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At least 127 records · Page 7Linked to original sources

Stability of chloroplastic triazine resistance in rutabaga backcross generations.

Triazine resistance originally observed in a weed biotype of birdsrape (Brassica campestris L.) has been transferred through cytoplasmic substitution into rutabaga (Brassica napus ssp. Rapifera [Metzg.] Minsk.) by conventional backcrossing. Photosynthetic function and resistance to triazines were examined in six backcross generations of rutabaga as well as in the original parents. Chloroplast thylakoid membranes were isolated and their sensitivity to atrazine, metribuzin, and diuron assayed by measuring the inhibition of photoreduction of 1,6-dichlorophenol indophenol as well as the alteration of in vitro chlorophyll fluorescence rise characteristics. Both assay methods indicated that triazine resistance persisted in all rutabaga backcross generations, and that it involved triazine binding sites in chloroplasts. There was little resistance to diuron. In vivo chlorophyll fluorescence was also monitored, in the absence of herbicides, as an indicator of the electron transfer properties of the chloroplast photosystem II complex. The results indicated that electron transport from Q(A) to Q(B) was slower (as indicated by a larger intermediate level fluorescence during the transient rise) in the triazine resistant parents as well as in all the rutabaga backcross generations.

Journal Article↗

Derivatives of 2,4-dimethoxy-1,3,5-triazine.

The crystal structure of three derivatives of 2,4-dimethoxy-1,3,5-triazine are described. In 4-(4,6-dimethoxy-1,3,5-triazin-2-yl)morpholine, C(9)H(14)N(4)O(3), the morpholine moiety adopts a chair conformation, and the dimethoxytriazine molecule adopts a butterfly conformation with respect to the two methoxy groups. In 3-(4,6-dimethoxy-1,3,5-triazin-2-yloxy)-2-methylphenol, C(12)H(13)N(3)O(4), the dimethoxytriazine moiety adopts a propeller conformation with respect to the methoxy groups, and the molecules form dimers held together by O-H.N hydrogen bonds. 4-(4,6-Dimethoxy-1,3,5-triazin-2-yloxy)phenyl phenyl ketone, C(18)H(15)N(3)O(4), crystallizes with two crystallographically independent molecules in the asymmetric unit. The two molecules adopt different conformations with respect to the geometric relations between the phenyl ketone and triazine moieties.

Journal Article↗

Characterization of S-triazine herbicide metabolism by a Nocardioides sp. isolated from agricultural soils.

Atrazine, a herbicide widely used in corn production, is a frequently detected groundwater contaminant. Nine gram-positive bacterial strains able to use this herbicide as a sole source of nitrogen were isolated from four farms in central Canada. The strains were divided into two groups based on repetitive extragenic palindromic (rep)-PCR genomic fingerprinting with ERIC and BOXA1R primers. Based on 16S ribosomal DNA sequence analysis, both groups were identified as Nocardioides sp. strains. None of the isolates mineralized [ring-U-(14)C]atrazine. There was no hybridization to genomic DNA from these strains using atzABC cloned from Pseudomonas sp. strain ADP or trzA cloned from Rhodococcus corallinus. S-Triazine degradation was studied in detail in Nocardioides sp. strain C190. Oxygen was not required for atrazine degradation by whole cells or cell extracts. Based on high-pressure liquid chromatography and mass spectrometric analyses of products formed from atrazine in incubations of whole cells with H(2)(18)O, sequential hydrolytic reactions converted atrazine to hydroxyatrazine and then to the end product N-ethylammelide. Isopropylamine, the putative product of the second hydrolytic reaction, supported growth as the sole carbon and nitrogen source. The triazine hydrolase from strain C190 was isolated and purified and found to have a K(m) for atrazine of 25 microM and a V(max) of 31 micromol/min/mg of protein. The subunit molecular mass of the protein was 52 kDa. Atrazine hydrolysis was not inhibited by 500 microM EDTA but was inhibited by 100 microM Mg, Cu, Co, or Zn. Whole cells and purified triazine hydrolase converted a range of chlorine or methylthio-substituted herbicides to the corresponding hydroxy derivatives. In summary, an atrazine-metabolizing Nocardioides sp. widely distributed in agricultural soils degrades a range of s-triazine herbicides by means of a novel s-triazine hydrolase.

