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PubMed2002

Hierarchical formation of helical supramolecular polymers via stacking of hydrogen-bonded pairs in water.

Bifunctional ureido-s-triazines provided with penta(ethylene oxide) side chains are able to self assemble in water, leading to helical columns via cooperative stacking of the hydrogen-bonded pairs (DADA array). Monofunctional ureido-s-triazines do not form such helical architectures. The presence of a linker, covalently connecting the two ureido-s-triazine units, is essential as it generates a high local concentration of aromatic units, favorable for stacking interactions. This hydrophobic stacking of the aromatic units occurs at concentrations as low as 5 x 10(-6) M and can be visualized by using fluorescence spectroscopy. The stacking generates a hydrophobic microenvironment that allows intermolecular hydrogen bonding to occur at higher concentrations because the hydrogen bonds are shielded from competitive hydrogen bonding with water. This hierarchical process results in the formation of a helical self-assembled polymer in water at concentrations above 10(-4) M. Chiral side chains attached to the ureido-s-triazine units bias the helicity of these columns as concluded from CD spectroscopy and "Sergeants and Soldiers" experiments.

Binding, Competitive↗
PubMed1981

Photoaffinity labeling of an herbicide receptor protein in chloroplast membranes.

2-Azido-4-ethylamino-6-isopropylamino-s-triazine (azido-atrazine) inhibits photosynthetic electron transport at a site identical to that affected by atrazine (2-chloro-4-ethylamino-6-isopropylamino-s-triazine). The latter is a well-characterized inhibitor of photosystem II reactions. Azido-atrazine was used as a photoaffinity label to identify the herbicide receptor protein; UV irradiation of chloroplast thylakoids in the presence of azido[(14)C]atrazine resulted in the covalent attachment of radioactive inhibitor to thylakoid membranes isolated from pea seedlings and from a triazine-susceptible biotype of the weed Amaranthus hybridus. No covalent binding of azido-atrazine was observed for thylakoid membranes isolated from a naturally occurring triazine-resistant biotype of A. hybridus. Analysis of thylakoid polypeptides from both the susceptible and resistant A. hybridus biotypes by sodium dodecyl sulfate/polyacrylamide gel electrophoresis, followed by fluorography to locate (14)C label, demonstrated specific association of the azido[(14)C]atrazine with polypeptides of the 34- to 32-kilodalton size class in susceptible but not in resistant membranes.

Journal Article↗
PubMed1979

Modification of Herbicide Binding to Photosystem II in Two Biotypes of Senecio vulgaris L.

THE PRESENT STUDY COMPARES THE BINDING AND INHIBITORY ACTIVITY OF TWO PHOTOSYSTEM II INHIBITORS: 3-(3,4-dichlorophenyl)-1,1-dimethylurea (diuron [DCMU]) and 2-chloro-4-(ethylamine)-6-(isopropyl amine)-S-triazene (atrazine). Chloroplasts isolated from naturally occurring triazine-susceptible and triazine-resistant biotypes of common groundsel (Senecio vulgaris L.) showed the following characteristics. (a) Diuron strongly inhibited photosynthetic electron transport from H(2)O to 2,6-dichlorophenolindophenol in both biotypes. Strong inhibition by atrazine was observed only with the susceptible chloroplasts. (b) Hill plots of electron transport inhibition data indicate a noncooperative binding of one inhibitor molecule at the site of action for both diuron and atrazine. (c) Susceptible chloroplasts show a strong diuron and atrazine binding ((14)C-radiolabel assays) with binding constants (K) of 1.4 x 10(-8) molar and 4 x 10(-8) molar, respectively. In the resistant chloroplasts the diuron binding was slightly decreased (K = 5 x 10(-8) molar), whereas no specific atrazine binding was detected. (d) In susceptible chloroplasts, competitive binding between radioactively labeled diuron and non-labeled atrazine was observed. This competition was absent in the resistant chloroplasts.We conclude that triazine resistance of both intact plants and isolated chloroplasts of Senecio vulgaris L. is based upon a minor modification of the protein in the photosystem II complex which is responsible for herbicide binding. This change results in a specific loss of atrazine (triazine)-binding capacity.

