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PubMed2003

Prediction of the behaviour of organic pollutants using cloud point extraction.

A preconcentration study based on the cloud point phenomenon was carried out for a set of triazine herbicides, three of them chloro-substituted and three of them methylthio-substituted. Concentration factors and recoveries were calculated as function of the percentage of the non-ionic surfactant Triton X-114 employed. From these values, obtained from a cloud point extraction (CPE) procedure, the distribution coefficient between the Triton X-114 micelles and water, Kc, prior to CPE was calculated for each triazine and related to the corresponding octanol-water partition coefficient, Kow. In order to confirm the results obtained with the triazine herbicides, two sets of data from chemically different organic pollutants--organophosporous and chlorophenols--obtained from the literature were assessed, concluding that they display a similar behaviour to that of the triazine herbicides. This can be used to predict the CPE behaviour of other organic pollutants from their octanol-water partition coefficients. The Kc values were compared with the analyte concentration ratio in the surfactant-rich phase and aqueous phase (Ksa) with a view to obtaining a link between the analyte behaviour prior to and after cloud point extraction procedures.

Environmental Pollutants↗
PubMed2002

Synthesis of a group-selective antibody library against haptens.

A generic strategy is described for the generation of libraries comprising hapten-selective antibody genes against a group of structurally related low molecular weight target molecules. Hapten antibody libraries are frequently suffering from high background levels of irrelevant antibody genes as a consequence of the immunization, where the small non-immunogenic target molecule is coupled to a large immunogenic carrier protein. In order to elevate the percentage of hapten-specific genes in the library, B cells harboring antibody genes against the group of triazine herbicides were enriched from 21 individual splenocyte populations by means of immunomagnetic separation (IMS). IMS utilizes the specific binding of membrane-associated immunoglobulin receptors on the B cell surface to hapten-coated paramagnetic beads. The variable genes of the specifically enriched subpopulation were cloned into a phagemid vector. The corresponding library yielded up to 75% triazine binding antibody clones after three rounds of phage selection. At least half of these antibodies (abs) were displaceable by triazines resulting in quantitative assays with nanomolar sensitivities. In contrast, no displaceable clone was obtained at the same selection level in a control library, where IMS was omitted. Due to the elevated percentage of relevant antibody genes, the library can be utilized either for the direct isolation of functional antibodies against various triazine herbicides or as group-specific gene source for evolutionary antibody optimization.

Animals↗
PubMed2001

Novel enzyme activities and functional plasticity revealed by recombining highly homologous enzymes.

BACKGROUND: Directed evolution by DNA shuffling has been used to modify physical and catalytic properties of biological systems. We have shuffled two highly homologous triazine hydrolases and conducted an exploration of the substrate specificities of the resulting enzymes to acquire a better understanding of the possible distributions of novel functions in sequence space. RESULTS: Both parental enzymes and a library of 1600 variant triazine hydrolases were screened against a synthetic library of 15 triazines. The shuffled library contained enzymes with up to 150-fold greater transformation rates than either parent. It also contained enzymes that hydrolyzed five of eight triazines that were not substrates for either starting enzyme. CONCLUSIONS: Permutation of nine amino acid differences resulted in a set of enzymes with surprisingly diverse patterns of reactions catalyzed. The functional richness of this small area of sequence space may aid our understanding of both natural and artificial evolution.

Aminohydrolases↗
PubMed2001

The fate of the cyclic nitramine explosive RDX in natural soil.

The sorption-desorption behavior and long-term fate of hexahydro-1,3,5-trinitro-1,3,5-triazine (RDX) was examined in sterilized and nonsterilized topsoil. Results of this study indicate that although RDX is not extensively sorbed by the topsoil (Ks(d) of 0.83 L/kg), sorption is nearly irreversible. Furthermore, there was no difference in the sorption behavior for sterile and nonsterile topsoil. However, over the longterm, RDX completely disappeared within 5 weeks in nonsterile topsoil, and hexahydro-1-nitroso-3,5-dinitro-1,3,5-triazine (MNX), hexahydro-1,3-dinitroso-5-nitro-1,3,5-triazine (DNX), and hexahydro-1,3,5-trinitroso-1,3,5-triazine (TNX) metabolites formed in the aqueous phase. Over the same period, recovery of RDX from sterile topsoil was high (55-99%), and the nitroso metabolites were not detected. Only traces of RDX were mineralized to CO2 and N2O by the indigenous microorganisms in nonsterile topsoil. Of the RDX that was mineralized to N2O, one N originated from the ring and the other from the nitro group substituent, as determined using N15 ring-labeled RDX. However, N2O from RDX represented only 3% of the total N2O that formed from the process of nitrification/denitrification.