Actinomycetales↗

Reproductive effects of hexahydro-1,3,5-trinitroso-1,3,5-triazine in deer mice (Peromyscus maniculatus) during a controlled exposure study.

Contamination with hexahydro-1,3,5-trinitro-1,3,5-triazine (Royal Demolition Explosive [RDX]) has been identified at areas of explosive manufacturing, processing, storage, and usage. Thus, the potential exists for exposure to N-nitroso compounds, hexahydro-1-nitroso-3,5-dinitro-1,3,5-triazine, hexahydro-1,3-dinitroso-5-nitro-1,3,5-triazine, and hexahydro-1,3,5-trinitroso-1,3,5-triazine (TNX), formed via anaerobic transformation of RDX. Following exposure, reproductive toxicity of TNX was evaluated in three consecutive litters of deer mice (Peromyscus maniculatus). Hexahydro-1,3,5-trinitroso-1,3,5-triazine was administered ad libitum via drinking water at four doses: 0 (control), 1, 10, and 100 microg/L. Endpoints investigated included reproductive success, offspring survival, offspring weight gain, offspring organ weights, and liver TNX residues. Data from the present study indicate that TNX bioaccumulates in the liver and is associated with postpartum mortality, dose-dependent decrease in body weight from birth to weaning, and decrease in kidney weight of deer mice offspring.

Animals↗

Circadian oscillations in chlorophyll fluorescence in a triazine-resistant chronomutant of Brassica napus.

The objectives of this study were to determine if there was variation in atrazine tolerance, measured by intensity of leaf-disc chlorophyll fluorescence, in triazine-resistant and -susceptible Brassica napus in terms of age of leaf on the plant, time of day, and time of assay after leaf disc removal and immersion in atrazine. In a growth room and field experiment, triazine-susceptible B. napus cv. "Tower" and triazine-resistant B. napus cv. "OAC Triton" were used. Chlorophyll fluorescence intensity measurements were made 15-30 min after disc removal. In both environments, two periods of reduced photosynthetic efficiency occurred in the circadian phase. The times that these periods occurred during the diurnal phase differed between biotypes. A phase shift in leaf chlorophyll fluorescence (LCF) maxima between resistant and susceptible biotypes resulted in two periods, early and late in the light phase, of increased LCF in resistant tissue. This differential pattern in LCF is support for the hypothesis that triazine-resistance chloroplast alterations imply an alteration in the temporal organization of chloroplast physiological function. Atrazine reduced the photosynthetic efficiency of resistant tissue in some instances. This could indicate that triazine resistance is not complete and that some metabolic role may be involved. The results reported here indicate that the most accurate estimation of the physiological state will be obtained from LCF measurements taken soon after leaf disc removal from the plant.

Atrazine↗

Triazine-based condensing reagents.

The synthesis, properties, and application of condensing reagents derived from 1,3,5-triazines are described. The mechanism of activation of carboxylic function, structure of reactive intermediates, and mechanism of acylation of nucleophiles are presented. The synthetic versatility of mono- and bifunctional reagents for syntheses in solution, triazine-based immobilized reagents, chiral triazines for enantiodifferentiating syntheses, are discussed. The scope and limitation of the synthetic utility of triazine reagents in the preparation of heterocyclic compounds, amides, esters, oligopeptides-including large-scale syntheses and use in the combinatorial chemistry-is demonstrated.

Combinatorial Chemistry Techniques↗

Comparative study of separation and determination of triazines by micellar electrokinetic capillary chromatography and nonaqueous capillary electrophoresis: application to residue analysis in natural waters.