Journal Article↗
PubMed1989

The mechanism of herbicide resistance in tobacco cells with a new mutation in the q(b) protein.

A new mutant of the psbA gene conferring resistance to 2-chloro-4-(ethylamino)-6-(isopropylamino)-s-triazine (atrazine) was obtained by selection of photomixotrophic tobacco (Nicotiana tabacum cv Samsun NN) cells. The 264th codon AGT (serine) in the wild psbA gene was changed to ACT (threonine) in these mutant tobacco cells. All other higher plants resistant to atrazine exhibit a change to GGT (glycine) in this codon. Measurements of Hill reaction activity and chlorophyll fluorescence showed that the threonine 264-containing plastoquinone serving as secondary stable electron acceptor of PSII (Q(B) protein) had not only strong resistance to triazine-type herbicides but also moderate resistance to substituted urea-type herbicides. Threonine-type Q(B) protein showed especially strong resistance to methoxylamino derivatives of the substituted urea herbicides. The projected secondary structures of the mutant Q(B) proteins indicate that the cross-resistance of threonine 264 Q(B) protein to triazine and urea herbicides is mainly due to a conformational change of the binding site for the herbicides. However, the glycine 264 Q(B) protein is resistant to only triazine herbicides because of the absence of an hydroxyl group and not because of a conformational change.

Journal Article↗
PubMed2001

Topochemically controlled solid-state methyl rearrangement in thiocyanurates.

4,6-Dimethoxy-3-methyl-1,3,5-triazine-2(3H)-thione crystallizes in two polymorphic forms, needles and plates. In the needle-shaped crystals (9a) the molecules occupy the crystallographic mirror plane, thus the layers are stacked along the b axis. The molecules of the other polymorph [plate-shape crystals, (9b)] are packed in a herringbone packing mode. Upon heating, (9b) undergoes a phase transition to form (9a). At 378 K the needles undergo O --> S topochemically controlled methyl transfer in the solid state to produce 1-methyl-4-methoxy-6-methylthio-1,3,5-triazine-2(1H)-one in 75% yield. The enthalpy of the rearrangement is estimated to be -39.1 kJ mol(-1). 1-Methyl-6-methoxy-4-methylthio-1,3,5-triazine-2(1H)-thione crystallizes in space group P2(1) with two crystallographically independent molecules in the asymmetric unit. Compound (9b) undergoes O --> S methyl transfer in the solid state at 373 K. The rearrangement is topochemically assisted and the product, 1-methyl-2,4-bismethylthio-1,3,5-triazine-6(1H)-one, is obtained in quantitative yield. The enthalpy of the rearrangement is estimated to be -58.8 kJ mol(-1). The crystal structures of the compounds as well as their DSC thermographs are described and discussed. Energy calculation by ab initio methods shows that the driving force for the reactions is the difference between the molecular energies of the pre-rearranged compounds and their products, 54.2 and 59.3 kJ mol(-1) in the two cases, respectively.

Journal Article↗
PubMedDate not supplied

Herbicides in ground water beneath Nebraska's Management Systems Evaluation Area.