Adsorption↗
PubMed2002

Use of liquid chromatography/tandem mass spectrometry to detect distinctive indicators of in situ RDX transformation in contaminated groundwater.

An important element of monitored natural attenuation is the detection in groundwater of distinctive products of pollutant degradation or transformation. In this study, three distinctive products of the explosive RDX (hexahydro-1,3,5-trinitro-1,3,5-triazine) were detected in contaminated groundwater from the Iowa Army Ammunition Plant; the products were MNX (hexahydro-1-nitroso-3,5-dinitro-1,3,5-triazine), DNX (hexahydro-1,3-dinitroso-5-nitro-1,3,5-triazine), and TNX (hexahydro-1,3,5-trinitroso-1,3,5-triazine). These compounds are powerful indicators of RDX transformation for several reasons: (a) they have unique chemical features that reveal their origin as RDX daughter products, (b) they have no known commercial, industrial, or natural sources, and (c) they are well documented as anaerobic RDX metabolites in laboratory studies. The products were analyzed by LC/MS/MS (liquid chromatography/mass spectrometry/mass spectrometry) with selected reaction monitoring and internal standard quantification using [ring-U-15N]RDX. Validation tests showed the novel LC/MS/MS method to be of favorable sensitivity (detection limits ca. 0.1 microg/L), accuracy, and precision. The products, which were detected in all groundwater samples with RDX concentrations of > ca. 1 microg/L (25 out of 55 samples analyzed), were present at concentrations ranging from near the detection limit to 430 microg/L. MNX was the typically the most abundant of the three nitroso-substituted products; concentrations of the products seldom exceeded 4 mol % of the RDX concentration, although they ranged as high as 26 mol % (TNX). Geographic and temporal distributions of RDX, MNX, DNX, and TNX were assessed. A degradation product resulting from RDX ring cleavage, methylenedinitramine, was not detected by LC/MS/MS in any sample (detection limit ca. 0.6-4 microg/L). This extensive field characterization of MNX, DNX, and TNX distributions in groundwater by a highly selective analytical method (LC/MS/MS) is significant because very little is known about the occurrence of intrinsic RDX transformation in contaminated aquifers.

Biotransformation↗
PubMed2005

N-triazinylammonium tetrafluoroborates. A new generation of efficient coupling reagents useful for peptide synthesis.

A new generation of triazine-based coupling reagents (TBCRs), designed according to the concept of "superactive esters", was obtained by treatment of 4-(4,6-dimethoxy-1,3,5-triazin-2-yl)-4-methylmorpholinium (DMTMM) chloride with lithium or silver tetrafluoroborate. The structure of 4-(4,6-dimethoxy-1,3,5-triazin-2-yl)-4-methylmorpholinium tetrafluoroborate was confirmed by X-ray diffraction. Activation of carboxylic acids by using this reagent proceeds via triazine "superactive ester". The coupling reagent was successfully used for the synthesis of Z-, Boc-, and Fmoc-protected dipeptides derived from natural and unnatural sterically hindered amino acids and for fragment condensation, in 80-100% yield and with high enantiomeric purity. The manual SPPS of the ACP(65-74) peptide fragment (H-Val-Gln-Ala-Ala-Ile-Asp-Tyr-Ile-Asn-Gly-OH) proceeded significantly faster than with TBTU or HATU, as well as the automated SPPS of the same fragment gave a purer product than by using TBTU or PyBOP. The reagent was also demonstrated to be efficient in on-resin head-to-tail cyclization of constrained cyclopeptides, in SPPS synthesis of Aib peptides, and in the synthesis of esters from appropriate acids, alcohols, and phenols. The high efficiency and versatility of this new generation of TBCRs confirm, for the first time, the usefulness of the concept of "superactive esters" in rational design of the structure of coupling reagents.