The separation and determination of a mixture of chloro- and methylthiotriazines in water samples by both micellar electrokinetic capillary chromatography (MEKC) and nonaqueous capillary zone electrophoresis (NA-CZE) were compared. The characteristics of both methods proved to be very similar in terms of separation efficiency and analysis times, but application of these methods for the analysis of triazines in natural waters, with a prior preconcentration step, revealed significant differences. A preconcentration step by solid-phase extraction (SPE) with Oasis HLB cartridges was accomplished for the determination of triazines at sub-ppb levels in drinking and river waters; when NA-CZE was used after this SPE step, electropherograms with fewer interferences and more stable baselines were obtained than when separation was carried out using MEKC. Another aspect related to the application to real samples was the lack of precision encountered upon evaluating the electrophoretic signals generated when using SPE coupled with NA-CZE. Here, we demonstrate the importance of choosing an appropriate internal standard for analyte quantification. It is recommended that a triazine belonging to the same family as that of the triazine to be determined should be used as internal standard.

Chromatography, Micellar Electrokinetic Capillary↗

1, 2, 4-Triazine N-oxide derivatives: studies as potential hypoxic cytotoxins. Part II.

New 1, 2, 4-Triazine N-oxide and N, N'-dioxide derivatives were synthesized in order to obtain compounds as selective hypoxic cell cytotoxins. The starting heterocycles have been prepared using a standard microwave oven in a clean and good-yielded process. The reactivity of methyl-1, 2, 4-triazine N(4)-oxide and N(1), N(4)-dioxide with different electrophilic agents has been studied. The desired products were obtained only when iminium electrophiles were employed. The regioselectivity of this process has been studied by means of experimental and theoretical (at ab initio level) procedures. Theoretically was expected that the most stable intermediates where the benzylic-like anion from position 5. A fact which agreed with the experimental observed regioselectivity. The new compounds were tested for their cytotoxicity in oxia and hypoxia. Some of them proved to be less active in hypoxic conditions than tirapazamine, 3-amino-benzo[1, 2-e]1, 2, 4-triazine N(1), N(4)-dioxide. Derivative 19, 6-methyl-5-[2-(5-nitrothienyl)ethenyl)-1, 2, 4-triazine N(4)-oxide, was the most cytotoxic compound, but it was non-selective.

Animals↗

An enantiomeric nanoscale architecture obtained from a pseudoenantiomeric aggregate: covalent fixation of helical chirality formed in self-assembled discotic triazine triamides by chiral amplification.

Covalent fixation of a chiral helical structure which is created in a self-assembling system by a chiral-amplification method based on the sergeants/soldiers principle is reported. Disk-shaped triazine triamides self-assembled to form columnar-type helical aggregates through pi-stacking interactions among the central triphenyltriazine moieties, hydrogen-bonding interactions among the amide groups, and van der Waals interactions among the alkyl groups in nonpolar solvents such as hexane, octane, toluene, and p-xylene. When the achiral triazine triamide soldier component is mixed with a tiny amount of the chiral triazine triamide sergeant component, control of the intrinsic supramolecular helicity of the self-assembled soldier component by the sergeant component leads to chiral amplification and formation of a pseudoenantiomeric aggregate with only one handedness of the helix. The helicity can be preserved by ring-closing olefin metathesis polymerization mediated by Grubbs catalyst when an achiral component with terminal olefinic groups forms the pseudoenantiomeric aggregate in the presence of a tiny amount of the chiral component without olefinic groups. After polymerization and removal of the chiral component, the polymeric architecture obtained from the achiral soldier component is optically active and thus can be regarded as an enantiomeric object in which the chiral information transferred from the chiral sergeant component is preserved. The nanoscale chiral structure is fixed perfectly, as indicated by CD spectroscopic evidence obtained in a polar THF medium at high temperature and low concentration. AFM and TEM observations show a nanoscale fibrous structure with a diameter of 2-4 nm, which corresponds to the molecular size of the triazine triamide monomer.