Profiles of ground water pesticide concentrations beneath the Nebraska Management Systems Evaluation Area (MSEA) describe the effect of 20 yr of pesticide usage on ground water in the central Platte Valley of Nebraska. During the 6-yr (1991-1996) study, 14 pesticides and their transformation products were detected in 7848 ground water samples from the unconfined water table aquifer. Triazine and acetamide herbicides applied on the site and their transformation products had the highest frequencies of detection. Atrazine [6-chloro-N-ethyl-N'-(1-methylethyl)-1,3,5-triazine-2,4,-diamine] concentrations decreased with depth and ground water age determined with 3H/3He dating techniques. Assuming equivalent atrazine input during the past 20 yr, the measured average changes in concentration with depth (age) suggest an estimated half-life of >10 yr. Hydrolysis of atrazine and deethylatrazine (DEA; 2-chloro-4-amino-6-isopropylamino-s-triazine) to hydroxyatrazine [6-hydroxy-N-ethyl-N'-(1-methylethyl)-1,3,5-triazine-2,4-diamine] appeared to be the major degradation route. Aqueous hydroxyatrazine concentrations are governed by sorption on the saturated sediments. Atrazine was detected in the confined Ogallala aquifer in ultra-trace concentrations (0.003 microg L(-1)); however, the possibility of introduction during reverse circulation drilling of these deep wells cannot be eliminated. In fall 1997 sampling, metolachlor [2-chloro-N-(2-ethyl-6-methylphenyl)-N-(2-methoxy-1-methylethyl) acetamide] was detected in 57% of the 230 samples. Metolachlor oxanilic acid [(2-ethyl-6-methylphenyl)(2-methoxy-1-methylethyl) amino]oxo-acetic acid] was detected in most samples. In ground water profiles, concentrations of metolachlor ethane sulfonic acid [2-[(ethyl-6-methylphenyl)(2-methoxy-1-methylethyl)amino]-2-oxo-ethanesulfonic acid] exceeded those of deethylatrazine. Alachlor [2-chloro-N-(2,6-diethylphenyl)-N-(methoxymethyl)acetamide] was detected in <1% of the samples; however, alachlor ethane sulfonic acid [2-[(2,6-diethylphenyl)(methoxymethyl)amino]-2-oxoethanesulfonic acid] was present in most samples (63%) and was an indicator of past alachlor use.

Adsorption↗
PubMed2005

Effect of corn root exudates on the degradation of atrazine and its chlorinated metabolites in soils.

DIMBOA (3,4-dihydro-2,4-dihydroxy-7-methoxy-2H-1,4-benzoxazin-3-one), a major benzoxazinone of Poaceae plants, was isolated and purified from corn seedlings. The effect of isolated and purified DIMBOA on the degradation of atrazine [2-chloro-4-(ethylamino)-6-(isopropylamino)-s-triazine], and its toxic breakdown products, desethylatrazine [2-chloro-4-amino-6-(isopropylamino)-s-triazine; DEA] and desisopropylatrazine [2-chloro-4-(ethylamino)-6-amino-s-triazine; DIA], was studied in the absence of plants using batch experiments, while the effect of corn root exudates on these compounds was determined in hydroponic experiments. Degradation experiments were performed in the presence and absence of 50 microM, 1 mM, or 5 mM DIMBOA resulting in ratios of DIMBOA to pesticide of 1:1, 20:1, and 100:1. We observed a 100% degradation of atrazine to hydroxyatrazine within 48 h at a ratio of DIMBOA to atrazine of 100:1. DIMBOA had the largest effect on atrazine, while it was about three times less effective on DEA and DIA. Corn (Zea mays L. cv. LG 2185) was exposed to 10 mg L(-1) of either atrazine, DEA, or DIA for 11 d in a growth chamber experiment. Up to 4.3 micromol L(-1) d(-1) of hydroxyatrazine were formed in the nutrient solutions by plants exposed to atrazine, while the formation of hydroxylated metabolites from plants exposed to DEA and DIA was smaller and also delayed. The formation of hydroxylated metabolites increased in the solution with plant age in all atrazine, DEA, and DIA treatments. HMBOA (3,4-dihydro-2-hydroxy-7-methoxy-2H-1,4-benzoxazin-3-one), the lactam precursor of DIMBOA, and a tentatively identified derivative of MBOA (2,3-dihydro-6-methoxy-benzoxazol-2-one) were detected in the corn root exudates. Mass balance calculations revealed that up to 30% of the disappearance of atrazine and DEA, and up to 10% of DIA removal from the solution medium in our study could be explained by the formation of hydroxylated metabolites in the solution itself. Our results show that higher plants such as corn have the potential to promote the hydrolysis of triazine residues in soils by exudation of benzoxazinones.

Atrazine↗
PubMed1984

[The almitrine dimesylate molecule. Various structure-activity relationship aspects].

