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 73 records · Page 4Linked to original sources
PubMedDate not supplied

Solid-phase extraction of carbofuran, atrazine, simazine, alachlor, and cyanazine from shallow well water.

Extraction of several nitrogen-containing pesticides from water on solid-phase C18 cartridges was rapid and accurate. One analyst can extract greater than 48 samples/day. Recovery efficiencies were 77, 95, 92, 90, and 99% with detection limits of 0.20, 0.05, 0.05, 0.20, and 0.10 micrograms/L for carbofuran, atrazine, simazine, alachlor, and, cyanazine, respectively. Extraction of the atrazine and simazine dealkylation products (deethylatrazine and deethylsimazine) was less efficient, e.g., 26 and 9%, respectively. Comparisons with 10 U.S. Geological Survey samples gave similar results.

Acetamides↗
PubMed1989

[Contamination of drinking water with atrazine, simazine and nitrate in the Rastatt, Baden-Baden and Bühl areas].

Drinking water samples taken from public waterworks and private water sources were examined between November 1986 and July 1988 for atrazin and simazin content in the area of the Rastatt Public Health Office and its subsidiary offices in Baden-Baden and Bühl (located in the Federal German Land of Baden-Württemberg). The overall result of the examination of 41 samples taken from public waterworks and of 29 samples taken from private water sources showed that the drinking water offered by the public waterworks from reservoirs in areas declared as protected drinking water areas, is generally free from pesticide residues. However, water from private sources must be considered as extremely exposed to risk. Of 29 wells that were tested, only three were free from atrazin and only 5 free from simazin. The nitrate situation can presently be considered as being under control. Limit values have not been exceeded anywhere except for one private well.

Atrazine↗
PubMed1987

[Dynamic modelling of the simazine content of soil].

A mathematical model of dynamics of simazine level in soil based on the hypothesis of several forms of simazine in soil and integral influence of environmental factors on inactivation has been worked out. The results of modelling are under discussion.

Herbicides↗
PubMed1978

[Studies on the effects of atrazine and simazine on the N-binding bacteria Azotobacter and Beijerinckia in the ferralitic soils of Cuba].

In two Cuban locations (Santiago de las Vegas and Jovellanos) the effect was investigated of increasing atrazin and simazin applications (0, 4, 8, 16 kg/ha) to the number of Azotobacter and Beijerinckia colonies in weakly ferrallitic soils 7 and 15 days after their application during the rainy and dry seasons. The results were as follows: 1. The number of the Beijerinckia colonies is higher in all variants than that of Azotobacter. 2. Beijerinckia and Azotobacter are stimulated up to 7 days, partly also up to 15 days, after application of the triazins. Atrazin exhibits a stronger and more lasting effect than simazin, and Azotobacter are influenced more strongly than Beijerinckia. 3. This stimulation can be adduced with a high degree of probability to the inhibition of organisms which have an antagonistic effect on N-binding bacteria.

Atrazine↗
PubMedDate not supplied

[Solid-phase methods of immunoenzyme analysis of the herbicides simazine and atrazine].

Competitive methods of enzyme immuno assay (EIA) for detecting simazine and atrazine were developed, and conditions providing optimal performance were found. EIA sensitivity was shown to increase by an order of magnitude if samples were preincubated with antibodies; chloride ions were omitted; a herbicide-peroxidase conjugate was treated with urea. In EIA using labelled antibodies sensitivities thresholds towards simazine and atrazine were 0.05 and 0.1 ng/ml, respectively. EIA took 1-2 h to be done. The methods developed might be applied for quality control of water.

Animals↗
PubMedDate not supplied

[N-demethylation and denitrosation activity of the rat liver, thymus lymphocytes and spleen after exposure to simazine and sodium nitrite].

Simazine and NaNO2 have been studied for their effect on cytochrome P-450-binding N-demethylation and denitrosation activity in the rat liver and lymphocytes in the subchronic (two-month-long) experiment. N-demethylation in lymphocytes of the thymus and spleen was higher than in the liver; denitrosation in the lymphocytes was not observed. Effects of simazine and NaNO2 being injected separately in most of cases have different directions. Combined injection of these substances exceeded the total effect.

Animals↗
PubMed1997

Dissipation and distribution of atrazine, simazine, chlorpyrifos, and tetradifon residues in citrus orchard soil.