Amides↗

On the low-lying excited states of sym-triazine-based herbicides.

We report a joint computational and luminescence study on the low-lying excited states of sym-triazines, namely, 1,3,5-triazine (1) and the ubiquitous herbicides atrazine [6-chloro-N2-ethyl-N4-isopropyl-1,3,5-triazine-2,4-diamine (2)] and ametryn [6-methylthio-N2-ethyl-N4-isopropyl-1,3,5-triazine-2,4-diamine (3)]. Geometrical structures, energetics, and transition and state properties of I and 2 were computed at the TD-DFT, CASSCF, and CASPT2 levels of theory. The fluorescence and phosphorescence emission spectra, lifetimes, and fluorescence quantum yields were measured for the three compounds, and from these, the energies of the lowest excited states and their corresponding radiative rates were determined. The predictions from CASPT2 calculations are in good agreement with the experimental results obtained from the luminescence studies and allow the interpretation of different absorption and emission features.

Absorption↗

Up-and-down procedure (UDP) determinations of acute oral toxicity of nitroso degradation products of hexahydro-1,3,5-trinitro-1,3,5-triazine (RDX).

Hexahydro-1,3,5-trinitro-1,3,5-triazine (RDX), a widely used military explosive and soil and ground water contaminant of munitions manufacturing and artillery training sites, undergoes microbial nitroreductase metabolism to 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). Human occupational and accidental exposures to RDX, as well as acute oral exposures in rats, result in seizures, but little is known about the toxicity of the RDX degradation products. The main objective of the present study was to determine the oral LD50 of the most potent RDX N-nitroso product in female Sprague-Dawley rats using the recently validated up-and-down procedure (UDP). With only 26 rats, MNX was identified as the most potent metabolite and a maximum likelihood estimate of 187 mg kg(-1) (95% confidence interval 118-491 mg kg(-1)) for its LD50 was established and found equivalent to that of RDX determined with the same protocol. CNS toxicity, manifested as forelimb clonic seizures progressing to generalized clonic-tonic seizures, was the critical adverse effect. Further, confirmation of the UDP LD50 for MNX with a fixed-dose design enabled identification of 94 mg kg(-1) as the highest nonlethal dose. An ED50 of 57 mg kg(-1) was determined for neurotoxicity, while splenic hemosiderosis and decreased blood hematocrit and hemoglobin concentration occurred with a threshold at 94 mg kg(-1) in 14-day survivors. These studies, while providing new toxicity data necessary for the management of RDX-contaminated sites, illustrate the efficiency of the UDP for comparative acute toxicity determinations and its value in guiding further characterization of dose dependency of identified adverse effects.

Animals↗

Triazine resistance in Amaranthus tuberculatus (Moq) Sauer that is not site-of-action mediated.

While surveying Illinois Amaranthus tuberculatus (Moq) Sauer (tall waterhemp) half-sib populations for herbicide response variability, several were observed to segregate for resistance to atrazine. Studies were conducted on greenhouse-grown A tuberculatus plants to compare atrazine responses among populations that were segregating for resistance (SegR), uniformly sensitive (UniS) or uniformly resistant (UniR). In chlorophyll fluorescence assays, leaves of plants from the SegR and UniS populations displayed changes in fluorescence after treatment with atrazine, indicating that atrazine was inhibiting electron transport of photosystem II in chloroplasts. Sequencing of a fragment of psbA, which encodes the D1 protein, revealed that the SegR population did not contain the amino acid substitution that is typically found in triazine-resistant plants. Whole-plant herbicide dose-response experiments revealed that, relative to the UniS population, atrazine resistances in the UniR and SegR populations were > 770-fold and 16-fold, respectively. The SegR population was also resistant to cyanazine (59-fold), but not to metribuzin, linuron or pyridate. Triazine resistance in the SegR population was shown to be a nuclear inherited trait, unlike maternal inheritance of site-of-action mediated triazine resistance found in the UniR population. Taken collectively, these findings confirm the existence of two distinct triazine resistance mechanisms in A tuberculatus.