The improvement in PaO2 induced by almitrine bismesylate is due to better adjustment between alveolar ventilation and lung perfusion (VA/Q ratio). Experimental studies and clinical pharmacology suggest that this improvement involves changes in both alveolar ventilation and pulmonary circulation. By synthesizing and testing compounds with different structures in a series of trisubstituted triazines, it has been possible to determine qualitative structure-activity relationships and to select almitrine bismesylate is due to better adjustment between the greatest, most rapid and longest lasting increase in PaO2. Almitrine bismesylate is a molecule with three components: a di-allylamino-triazine group, a piperazine ring and a bis-parafluoro-benzhydryl fraction. The di-allylamino-triazine group may be regarded as responsible for the effects on blood gases and ventilation. The presence of two allyl-amino substituents is an absolute prerequisite, and the triazine ring can possibly be replaced by a very similar pyrimidine ring. The piperazine ring is mainly responsible for dissociation between the effects on blood gases and on ventilation as well as for the general kinetics of the biological action of the drug. Molecules of this series which have a pyrrolidine ring or an azetidine ring instead of a piperazine ring do increase PaO2 but much more slowly than almitrine bismesilate. Finally, the bis-parafluoro-benzhydryl group modulates the intensity and duration of the effects on blood gases. Other constituents, such as the cinnamylamino, alpha-cyclohexyl-parafluorobenzyl, beta-naphthyl methyl or 5-fluoro-benzofluranyl-methyl groups also exert favourable biological activities comparable to those of the bis-parafluorobenzhydryl group characteristic of almitrine bismesylate.

Almitrine↗
PubMed2006

Ion-pair association and acid-base equilibria in nonaqueous capillary electrophoresis of weakly basic compounds.

CE in nonaqueous media was used to study the migrating behavior of two weakly basic s-triazine pesticides and one of their metabolites. The target pesticides were selected to be representative for each of the two main groups: propazine and deethylatrazine for the chloro-s-triazines group and ametryn for the methylthio-s-triazines group. To elucidate the phenomena involved, systematic studies were carried out in the different organic media studied. Absolute mobilities were determined in 50% v/v methanol (MeOH)/ACN by extrapolation of the effective mobilities to zero ionic strength in the presence of different concentrations of perchloric acid. Conductivity measurements performed in MeOH and 50 and 20% v/v methanol/ACN permitted the evaluation of the associations of the components of the BGE. The effects of ionic strength on the actual mobilities of the compounds were determined in the presence of perchloric acid and SDS in different organic media. Two different ion-pair equilibria were considered: one due to the presence of perchlorate anions present in the BGE and second that from the added dodecyl sulfate anions. Bearing in mind that these weakly basic compounds can exhibit ion-pair and acid-base equilibria, the acid-base and ion-pair parasite reaction coefficients were determined. Finally, the effects of ionic strength, ion-pair interactions and acid-base properties on the effective electrophoretic mobilities of the analytes are discussed.

Acetonitriles↗
PubMedDate not supplied

Effects of tail-like substituents on the binding of competitive inhibitors to the Q(B) site of photosystem II.

The QB quinone-binding site of photosystem II is an important target for herbicides. Two major classes of herbicides are based on s-triazine and phenylurea moieties. A small library of triazine and phenylurea compounds has been synthesized which have tail-like substituents in order to test the effects of charge, hydrophobicity and size of the tail on binding properties. It is found that a tail can be attached to one of the alkylamino groups of triazine-type herbicides or to the para position of phenylurea-type herbicides without loss of binding, provided that the tail is hydrophobic. This indicates that the herbicides must be oriented in the QB site such that these positions point toward the natural isoprenyl tail-binding pocket that extends out of the Q(B) site. In turn, the requirement that the tail must extend out of the QB site constrains the size of the other herbicide substituents in the pocket. This is in agreement with the presumed orientation and fit of ligands in the QB site. When longer hydrophobic tails are used, the binding penalty that occurs upon adding a charged substituent at the distal end is reduced. This allows the use of a series of tail substituents possessing a distal charge as an approximate molecular ruler to measure the distance from the QB site to the aqueous phase. Even a 10-carbon alkyl chain still shows a 4-fold effect from the presence or absence of a distal charge. Such a chain does not appear to be long enough to extend from the bulk aqueous phase to the QB site because binding is completely lost when a large hydrophilic domain (PEG(4000)) is attached to the distal end. Longer tails are effective only if they are sufficiently hydrophobic. An effort was made to use tailed herbicides for affinity binding of photosystem II. It was found that hydrophobic linkers promote nonspecific binding, but careful choice of solvent conditions, such as the use of excess nonionic detergent well above its critical micelle concentration, might obviate this problem during affinity-binding applications.