Amides↗
PubMed2003

Analytical method for the determination of atrazine and its dealkylated chlorotriazine metabolites in water using SPE sample preparation and GC-MSD analysis.

A method is reported for the determination of atrazine and its dealkylated chlorotriazine metabolites in ground, surface, and deionized water. Water samples are adjusted to pH 3-4 prior to loading onto two SPE cartridges in series: C-18 and C-18/cation exchange mixed-mode polymeric phases. The analytes are eluted from each of the two cartridges separately, and the pooled and concentrated fraction is analyzed using gas chromatography-mass selective detection in the selected ion monitoring mode. The lower limit of method validation is 0.10 micrograms/L (ppb) for 2-chloro-4-(ethylamino)-6-(isopropylamino)-s-triazine (atrazine), 2-amino-4-chloro-6-(isopropylamino)-s-triazine (G-30033, deethylatrazine), 2-amino-4-chloro-6-(ethylamino)-s-triazine (G-28279, deisopropylatrazine), and 2,4-diamino-6-chloro-s-triazine (G-28273, didealkyatrazine). The overall mean procedural recoveries (and standard deviations) are 96 (6.9), 96 (5.5), 95 (6.8), and 100% (10%) for atrazine, G-30033, G-28279, and G-28273, respectively (n = 49). The method validation study was conducted under U.S. EPA FIFRA Good Laboratory Practice Guidelines 40 CFR 160. The reported procedure accounts for residues of G-28273 in water.

Atrazine↗
PubMed1984

Bacterial degradation of N-cyclopropylmelamine. The steps to ring cleavage.

The s-triazine cyclopropylmelamine (N-cyclopropyl-1,3,5-triazine-2,4,6-triamine) was degraded to about 6 mol of NH4+/mol of substrate by a mixture of two bacteria (strains A and D, both Pseudomonas spp.) Only strain A grew with cyclopropylmelamine as sole and limiting source of nitrogen. The organism obtained 2 mol of nitrogen/mol of substrate and excreted a product that was identified as cyclopropylammelide [6-cyclopropylamino-1,3,5-triazine-2,4(1 H,3 H)-dione]. Proteins in extracts from strain A were separated on a Sephadex G-200 column. Cyclopropylmelamine was found to be deaminated in two separable steps to cyclopropylammelide via cyclopropylammeline [4-amino-6-cyclopropylamino-1,3,5-triazine-2(1 H)-one], which was identified. Strain D could not utilize cyclopropylmelamine or cyclopropylammeline, but could utilize cyclopropylammelide (or homologue) as sole and limiting source of nitrogen and obtain about 4 mol of nitrogen/mol of substrate. Proteins in cell extracts from strain D were separated on a DEAE-cellulose column. Alkylammelides were degraded quantitatively by one enzyme fraction to 1 mol of cyanuric acid plus 1 mol of alkylamine/mol of substrate. The specific activities of enzymes in extracts of the two strains were as high as the activities observed during growth. The three activities studied in the two strains were all active under aerobic and oxygen-free conditions. The reactions appear to be hydrolytic, yielding 2 mol of NH4+ plus 1 mol of cyclopropylamine and 1 mol of cyanuric acid/mol of substrate.

Chemical Phenomena↗
PubMed1983

Qualitative analysis of waste-water from ametryne production.

s-Triazines in waste-water from the synthesis of ametryne (2-(ethylamino)-4-[(l-methylethyl) amino]-6-(methylthio)-1,3,5-triazine) were tentatively identified co-chromatographically by HPLC and by UV-spectra. Alkylated s-triazines (e.g. hydroxyametryne, 4-(ethylamino)-6-(methylthio)-1,3,5-triazine-2(1H)-one, and N-ethylammelide) were isolated by preparative chromatography on a reversed phase support, and were identified by mass spectrometry. Putative cyanuric acid was desalted on activated charcoal and its identity confirmed as the silylated derivative by GLC.

Herbicides↗
PubMedDate not supplied

Tillage, intercrop, and controlled drainage-subirrigation influence atrazine, metribuzin, and metolachlor loss.