Amaranthus↗

A DNA-electrochemical biosensor for screening environmental damage caused by s-triazine derivatives.

An electrochemical DNA-biosensor has been used to investigate the interactions between DNA and members of a group of ten derivatives of 1,3,5-triazine herbicides: chloro-s-triazines (atrazine, propazine, terbutylazin, and cyanazin), thiomethyl-s-triazines (ametryn, prometryn, terbutryn, and simetryn), and methoxy-s-triazines (prometon and terbumeton). A UV spectrophotometric study of this group of herbicides was also undertaken. Of this group only cyanazin could be oxidized in aqueous solution using a glassy carbon electrode. Use of the electrochemical DNA-biosensor revealed the occurrence of a time-dependent interaction of all the herbicides with DNA, via the appearance of guanine, guanosine, and adenosine oxidation signals that correspond to DNA damage. Adduct formation between the herbicide and the DNA purine bases guanine and adenine is suggested as a mechanism.

Biosensing Techniques↗

The role of organic colloids in herbicide transfer to rivers: a quantitative study of triazine and phenylurea interactions with colloids.

For moderately hydrophobic compounds such as most pesticides adsorption on colloids (<0.2 microm) may play a key role in pesticide mobility as well as in their degradation by chemical and microbiological processes. However, until now, pesticide-organic colloid interactions are poorly understood. Quantitative data for sorption equilibria on colloids of two series of herbicides including triazines (atrazine, simazine, terbutylazine, prometryne, desethylatrazine, and desisopropylatrazine) and phenylureas (isoproturon, linuron, neburon, and diuron) sampled in the Seine river (urban zone) and the Marne river (agricultural zone) are presented. Partition coefficient of herbicides on colloids (K(com)), were evaluated by solid-phase extraction coupled with high-performance liquid chromatography-UV diode-array detection (SPE-HPLC-UV/DAD). In the case of triazines a satisfactory log-log correlation was found between K(com) and octanol-water coefficient (K(ow)) values. Phenylureas did not obey this correlation, with K(com) values being about two times higher than those of triazines. The existence of two distinct types of adsorption behaviour on colloids partly explains the different occurrence of triazines and phenylureas in surface waters.

Adsorption↗

Clean-up of triazines in vegetable extracts by molecularly-imprinted solid-phase extraction using a propazine-imprinted polymer.

An analytical methodology based on a molecularly imprinted solid-phase extraction (MISPE) procedure was developed for the determination of several triazines (atrazine, simazine, desethylatrazine (DEA), desisopropylatrazine (DIA), and propazine) in vegetable samples. A methacrylic acid-based imprinted polymer was prepared by precipitation polymerisation using propazine as template and toluene as porogen. After removal of the template by Soxhlet extraction, the optimum loading, washing, and elution conditions for MISPE of the selected triazines were established. The optimised MISPE procedure was applied to the extraction of the selected triazines in pea, potato, and corn sample extracts and a high degree of clean-up was obtained. However, some remaining interferences, non-specifically and strongly bound to the polymeric matrix, appeared in the chromatogram, preventing quantification of DIA in potatoes and DIA, DEA, and propazine in corn samples. Thus, a new clean-up protocol based on the use of a non-imprinted polymer for removal of these interferences prior to the MISPE step was developed. By following the new two-step MISPE procedure, the matrix compounds were almost completely removed, allowing the determination of all the triazines selected at concentration levels below the established maximum residue limits, making the developed procedure suitable for monitoring these analytes in vegetable samples.

Chromatography, High Pressure Liquid↗

Biodegradation of hexahydro-1,3,5-trinitro-1,3,5-triazine by novel fungi isolated from unexploded ordnance contaminated marine sediment.

