88+/-0.06). The results suggest that the higher soil organic matter content will cause lower probability of contamination of soil organisms with simazine.

Animals↗

Simazine and metolachlor removal by subsurface flow constructed wetlands.

A subsurface flow constructed wetlands system was used in this pilot-scale field study to treat runoff from a container nursery. The goal of the study was to determine the statistical significance of certain factors on the removal of simazine (2-chloro-4,6-bis[ethylamino]-s-triazine) and metolachlor (2-chloro-N-[2-ethyl-6-methylphenyl]-N-[2-methoxy-1-methylethyl] acetamide). The factors analyzed included the hydraulic flowrate, media depth, cell aspect ratio, and the presence or absence of Scirpus validus. Analysis of variance using the general linear model procedure determined that vegetation and flowrate significantly (alpha = 0.05) affected herbicide mass removal. The results showed that vegetated subsurface flow cells generally remove more simazine and metolachlor than nonvegetated cells. Decreasing the hydraulic loading rate and, therefore, the areal simazine mass loading rate to vegetated cells from 1659 to 415 mg/m2 caused an increase in the percentage of total mass removed from approximately 60 to 96%. Similarly, metolachlor mass removal percentage increased from approximately 62 to 96% when the areal mass loading to vegetated cells decreased from 1037 to 260 mg/m2. Media depth and aspect ratio did not significantly (alpha = 0.05) affect effluent simazine and metolachlor concentrations. Peak effluent metolachlor concentrations were less than 300 microg/L from vegetated cells receiving hydraulic loading rates of 204 and 102 m3/d x ha. Peak simazine concentrations in the effluent of cells receiving similar hydraulic loadings were approximately 1400 and 750 microg/L (204 and 102 m3/d x ha), respectively.

Herbicides↗

Determination of atrazine, deethylatrazine and simazine in water at parts-per-trillion levels using solid-phase extraction and gas chromatography/ion trap mass spectrometry.

Methods for trace analysis of atrazine and simazine in water have been developed by using stable-isotope dilution with detection by gas chromatography/mass spectrometry. D(5)-Atrazine was used as the internal standard for the determination of atrazine and deethylatrazine, while (13)C(3)-simazine was used for simazine analysis. Water samples were fortified with known amounts of the internal standards and submitted to solid-phase extraction with a C(18) bonded-silica cartridge. A gas chromatograph coupled with an ion-trap mass spectrometer was used to analyze the water sample extracts. Method detection limits were 38 parts-per-trillion (ppt) for atrazine and deethylatrazine and 75 ppt for simazine. The accuracy of the method, represented by relative analytical errors, was less than 15%, and the method precision was less than 5% (relative standard deviation, n = 9). The method was successfully applied to analyze surface water samples collected from a reservoir and a river at ppt levels.

Atrazine↗

Chlorophyll a fluorescence and photosynthetic activity as tools for the evaluation of simazine toxicity to Protosiphon botryoides and Anabaena variabilis.

On studying the effect of simazine on Protosiphon botryoides and Anabaena variabilis, data revealed that chlorophyll a content and dry weight were decreased with the increase in simazine concentration. High concentration of simazine (0.8 mg L(-1)) reduced gross photosynthesis and carbohydrate content, whereas protein content and respiration rate were increased. Algal cell recovery from simazine toxic effect occurred after 2 and 4 days for Anabaena and Protosiphon, respectively, which may be attributed to the difference in algal genotype of the tested organisms.

Anabaena↗

Behaviour of simazine in soil amended with the final residue of the olive-oil extraction process.

Addition of organic wastes to agricultural soils is becoming a common practice as a disposal strategy and to improve the physical and chemical soil properties. However, in order to optimise the use of organic wastes as soil amendments, their effect on the behaviour of other compounds that are also used in agriculture, such as pesticides, needs to be assessed. In this work, we have investigated the effects of the addition of the final solid residue of the new technology of olive-oil extraction (extracted alperujo or solid olive-mill waste, SOMW2) on the sorption, degradation and leaching of the herbicide simazine in a sandy loam soil. The results are compared with those of a previous study, where the intermediary by-product of the olive-oil processing technology (unextracted alperujo or SOMW1) was applied to the same soil. The soil was amended in the laboratory with SOMW2 at two different rates (5% and 10% w/w). Simazine sorption isotherms showed a great increase in herbicide sorption after SOMW2 addition to soil. SOMW2 addition also increased sorption irreversibility. Incubation studies revealed reduced biodegradation of simazine in the soil amended with SOMW2 compared to the unamended soil. Breakthrough curves of simazine in handpacked soil columns showed that SOMW2 addition retarded the vertical movement of the herbicide through the soil and greatly reduced the amount of herbicide available for leaching. Interestingly, the results were quantitatively different from those obtained for the intermediary by-product SOMW1, illustrating the importance of the specific characteristics of the organic amendment in determining its effect on pesticide behaviour.