Atrazine (6-chloro-N2-ethyl-N4-isopropyl-1,3,5-triazine-2,4-diamine) and metolachlor [2-chloro-N-(2-ethyl-6-methylphenyl)-N-(2-methoxy-1-methylethyl)acetamide] have been found with increasing occurrence in rivers and streams. Their continued use will require changes in agricultural practices. We compared water quality from four crop-tillage treatments: (i) conventional moldboard plow (MB), (ii) MB with ryegrass (Lolium multiflorum Lam.) intercrop (IC), (iii) soil saver (SS), and (iv) SS + IC; and two drainage control treatments, drained (D) and controlled drainage-subirrigation (CDS). Atrazine (1.1 kg a.i. ha-1), metribuzin [4-amino-6-(1,1-dimethylethyl)-3-(methylthio)-1,2,4-triazine-5(4H)-one] (0.5 kg a.i. ha-1), and metolachlor (1.68 kg a.i. ha-1) were applied preemergence in a band over seeded corn (Zea mays L.) rows. Herbicide concentration and losses were monitored from 1992 to spring 1995. Annual herbicide losses ranged from < 0.3 to 2.7% of application. Crop-tillage treatment influenced herbicide loss in 1992 but not in 1993 or 1994, whereas CDS affected partitioning of losses in most years. In 1992, SS + IC reduced herbicide loss in tile drains and surface runoff by 46 to 49% compared with MB. The intercrop reduced surface runoff, which reduced herbicide transport. Controlled drainage-subirrigation increased herbicide loss in surface runoff but decreased loss through tile drainage so that total herbicide loss did not differ between drainage treatments. Desethyl atrazine [6-chloro-N-(1-methylethyl)-1,3,5-triazine-2,4-diamine] comprised 7 to 39% of the total triazine loss.

Acetamides↗
PubMedDate not supplied

Gas chromatographic determination of ametryn and its metabolites in tropical root crops.

Residue analysis of the herbicide ametryn (2-methylthio-4-ethylamino-6-isopropylamino-s-triazine) is widely known but an analytical method for determining its metabolites has not yet been reported in the literature. A method has been developed for the extraction and determination of ametryn and 3 metabolites, 2-methylthio-4-amino-6-isopropylamino-s-triazine (GS-11354), 2-methylthio-4,6-diamino-s-triazine (GS-26831), and 2-methylthio-4-amino-6-ethylamino-s-triazine (GS-11355) in taniers , yams , cassava. Residues were extracted from crops with ethyl acetate-toluene (3 + 1 v/v), using a Polytron homogenizer and anhydrous sodium sulfate added for drying. The extracts were cleaned up by automated gel permeation chromatography on Bio-Beads SX-3 gel in the same solvent system. Quantitative determination was performed by gas chromatographic (GC) analysis on a column packed with 5% DEGS -PS on 100-120 mesh Supelcoport using either an N-P detector or a flame photometric detector ( FPD ) in the sulfur mode. Minimum detection by the flame photometric detector is 10 ng each for ametryn , GS-11354, and GS-11355 and 21 ng for GS-26831; by the N-P detector, 0.3 ng of each component gives easily quantitatable peaks. On a parts per million basis, starting with 25 g sample, the FPD detected a minimum level of 0.04 microgram/g each for ametryn , GS-11354, and GS-11355, and 0.08 microgram/g for GS-26831. The N-P detector could detect 0.0024 microgram/g for all 4 compounds. In addition to superior sensitivity, instrumental conditions allowed the complete separation of components in 10 min, for the N-P detector; more than 30 min was required for the FPD . Recoveries from fortified crops ranged from 67 to 111% at levels of 0.1-1.0 microgram/g.

Chromatography, Gas↗
PubMed2004

Synthesis of boron-containing heterocyclic compounds.

The synthesis of boron-containing 1,3,5-triazines and 1,2,4-triazines is described. Derivatives of 1,3,5-triazine containing the o-carborane cluster have been obtained by reacting the corresponding propargyl derivatives with B(10)H(14). Derivatives of 1,2,4-triazine containing the B(12)H(12)(2-) cluster have been obtained by nucleophilic substitution of ethylsulfone derivatives with B(12)H(11)SH(2-). They have been isolated in their ring-protonated form. Reaction of RNH(2)-B(8)H(11)NH-R with stericly demanding heterocycles failed, either for steric or for solubility reasons.