Binding, Competitive↗
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↗
PubMed2000

Oil-in-water emulsions as suitable working media for the direct polarographic determination of aziprotryne and desmetryne from its organic extracts in water samples.

The electroanalytical behavior of the reduction of the herbicides aziprotryne (2-azido-4-isopropylamino-6-methylthio-1,3,5-triazine) and desmetryne (4-isopropylamino-6-methylamino-2-methylthio-1,3,5-triazine) in oil-in-water emulsions is reported. This medium allows the differential pulse polarographic determination of these s-triazines directly from their sample extracts in an appropriate organic solvent. Sodium pentanesulfonate was chosen as the most suitable surfactant to be used as emulsifying agent, whereas ethyl acetate was selected as the organic solvent to form the emulsions. The peak current was maximum in a 0.3 mol L(-1) HClO4 medium of the continuous aqueous phase for aziprotryne, and at pH 3.0 for desmetryne, and the potential became more negative as the pH increased for both herbicides. The limiting current is diffusion controlled and the electrode process is irreversible. Four electrons are involved in the overall electrochemical reduction process as determined by controlled potential coulometry, whereas the alpha n(a) values suggested that two electrons are involved in the rate-determining step. Using differential pulse polarography, aziprotryne and desmetryne can be determined in the emulsified medium over the concentration ranges 1.0 x 10(-7)-1.0 x 10(-4) mol L(-1), with limits of detection of 4.5 x 10(-8) mol L(-1) and 6.6 x 10(-8) mol L(-1), respectively. The method was applied to the determination of aziprotryne and desmetryne in spiked irrigation water. At concentration levels of 6.0 x 10(-7) mol L(-1) aziprotryne and 4.0 x 10(-7) mol L(-1) desmetryne, recoveries of 94 +/- 3% and 94 +/- 4%, respectively, were obtained after preconcentration on Sep-Pack C18 cartridges. Finally, partial least-squares regression (PLSR) has been used for treatment of the polarographic data obtained from mixtures of aziprotryne, desmetryne and simazine in oil-in-water emulsions. The size of the calibration set was of 29 samples by ninety two current measurements at different potentials. Prediction of the herbicides concentration within the range 1.0 x 10(-6)-1.0 x 10(-5) mol L(-1) was possible.

Calibration↗
PubMed2001

Triazinyl derivatives that are potent inhibitors of glucose transport in Trypanosoma brucei.

Glucose transport in Trypanosoma brucei is facilitated by a transporter that is kinetically markedly different from its mammalian homologue. In this regard, the trypanosomal transporter may be selectively targeted. We investigated the potential of a series of triazinyl derivatives as inhibitors of glucose transport in T. brucei. A graded response of glucose transporter inhibition by these compounds was observed, with Cibacron blue 3GA, CiB, being the most potent. This inhibited transport by up to 90% in a concentration-dependent manner, with an IC50 of about 19.4 microM. A Dixon plot of different concentrations of this triazine and the rate of transport suggested that inhibition may be simple and competitive. The inhibition constant Ki was 14.8 microM. Although cytochalasin B has been widely reported to inhibit glucose uptake by mammalian and other eukaryotic glucose transporters, it had no effect at all on the trypanosome transporter at concentrations equivalent to those of the triazines. This may suggest structural differences between the trypanosome and mammalian glucose transporters and also suggests that the triazine moiety may serve as a template for the design potent trypanocides targeted at the glucose transporter.

Animals↗
PubMed2006

Structure basis for the inhibitory mechanism of a novel DNase gamma-specific inhibitor, DR396.