Adsorption↗

Investigations on the binding mechanism of the herbicide simazine to dissolved organic matter in leachates of compost.

14C-labelled simazine was composted together with biowaste on a pilot (m3) scale. The herbicide was quickly bound to the compost matrix. By aqueous extraction of 29 and 200 days old compost (equivalent to thermophilic and mesophilic phase of composting) only 4.2% and 3.1% respectively of the radioactivity in the compost samples could be extracted with water. Analysis of the extracts using high-performance size exclusion chromatography (HPSEC) revealed that the dissolved organic matter (DOM) had molecular weights ranging between 2 and 28 kDa. The amount of DOM-associated radioactivity increased from 53% (day 29) to 65% (day 200) of total extractable radioactivity. The type of binding of the 14C-labelled residues and the DOM was elucidated by silylation of humic matter and subsequent HPSEC. The data demonstrated that besides polar metabolites also intact simazine was bound to the DOM. A distinct shift from rather weak interactions to strong covalent linkages of simazine and its metabolites with increasing age of the compost was observed. The results showed that only low amounts of free simazine and its degradates can be extracted with water. We concluded that the shift towards stable covalent linkages is equivalent to a detoxification of the contaminant in aged compost. Consequently, the use of the analysed compost in its mature stage should not pose an environmental risk to the groundwater or the subsoil.

Carbon Radioisotopes↗

Integrated optical surface plasmon resonance immunoprobe for simazine detection.

This paper presents the detailed design and characterisation of a regenerable integrated optical surface plasmon resonance immunoprobe as a detector for the triazine herbicide simazine. A sensor design theoretically optimised for use in the aqueous environment is presented and its fabrication described. Experimental results on the sensitivity to changes in bulk refractive index of the analyte and on non-specific binding of ovalbumin are presented. Binding inhibition immunoassays were conducted for simazine and the lower limit of detection determined to be 0.16 microgram/l using anti-simazine IgG antibodies and 0.11 microgram/l using anti-simazine Fab fragments. A sample test cycle of 20 min was established.

Biosensing Techniques↗

Immunoassay techniques for detection of the herbicide simazine based on use of oppositely charged water-soluble polyelectrolytes.

Linear water-soluble polyelectrolytes, i.e., poly(methacrylate) polyanion and poly(N-ethyl-4-vinylpyridinium) polycation, were used as carriers for the reactants in immunoassay. The strength of ionic forces through distance and the cooperative binding of oppositely charged chains, the carriers interact with each other at an extremely high rate and affinity. These properties of the polyelectrolytes made it possible to carry out the immunochemical steps of the assay in true solution and then to quickly separate the resulting products from the reaction mixtures. The above approach was applied to an assay for the herbicide simazine. Both enzyme-linked immunosorbent assay (ELISA) and dot blot formats of the immunoassay were evaluated. In the ELISA format, the polycation was adsorbed on the surface of a microtiter plate. A tracer antigen (simazine) was allowed to interact in solution with components of the reaction mixture containing simazine-peroxidase conjugate, specific antibodies, and staphylococcal protein A conjugated with the polyanion, and then the mixture was added to the immobilized polycation. Quick separation of the immunoreactants was achieved due to formation of interpolyelectrolyte complexes between polycation and polyanion molecules. After washing, the microplate wells were filled with a solution of substrate, and the optical density of the reaction products was measured. In the second format, a solution of the same reaction mixture (after incubation) was filtered through a porous membrane, with the polycation adsorbed. The subsequent addition of substrate led to the development of colored spots. Sensitivity of the dot blot format was close to that of the traditional ELISA format using the same reactants, i.e., 0.5 ng/mL. However, the assay was much faster (assay time decreased from 100-120 to 45 min). Sensitivities of the dot immunoassay were 1 ng/mL for densitometric detection and 10 ng/mL for visual detection with a duration of 20 min. The techniques developed here were used for simazine determination in water, milk, and juices.

Electrolytes↗

Adsorption of the herbicide simazine by montmorillonite modified with natural organic cations.

Three organic cations with a natural origin (L-carnitine, L-cystine dimethyl ester, and thiamine) were introduced at different loadings in the interlayer of a low-charge montmorillonite, and the performance of the modified clays as adsorbents of the herbicide simazine was investigated using batch adsorption-desorption experiments. The organic cations were selected on the basis of their natural origin and the presence of diverse functional groups in their structures, which was expected to influence simazine adsorption. Elemental analysis and spectroscopy results demonstrated the presence of the organic cations in the modified montmorillonites and their entrance in the clay mineral interlayers. Batch adsorption results showed that modification with thiamine (K(f) = 96-138), cystine dimethyl ester (K(f) = 400-753), and especially carnitine (K(f) > 10 000) enhanced the adsorption of simazine by montmorillonite (K(f) = 28-47). It appeared that the specific interlayer microenvironment provided by the functional groups of each organic cation was an important factor controlling the adsorption efficiency of the modified clays. For carnitine and cystine dimethyl ester, the increase in simazine adsorption was considerably greater than that observed after montmorillonite modification with "classical" alkylammonium cations, such as phenyltrimethylammonium or hexadecyltrimethylammonium. This illustrated how modification of smectitic clay minerals with natural organic cations containing appropriate functional groups can be a useful strategy to improve the performance of organoclays for the removal of specific organic pollutants from the environment.