Journal Article↗
PubMed2002

Atrazine in groundwater of Vojvodina Province.

The objective of this study was to investigate concentrations of atrazine (2-chloro-4-ethylamino-6-isopropylamino-1,3,5-triazine), deethylatrazine (DEA) (2-amino-4-chloro-6-isopropylamino-1,3,5-triazine), deisopropylatrazine (DIA) (2-amino-4-chloro-6-ethylamino-1,3,5-triazine) and deethyldeisopropylatrazine (DEIA) (6-chloro-2,4-diamino-1,3,5-triazine) in groundwaters of Vojvodina Province. A study was conducted during April 2001. Some 110 samples of groundwater were taken from near surface aquifers. The water samples were first passed through a disk containing solid matrix coated with a chemically bonded C-18 organic phase. The disk was then eluted with supercritical carbon dioxide to remove compounds from the sorbent. Finally the extract was injected into capillary gas chromatograph. Average concentrations were 0.198 microg L(-1) for atrazine, 0.116 microg L(-1) for DEA, 0.043 microg L(-1) for DIA and 0.077 microg L(-1) for DEIA.

Atrazine↗
PubMed1999

Light induced transformation of tribenuron-methyl

To study the photostability of sulfonylurea herbicide tribenuron-methyl (methyl 2-[[[[ N-(4-methoxy-6-methyl-1,3,5-triazin-2-yl) methylamino] carbonyl]amino]sulfonyl]benzoate), in the field, model experiments with organic solvents were performed. Irradiation of tribenuron-methyl in methanol, isopropanol and cyclohexane yielded 4-methoxy-6-methyl-2-aminomethyl-1,3,5-triazine; methyl-2-(aminosulfonyl) benzoate; N-(4-methoxy-6-methyl-1,3,5-triazin-2-yl)-N-methyl urea; N-(2-carbomethoxy phenyl)-N-(4-methoxy-6-methyl-1,3,5-triazin-2-yl)-N'-methyl urea; 2-(aminosulfonyl) benzoic acid, N-methyl saccharin and saccharin in considerable amounts. The rate of degradation in different solvents followed first-order kinetics with a statistically significant correlation coefficient.

Journal Article↗
PubMed2001

Rapid reductive dechlorination of atrazine by zero-valent iron under acidic conditions.

The dechlorination of atrazine (2-chloro-4-ethylamino-6-isopropylamino-1,3,5-triazine) via reaction with metallic iron under low-oxygen conditions was studied using reaction mixture pH values of 2.0, 3.0, and 3.8. The pH control was achieved through addition of sulfuric acid throughout the duration of the reaction. The lower the pH of the reaction mixture, the faster the degradation of atrazine. The surface area of the sulfuric acid-treated iron particles was 0.31 (+/- 0.01) m2 g-1 and the surface area normalized initial pseudo-first order rate constants (kSA, where rate = kSA x (surface area/l) x [Atrazine]) at pH values of 2.0, 3.0, and 3.8 were equal to, respectively, 3.0 (+/- 0.4) x 10(-3) min-1 m-2 l, 5 (+/- 3) x 10(-4) min-1 m-2 l, and 1 (+/- 1) x 10(-4) min-1 m-2 l. The observed products of the degradation reaction were dechlorinated atrazine (2-ethylamino-4-isopropylamino-1,3,5-triazine) and possibly hydroxyatrazine (2-ethylamino-4-isopropylamino-6-hydroxy-s-triazine). Triazine ring protonation may account, at least in part, for the observed effect of pH on atrazine dechlorination via metallic iron.

Acids↗
PubMed2000

Urinary biomarkers of atrazine exposure among farm pesticide applicators.