DNase gamma, a member of the DNase I family, has been suggested to cause DNA fragmentation during apoptosis. We recently identified 4-(4,6-dichloro-[1,3,5]-triazine-2-ylamino)-2-(6-hydroxy-3-oxo-3H-xanthen-9-yl)-benzoic acid (DR396) as a novel specific inhibitor for human DNase gamma [Sunaga, S.; Kobayashi, T.; Yoshimori, A.; Shiokawa, D.; Tanuma, S. Biochem. Biophys. Res. Commun.2004, 325, 1292]. However, the binding mode (coordinate) of DR396 to DNase gamma has not yet been defined. Here, we examined the molecular basis for the inhibitory activity of DR396 to DNase gamma by structure-based computational docking studies. In the blind-docking study using a human DNase gamma homology model, a unique binding site of DR396 was predicted, which is tentatively named the 'DNA trapping site' because of the binding domain of the unhydrolyzed DNA strand, but not the active site. Targeting the DNA trapping site as a hot spot, new human DNase gamma inhibitors were obtained from our diverse chemical library in silico. These inhibitors showed high correlations between their predicted binding-free energies (DeltaGs) and observed IC50 values in the DNA trapping site but not the active site. The IC50 of a regioisomer of DR396, 5-(4,6-dichloro-[1,3,5]-triazine-2-ylamino)-2-(6-hydroxy-3-oxo-3H-xanthen-9-yl)-benzoic acid (DF365), was 73 microM (DeltaG=-9.75 kcal/mol), a 20-fold weaker inhibitory ability than that of DR396 (IC50=3.2 microM, DeltaG=-11.22 kcal/mol). Fluorescein and triazine derivatives, partial structures of DR396, had little inhibitory activity for DNase gamma. Docking analyses of the interaction between DR396 and DNase gamma revealed that DR396 binds tightly to three subsites (S1, S2, and S3) in the trapping site of DNase gamma by forming six hydrogen bonds, whereas DF365 and the partial structures are unable to form hydrogen bonds at all three subsites. These findings suggest that the specificity and potency of the inhibitory activity of DR396 for DNase gamma is due to the specific interaction of DR396 with three subsites in the DNA trapping site of DNase gamma.

Amino Acid Sequence↗
PubMed2004

Degradation of the antifouling compound Irgarol 1051 by manganese peroxidase from the white rot fungus Phanerochaete chrysosporium.

Irgarol 1051 (2-methylthio-4-tert-butylamino-6-cyclopropylamino-s-triazine), a derivative of s-triazine herbicide, is an antifouling compound used as an alternative to organotins. The compound is highly persistent and is known to be biodegraded only by the white rot fungus, Phanerochaete chrysosporium. We used partially purified manganese peroxidase (MnP) prepared from P. chrysosporium to evaluate its capacity to degrade Irgarol 1051. MnP degraded Irgarol 1051 to two major products, one identified as M1 (identical to GS26575, 2-methylthio-4-tert-butylamino-6-amino-s-triazine) and the other not identified but with same mass spectrum as M1 and a different ultraviolet spectrum. This report clearly demonstrates that this ligninolytic enzyme is involved in the degradation of Irgarol 1051.

Biodegradation, Environmental↗
PubMed2005

Assessment of the risk posed by the antifouling booster biocides Irgarol 1051 and diuron to freshwater macrophytes.