An environmental fate study was conducted in a citrus orchard plot in València (Spain) in the fall of 1993. Dissipation and distribution of atrazine, simazine, chlorpyrifos and tetradifon residues following their controlled addition for agricultural purposes in a mediterranean red soil (Luvic Calcisol, Rhodoxeralf) were evaluated. During a two-month period, the amounts of applied pesticides in different soil layers (0-0.05, 0.05-0.22, 0.22-0.42, and 0.42-0.52 m) were monitored. In addition, information on soils, weather and agricultural practice were collected. Degradation half-lives were calculated, assuming zero-order kinetics: 11 days for atrazine, 12 days for simazine, 10 days for chlorpyrifos, and 18 for tetradifon. The distribution through the soil profile shows that the pesticide concentrations were always highest in the upper layer (0-0.05 m) of soil, and that atrazine was the most mobile of all the four pesticides investigated.

Chlorpyrifos↗
PubMed1967

Effect of simazine on nitrate reductase activity in corn.

The nutritional and environmental parameters required for eliciting increases in the nitrogen content and growth of corn (Zea mays L.) by non-toxic levels of simazine have been established. Corn seedlings with the endosperm removed 10 days after germination, proved to be a suitable test species. The addition of simazine to the root-zone area of corn plants grown under both sub-optimal temperatures and low nitrate levels, increased the nitrogen content and dry weight of the plants by 20 to 25%. This increase was found to be associated with an effect on nitrate reductase.

Journal Article↗
PubMed1970

The effects of simazine and temperature on photosynthesis in rye.

Temperature during growth had a strong influence on light-saturated rates of photosynthesis and respiration in rye (Secale cereale). Carbon dioxide uptake was depressed at the low temperatures and reached maximal values higher than 30 milligrams of carbon dioxide per square decimeter per hour at the intermediate temperatures. Respiration rates increased substantially while growth temperature decreased. Simazine treatment (0.00, 0.03, 0.08, 0.12 milligrams per liter) resulted in no significant stimulatory or inhibitory effects at low temperatures, but progressively inhibited growth and photosynthesis at the higher temperatures. Respiration rates were not significantly influenced. Thus, the effect of simazine is strongly temperature-dependent and is more pronounced on photosynthesis than respiration.

Journal Article↗
PubMed1980

Formation of N-nitroso compounds of the pesticides atrazine, simazine and carbaryl with nitrogen oxides.

The nitrosation of atrazine, simazine and carbaryl by nitrogen oxides was investigated in model experiments. Pure pesticides and their corresponding formulations were exposed, as dry powders and as aqueous suspensions, to defined concentrations of NOx (1000, 100, 10 and 1 ppm) in a reaction chamber. Nitrosated pesticides were determined by HPLC-TEA. Generally, the amount of nitrosation increased with the reaction time. At high NOx concentrations (1000 and 100 ppm), nitrosation approached saturation. For atrazine and simazine, further reaction with nitrogen oxides might occur. Nitrosation rates of dry powdered pesticides were inversely proportional to grain size and to air moisture content. Nitrosation of aqueous pesticide suspensions by nitrogen oxides was strongly inhibited at pH values higher than 5.

Atrazine↗
PubMed2004

Transport and distribution of lindane and simazine in a riverine environment: measurements in bed sediments and modelling.

Aquatic sediments often remove hydrophobic contaminants from fresh waters. The subsequent distribution and concentration of contaminants in bed sediments determines their effect on benthic organisms and the risk of re-entry into the water and/or leaching to groundwater. This study examines the transport of simazine and lindane in aquatic bed sediments with the aim of understanding the processes that determine their depth distribution. Experiments in flume channels (water flow of 10 cm s(-1)) determined the persistence of the compounds in the absence of sediment with (a) de-ionised water and (b) a solution that had been in contact with river sediment. In further experiments with river bed sediments in light and dark conditions, measurements were made of the concentration of the compounds in the overlying water and the development of bacterial/algal biofilms and bioturbation activity. At the end of the experiments, concentrations in sediments and associated pore waters were determined in sections of the sediment at 1 mm resolution down to 5 mm and then at 10 mm resolution to 50 mm depth and these distributions analysed using a sorption-diffusion-degradation model. The fine resolution in the depth profile permitted the detection of a maximum in the concentration of the compounds in the pore water near the surface, whereas concentrations in the sediment increased to a maximum at the surface itself. Experimental distribution coefficients determined from the pore water and sediment concentrations indicated a gradient with depth that was partly explained by an increase in organic matter content and specific surface area of the solids near the interface. The modelling showed that degradation of lindane within the sediment was necessary to explain the concentration profiles, with the optimum agreement between the measured and theoretical profiles obtained with differential degradation in the oxic and anoxic zones. The compounds penetrated to a depth of 40-50 mm over a period of 42 days.

Adsorption↗
PubMed1999

In vitro metabolism of chlorotriazines: characterization of simazine, atrazine, and propazine metabolism using liver microsomes from rats treated with various cytochrome P450 inducers.