Undersea deposition of unexploded ordnance (UXO) constitutes a potential source of contamination of marine environments by hexahydro-1,3,5-trinitro-1,3,5-triazine (RDX) and octahydro-1,3,5,7-tetranitro-1,3,5,7-tetrazocine (HMX). Using sediment from a coastal UXO field, Oahu Island, Hawaii, we isolated four novel aerobic RDX-degrading fungi HAW-OCF1, HAW-OCF2, HAW-OCF3 and HAW-OCF5, tentatively identified as members of Rhodotorula, Bullera, Acremonium and Penicillium, respectively. The four isolates mineralized 15-34% of RDX in 58 days as determined by liberated 14CO2. Subsequently we selected Acremonium to determine biotransformation pathway(s) of RDX in more details. When RDX (100 microM) was incubated with resting cells of Acremonium we detected methylenedinitramine (MEDINA), N2O and HCHO. Also we detected hexahydro-1-nitroso-3,5-dinitro-1,3,5-triazine (MNX) together with trace amounts of hexahydro-1,3-dinitroso-5-nitro-1,3,5-triazine (DNX) and hexahydro-1,3,5-trinitroso-1,3,5-triazine (TNX). Under the same conditions MNX produced N2O and HCHO together with trace amounts of DNX and TNX, but we were unable to detect MEDINA. TNX did not degrade with Acremonium. These experimental findings suggested that RDX degraded via at least two major initial routes; one route involved direct ring cleavage to MEDINA and another involved reduction to MNX prior to ring cleavage. Nitrite was only detected in trace amounts suggesting that degradation via initial denitration did take place but not significantly. Aerobic incubation of Acremonium in sediment contaminated with RDX led to enhanced removal of the nitramine.

Biodegradation, Environmental↗

Herbicidal triazines: acute toxicity on Daphnia, fish, and plants and analysis of its relationships with structural factors.

The 24- and 48-hr EC50 immobilization test of Daphnia magna has been performed on 14 herbicidal triazines characterized by structural differences with respect to the substituent groups at the three carbon atoms in the s-triazinic ring. EC50 values of the tested compounds were found to vary within a factor of 6 to 7; such variations of toxicity have been analyzed in terms of structural variations concerning (i) the type of substituents, i.e., Cl, SCH3, or OCH3, at the carbon atom C-2, and (ii) the number and size of the alkyl groups at the aminic nitrogen atoms bound to the ring carbons C-4 and C-6. Literature data relative to the acute toxicity of the considered herbicides on fish and plants were also analyzed with reference to the above structural features. The possibility that separate contributions to toxic effects of triazines are provided by specific groups bound to the common structural moiety, constituted by the 1,3,5-triazinic ring, is examined and discussed.

Animals↗

N-Nitroso compounds produced in deer mouse (Peromyscus maniculatus) GI tracts following hexahydro-1,3,5-trinitro-1,3,5-triazine (RDX) exposure.

Given the potent carcinogenic effects of most N-nitroso compounds, the reductive transformation of the common explosive hexahydro-1,3,5-trinitro-1,3,5-triazine (RDX) to a group of N-nitroso derivatives, 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) in the environment have caused concerns among the general public. Questions are arising about whether the same transformations also occur in mammals, and if true, to what extent. This study investigated the N-nitroso derivatives production in the deer mouse GI tract following RDX administration. Findings verified that such transformations do occur in the mammalian GI tract at notable levels: the average MNX concentrations in deer mice stomach were 85 microg/kg and 1318 microg/kg for exposure to 10mg/kg and 100mg/kg diet, respectively. DNX in stomach were 217 microg/kg for the 10mg/kg dose group and 498 microg/kg for the 100mg/kg dose group. Changes in other toxic endpoints including body weight gain, food consumption, organ weight, and behavior were also reported.

Animals↗