Antifouling paints are used to reduce the attachment of living organisms to the submerged surfaces of ships, boats and aquatic structures, usually by the release of a biocide. Two 'booster' biocides in common use are the triazine herbicide Irgarol 1051 (N-2-methylthio-4-tert-butylamino-6-cyclopropylamino-s-triazine), and diuron (1-(3,4-dichlorophenyl)-3,3-dimethylurea), which are designed to inhibit algal photosynthesis. Previous research has been directed at the effects of these compounds in marine and estuarine environments. In 2001 we sampled the main rivers and shallow freshwater lakes (Broads) of East Anglia UK for Irgarol 1051, its metabolite GS26575 (2-methylamino-4-tert-butylamino-6-amino-s-triazine) and diuron in order to establish the baseline environmental concentrations of these compounds in freshwater systems of eastern UK and to investigate their possible effects on aquatic plants. Irgarol 1051, GS26575 and diuron were found in water samples collected from 21 locations. The highest concentrations were found in the Norfolk and Suffolk Broads in May. The rivers Great Ouse, Wissey, Bure and Yare also contained all three compounds, as did the Great Ouse Cut-off Channel. The toxicity of these biocides to three macrophyte species (Apium nodiflorum, Chara vulgaris, and Myriophyllum spicatum) was investigated. Deleterious effects on relative growth rate, the maximum quantum efficiency (Fv/Fm) of photosystem II and, for Apium, root mass production were found. C. vulgaris was generally most sensitive; growth, especially of roots, was strongly affected in A. nodiflorum; growth rate of M. spicatum was sensitive to diuron. No observed effect concentrations (NOEC) were interpolated using standard toxicological analysis. These were compared with measured environmental concentrations (MEC) to determine the ranges of risk quotients (MEC/NOEC). Both Irgarol 1051 and diuron represented significant risks to A. nodiflorum and C. vulgaris in this area.

Chara↗
PubMed2006

Comparison of a non-aqueous capillary electrophoresis method with high performance liquid chromatography for the determination of herbicides and metabolites in water samples.

A method of capillary electrophoresis (CE) for the determination of triazine herbicides and some of their main metabolites in water samples has been developed. The proposed CE method includes an off-line solid-phase extraction (SPE) procedure with LiChrolut EN sorbent coupled to a non-aqueous capillary electrophoresis (NACE) separation with UV detection. The target compounds were the chloro-s-triazines simazine, atrazine, propazine; the methyltio-s-triazines ametryn and prometryn and three main derivatives from the atrazine degradation products; namely, deethylatrazine, deethylhydroxyatrazine and deisopropylhydroxyatrazine. The analytical characteristics of the CE method are reported. The repeatability of the method was studied considering the different steps of the method separately in order to determine the contributions of each step to the total variability of the method. The NACE-UV results are compared with those obtained with a high performance liquid chromatography with UV detection (HPLC-UV) method. The same off-line SPE procedure was applied to both techniques. The results obtained show that both methods afford the same results in the analysis of surface and drinking water samples, with a level of significance regarding the F- and t-tests greater than 0.05 in all the cases. The detection limits in surface water samples were in the 0.04-0.32 microg l(-1) and 0.11-1.2 microg l(-1) ranges for the NACE-UV and HPLC-UV methods, respectively. The recoveries (spiked/found) were significantly 100% in all cases.

Atrazine↗
PubMed2006

Fenton-enhanced gamma-radiolysis of cyanuric acid.

Degradation of cyanuric acid (OOOT), a stable end product of oxidative decomposition of atrazine, is investigated in a combined field of gamma radiolysis and fenton reaction. The reaction of hydroxyl radical (OH) at pH 6 was carried out by irradiating N(2)O saturated aqueous solutions containing OOOT (1 x 10(-3) mol dm(-3)), and this resulted only a marginal degradation (20%). However, when the same reaction was carried out in the presence of varying concentrations of ferrous sulfate ((5-10)x10(-5) mol dm(-3)), the decay of OOOT has been enhanced to more than 80%. This decay followed a first order kinetics. Nearly similar effects were observed with another triazine derivative, 2,4-dioxohexahydro-1,3,5-triazine (DHT). Two major reaction mechanisms are proposed for the enhanced decay of OOOT. The formation of unstable hydroxyl radical adducts from the reaction of .OH which is the result of gamma radiolysis and the Fenton reaction (resulting from the reaction of the added Fe(II) and of the H(2)O(2) from the radiolysis of water), is proposed as the first mechanism. The second mechanism, which is likely the major contributor to degradation, is proposed as the reaction of a nucleophilic adduct, Fe(II)OOH, which could directly react with the electron deficient triazine ring. It is highlighted that such degradation reactions must be explored for the complete degradation of the byproducts of the oxidative decomposition of atrazine.

Environmental Restoration and Remediation↗