The in vitro metabolism of chlorotriazines, simazine (SIZ), atrazine (ATZ), and propazine (PRZ) was studied using control, 3-methylcholanthrene-, phenobarbital-, pyridine-, dexamethasone-, and clofibrate-treated rat liver microsomes. The metabolites were determined by HPLC. The principal reactions by cytochrome P450 (P450) system were N-monodealkylation and isopropylhydroxylation in all rat liver microsomes. As a result, 2-chloro-4-ethylamino-6-amino-1,3,5-triazine (M1) (SIZ-M1 for SIZ and ATZ-M1 for ATZ) and 2-chloro-4-amino-6-isopropylamino-1,3, 5-triazine (M2) (ATZ-M2 for ATZ and PRZ-M2 for PRZ), 2-chloro-4-ethylamino-6-(1-hydroxyisopropylamino)-1,3,5-triazine (M3) (ATZ-M3 for ATZ), and 2-chloro-4-isopropylamino-6-(1-hydroxyisopropylamino)-1,3,5-triazi ne (M4) (PRZ-M4 for PRZ) were detected as the metabolites. N-bidealkylation and 2-hydroxylation were not found in this system. The formation rates of SIZ-M1, ATZ-M1, ATZ-M2, and PRZ-M2 were markedly induced by 3-methylcholanthrene, phenobarbital, and pyridine. On the other hand, the formation rates of ATZ-M3 and PRZ-M4 were significantly induced by phenobarbital, pyridine, and/or clofibrate, but not by 3-methylcholanthrene. The enzyme kinetics of chlorotriazine metabolism were examined by mean of Eadie-Hofstee analyses. Although there was no remarkable difference of Km for the products in chlorotriazine metabolism among the microsomes tested, the Vmax and Clint (Vmax/Km) for the products in chlorotriazine metabolism are affected by P450 inducers, except for dexamethasone. The formation rates of SIZ-M1, ATZ-M1, ATZ-M2, and PRZ-M2 were significantly correlated with 7-ethoxyresorufin O-deethylase, acetanilide 4-hydroxylase, 7-ethoxycoumarin O-deethylase, 4-nitrophenol 2-hydroxylase, and testosterone 7alpha-hydroxylase activities and CYP1A1/2 level, whereas the formation rates of ATZ-M3 and PRZ-M4 were significantly correlated with testosterone 16beta-hydroxylase, bufuralol 1'-hydroxylase, and 4-nitrophenol 2-hydroxylase activities and CYP2B1/2 level. These results suggest that the inducibility in metabolism of SIZ, ATZ, and PRZ is different between N-monodealkylation and isopropylhydroxylation and that the N-monodealkylation and isopropylhydroxylation are induced by CYP1A1/2, CYP2B1/2, and CYP2B1/2, respectively.

Animals↗
PubMed2004

Klebsiella planticola strain DSZ mineralizes simazine: physiological adaptations involved in the process.

We examined the ability of a soil bacterium, Klebsiella planticola strain DSZ, to degrade the herbicide simazine (SZ). Strain DSZ is metabolically diverse and grows on a wide range of s-triazine and aromatic compounds. DSZ cells grown in liquid medium with SZ (in 10 mM ethanol) as carbon source mineralized 71.6+/-1.3% of 0.025 mM SZ with a yield of 4.6+/-0.3 microg cell dry weight mmol(-1) carbon. The metabolites produced by DSZ during SZ degradation included ammeline, cyanuric acid, N-formylurea and urea. We studied the physiological adaptations which allow strain DSZ to metabolize SZ. Using scanning electron microscopy, we detected DSZ cells covering the surfaces of SZ crystals when the herbicide was used at high concentrations (0.1 mM). The membrane order observed by FTIR spectroscopy showed membrane activity at low temperature (4 degrees C) to assimilate the herbicide. Membrane fatty acid analysis demonstrated that strain DSZ adapted to grow on SZ by increasing the degree of saturation of membrane lipid fatty acid; and the opposite effect was detected when both SZ and ethanol were used as carbon sources. This confirms the modulator effect of ethanol on membrane fluidity.

Adaptation, Physiological↗
PubMed1999

In vitro metabolism of simazine, atrazine and propazine by hepatic cytochrome P450 enzymes of rat, mouse and guinea pig, and oestrogenic activity of chlorotriazines and their main metabolites.