PURPOSE: This study assessed the feasibility of three laboratory methods for the detection of atrazine, a triazine herbicide, and its related metabolites in urine collected from field applicators.METHODS: Urine samples were collected from 256 randomly sampled field applicators 8 hours post application. Of these, 99 reported atrazine use during the application prior to sample collection and these samples were subsequently analyzed for urinary biomarkers.RESULTS: 37.4% (n = 37) samples showed detectable levels (minimum = 1.0 ng/mL) of deethylatrazine using gas chromatographic mass spectrometry (GCMS) analysis (X = 14.2 ng/mL; s.d. = 13.5). Fifty samples were tested using atrazine mercapturate in urine ELISA methods and 80% (n = 40) of these samples showed detectable levels of atrazine (X = 6.4 ng/mL; s.d. = 7.5). Of 10 samples tested by triazines in water ELISA methods, a common assay used for the detection of atrazine in groundwater, 100% showed detectable levels of atrazine (X = 22.4 ng/mL; s.d. = 13.9). Of the 21 samples collected from non-applicators and tested by GCMS, none evidenced detectable atrazine levels. Using GCMS as the gold standard, analyses showed that the mercapturate in urine ELISA was 48% sensitive and 91% specific whereas the triazines in water ELISA was 69% sensitive and 100% specific.CONCLUSIONS: It is possible to detect one-time atrazine exposures through analysis of urinary biomarkers among pesticide applicators. The feasibility of triazines in water ELISA methods for use in field studies for analyzing the presence of atrazine and related metabolites in urine was supported, but these methods need further testing on larger applicator samples before they can be used for standard screening.

Journal Article↗
PubMed1998

Analytical Method for the Determination of Atrazine and Its Dealkylated Chlorotriazine Metabolites in Urine by Gas Chromatography/Mass Selective Detection.

A multiresidue method is reported for the determination of atrazine and its chloro dealkylated metabolites in urine. Urine samples were subjected to a protein precipitation procedure followed by further purification using strong anion exchange and silica solid-phase extraction columns. Final analysis was accomplished using gas chromatography/mass selective detection in the selected ion monitoring mode. The limits of detection were 0.050 ng injected for 2,4-diamino-6-chloro-s-triazine (G-28273) and 0.025 ng injected for 2-chloro-4-(ethylamino)-6-(isopropylamino)-s-triazine (atrazine), 2-amino-4-chloro-6-(isopropylamino)-s-triazine (G-30033), and 2-amino-4-chloro-6-(ethylamino)-s-triazine (G-28279). The limits of quantification were 1.0 ppb for atrazine and G-30033 and 2.0 ppb for G-28279 and G-28273. The mean procedural recoveries obtained during the method validation were 115, 113, 112, and 97% and the standard deviations were 10.6, 10.2, 9.5, and 16.1% for atrazine, G-30033, G-28279, and G-28273, respectively. Additional recovery data were obtained during a worker exposure study and during an outside ruggedness trial. All studies were conducted under U.S. EPA FIFRA Good Laboratory Practice Standards 40 CFR 160.

Journal Article↗
PubMed2000

Analytical method for the determination of atrazine and its dealkylated chlorotriazine metabolites in water using gas chromatography/mass selective detection.

A multiresidue method is reported for the determination of atrazine and its dealkylated chlorotriazine metabolites in water. Water samples are buffered to pH 10 and partitioned in ethyl acetate. Final analysis is accomplished using gas chromatography/mass selective detection (GC/MSD) in the selected ion monitoring (SIM) mode. The limit of detection (LOD) is 0.050 ng and the limit of quantification (LOQ) is 0.10 ppb for 2-chloro-4-(ethylamino)-6-(isopropylamino)-s-triazine (atrazine), 2-amino-4-chloro-6-(isopropylamino)-s-triazine (G-30033), 2-amino-4-chloro-6-(ethylamino)-s-triazine (G-28279), and 2, 4-diamino-6-chloro-s-triazine (G-28273). The mean procedural recoveries were 90, 92, 98, and 85% and the standard deviations were 12, 13, 16, and 20% for atrazine, G-30033, G-28279, and G-28273, respectively (n = 30). The study was conducted under U.S. EPA FIFRA Good Laboratory Practice Guidelines 40 CFR 160 for method validation. The reported procedure accounts for residues of G-28273 in water that are not included in EPA Method 507.

Atrazine↗