Adsorption↗

Kinetics of simazine advanced oxidation in water.

Comparison of the effects and kinetics of UV photolysis and four advanced oxidation systems (ozone, ozone/hydrogen peroxide, ozone/UV radiation and UV radiation/hydrogen peroxide) for the removal of simazine from water has been investigated. At the conditions applied, the order of reactivity was ozone < ozone/hydrogen peroxide < UV radiation < ozone/UV radiation and UV radiation/hydrogen peroxide. Rate constants of the reactions between ozone and simazine and hydroxyl radical and simazine were found to be 8.7 M-1s-1 and 2.1 x 10(9) M-1s-1, respectively. Also, a quantum yield of 0.06 mol.photon-1 was found for simazine at 254 nm UV radiation. The high value of the quantum yield corroborated the importance of the direct photolysis process. Percentage contributions of direct reaction with ozone, reaction with hydroxyl radicals and direct photolysis were also quantified.

Herbicides↗

[Liver steatosis and disorders of mitochondrial oxidative phosphorylation after experimental administration of simazine].

BACKGROUND: Triazine herbicides are widely used in extensive agricultural production, however, some ecological and health hazards occur due to water and food contamination. AIM: The aim of this study was to evaluate the effects of long-term simazine feeding on the steatosis development and the changes of liver bioenergetics in experimental animals. METHODS: A population of B6C3F1 mice were fed with simazine (2 g and 4 g/kg/day, respectively) for 35 weeks. The concentration of cholesterol and triacylglycerols were measured in liver tissue. Liver mitochondria were isolated and parameters of oxidative phosphorylation were assessed polarographically using Clark oxygen electrode with NAD glutamate and/or FAD succinate as substrates. RESULTS: Significant changes (p < 0.001) expressed as medians (with confidence intervals) against control animals were found in both experimental groups after simazine feeding. The concentration of triacylglycerols increased from 10.3 (8.8-10.9) to 20.1 (18.0-20.9) and 47.7 (23.8-56.0), respectively. The parameters of oxidative phosphorylation with NAD substrate glutamate decreased as follows: The index of respiratory control from 7.7 (6.4-9.0) to 4.8 (4.0-6.3) resp. 4.4 (3.9-4.6); the rate of oxygen consumption in the state 3 (with ADP) from 84.2 (82.0-92.3) to 65.4 (50.8-70.7) resp. 69.9 (65.0-78.4) nAtO.mg.prot-1.min-1; and phosporylation rate from 215.3 (204.4-232.2) to 166.3 (120.4-193.6) resp. 169.6 (155.3-176.9) nmolATP.mg.prot-1.min-1. Comparable changes were detected in oxidative phosphorylation with FAD succinate as substrate. CONCLUSIONS: Liver steatosis development and mitochondrial energetics inhibition were determined in mice after long-term simazine feeding, nevertheless, liver energy production was sufficient to satisfy the liver function and the needs of the whole organism. (Tab. 4, Fig. 6, Ref. 24.)

Animals↗

[Decomposition of simazine herbicide in algal cultures].

The possibility of simazine accumulation and detoxication in the cultures of some species of green, yellow-green, and blue-green algae was investigated. It has been shown that the algae can accumulate simazine in amounts hundred times exceeding its concentration in the cultural medium. The protein fraction contained up to 28.8% of simazine accumulated by the algae. The accumulation of water-soluble products of simazine metabolism in the cultural medium is indicative of the partial transformation of the herbicide.

Absorption↗

Degradation of simazine by microorganisms isolated from soils of Spanish olive fields.

The capability of the microbial flora isolated from an olive field soil from Andalusia to mineralize simazine has been analyzed. From this soil, a group of bacteria capable of degrading 60 mg simazine litre(-1) in less than a week has been isolated. These microorganisms showed a low capacity for degrading this herbicide to carbon dioxide. When total DNA was isolated from this group of bacteria, we were able to detect by PCR the presence of only the atzC and the trzN genes. Some components of this bacterial population have been identified by sequencing of specific fragments from bacterial 16S rDNA, including Variovorax sp, Pseudoxanthomonas mexicana Thierry et al, Acidovorax sp and Methylopila capsulata Doronina et al. These data suggest that this consortium of bacteria performs an incomplete degradation of the simazine

Bacteria↗