1. The in vitro metabolism of chlorotriazines, simazine (SIZ), atrazine (ATZ) and propazine (PRZ) in liver microsomes from rat, mouse and guinea pig and the oestrogenic activity of chlorotriazines and their main metabolites have been studied. 2. The formation rates of products in chlorotriazine metabolism were determined by HPLC. The principal reactions catalysed by the cytochrome P450 (P450) system were N-monodealkylation and isopropylhydroxylation in all liver microsomes. As a result, 2-chloro-4-ethylamino-6-amino-1,3,5-triazine (M1) (SIZ-M1 for SIZ and ATZ-M1 for ATZ) and 2-chloro-4-amino-6-isopropylamino-1,3,5-triazine (M2) (ATZ-M2 for ATZ and PRZ-M2 for PRZ), and 2-chloro-4-ethylamino-6-(1-hydroxyisopropylamino)-1,3,5-triazine (M3) (ATZ-M3 for ATZ) and 2-chloro-4-isopropylamino-6-(1-hydroxyisopropylamino)-1,3,5-triazi ne (M4) (PRZ-M4 for PRZ) were detected as the metabolites. N-bidealkylation was not found in this system. 3. The formation rates of N-deethylated metabolites (SIZ-M1 and ATZ-M2) were generally higher in mouse than in rat and guinea pig. The formation rates of N-deisopropylated metabolites (ATZ-M1 and PRZ-M2) in guinea pig were the lowest among the three animal species. The formation rates of isopropylhydroxylated metabolites (ATZ-M3 and PRZ-M4) were remarkably low in mouse compared with rat and guinea pig. 4. The enzyme kinetics of chlorotriazine metabolism were examined by Eadie-Hofstee analyses. Some species differences in Michaelis-Menten parameters for each metabolite were observed, and the ranking orders were varied among the metabolites. 5. The binding affinity of chlorotriazines (SIZ, ATZ and PRZ) and their metabolites (M1-4) for recombinant human oestrogen receptor-alpha was assayed using the fluorescence polarization method. The binding affinity of M2 was significantly higher than those of parent compounds and other metabolites, although the oestrogenic activity was remarkably low compared with that of 17beta-oestradiol (E2). 6. These results suggest that the pattern of metabolism of SIZ, ATZ and PRZ by the P450 system differs extensively among rat, mouse and guinea pig, and that M2 may be an activated metabolite of chlorotriazines.

Animals↗
PubMedDate not supplied

Simultaneous determination of alachlor, metolachlor, atrazine, and simazine in water and soil by isotope dilution gas chromatography/mass spectrometry.

A multiresidue method was developed for the simultaneous determination of low parts per billion (ppb) concentrations of the herbicides alachlor, metolachlor, atrazine, and simazine in water and soil using isotope dilution gas chromatography/mass spectrometry (GC/MS). Known amounts of 15N,13C-alachlor and 2H5-atrazine were added to each sample as internal standards. The samples were then prepared by a solid phase extraction with no further cleanup. A high resolution GC/low resolution MS system with data acquisition in selected ion monitoring mode was used to quantitate herbicides in the extract. The limit of detection was 0.05 ppb for water and 0.5 ppb for soil. Accuracy greater than 80% and precision better than 4% was demonstrated with spiked samples.

Acetamides↗
PubMed1985

Effects of the herbicides simazine and bromophenoxim on the microflora of two soil types in Egypt.

The effects of the herbicides simazine and bromophenoxim on the microflora of two soil-types were studied. It was found that the effects produced on the microbial biomass depended on the type and concentration of the herbicide used and the nature of soil treated. It was also found that the application of these herbicides to the studied soils caused significant alterations in the species composition of its microflora. These alterations were detected by the disappearance or appearance of certain species under a specific concentration of the used herbicide. Species density was also affected.

Bacteria↗
PubMedDate not supplied

Liquid chromatographic determination of simazine, atrazine, and propazine residues in catfish.

A liquid chromatographic (LC) method is described for the simultaneous determination of the triazine herbicides, simazine (SIM), atrazine (ATZ), and propazine (PRO) in the 12.5-100 ppb range in catfish. The herbicides are extracted from catfish homogenates with ethyl acetate, followed by solvent partitioning between acetonitrile and petroleum ether and additional cleanup on a C18 cartridge. A Supelcosil LC-18-DB column is used for LC separation, and UV determination is at 220 nm. The isocratic mobile phase is a mixture of methanol, acetonitrile, and water. Mean recoveries from catfish were 88.7, 96.9, and 91.7%; standard deviations were 6.84, 7.78, and 6.26%; and coefficients of variation were 7.72, 8.03, and 6.82% for SIM, ATZ, and PRO, respectively.

Animals↗
PubMed1989

Isotachophoretic determination of herbicides prometryne, desmetryne, terbutryne and hydroxy-derivatives of atrazine and simazine in extracts of milk.

A method is described for the determination of the triazine herbicides prometryne, desmetryne, terbutryne, OH-atrazine and OH-simazine in purified extracts of milk using analytical capillary isotachophoresis. The reproducibility of isotachophoretic analyses was 3.5% and the detection sensitivity reached 2 ng. Recovery of triazines from fortified samples of homogenized full milk (0.05 mg/L) was about 65%.

Animals↗