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Photo-induced degradation of diuron in aqueous solution by nitrites and nitrates: kinetics and pathways.

The photo-induced degradation of diuron (3-(3,4-dichlorophenyl)-1,1-dimethylurea) in aqueous solution under simulated solar irradiation has been investigated in the presence of NO3-/NO2- ions. The degradation rates were compared by varying environmental parameters including substrate and inducer concentrations, oxygen content and pH. The photoproducts were identified by extensive LC-ESI-MS and LC-ESI-MS-MS studies after SPE preconcentration on prepacked cartridges. In both NO3- and NO2- conditions, oxidation of the N-(CH3)2 terminus group is the main process leading to the N-monodemethylated (NHCH3), N-formyl (N(CH3)CHO) and the uncommon and unstable carbinolamine (N(CH3)CH2OH) by-products. Cl/OH substituted and nitrated phenylureas are formed minorily. Degradation pathways involving OH* and NO2* (or dimer) radicals as reactive species are proposed.

Biodegradation, Environmental↗

Effect of drying on the desorption of diuron and terbuthylazine from natural soils.

This work was initiated to study the effects of climate induced soil water status variations which can reach extreme values under natural conditions on the sorption process of hydrophobic organic compounds. Based on the classical slurry batch methodology an approach is developed that allows the fast and careful complete drying of soil suspensions (microwave technique). Classical adsorption experiments were followed by three desorption steps with and without drying cycles. Drying and re-wetting enhanced the sorption-desorption hysteresis and Freundlich adsorption coefficients increased from 5.9 to 16 and 5.2 to 21 over three drying cycles for diuron and terbuthylazine respectively. Assuming the validity of a dual stage adsorption process, model evaluation suggests that drying is as a shrinking-like process leading to conformational changes of the dominant sorbent (soil organic matter) which restrict the intra-micro-particle diffusion. Rewetting only leads to a partial recovery of the diffusional pore space.

Adsorption↗

Assessment of photo-Fenton and biological treatment coupling for Diuron and Linuron removal from water.

The coupling of photo-Fenton (chemical) and biological treatments has been used for the removal of Diuron and Linuron herbicides from water. The chemical reaction was employed as a pre-treatment step for the conversion of the toxic and non-biodegradable herbicides into biodegradable intermediates that were subsequently removed by means of a biological sequencing batch reactor (SBR). Multivariate experimental design was used to select four photo-Fenton reagent dose combinations for the coupling experiments. Concentrations of hydrogen peroxide between 10 and 250 mg L(-1), and iron (II) concentrations between 2 and 20 mg L(-1) have been tested. 15.9 mg L(-1) of Fe(II) and 202 mg L(-1) of H(2)O(2) were needed to convert initial toxic and non-biodegradable herbicides into suitable intermediates for a subsequent biological treatment. Detrimental effects due to the excess of reactants were detected. Chemical oxygen demand (COD), average oxidation state (AOS), total organic carbon (TOC) and hydrogen peroxide concentration are the parameters used to trace the experiments course. Also, toxicity (EC(50)(15)) and biodegradability (BOD(5)/COD) tests were carried out at the end of each chemical oxidation. Complete disappearance of the herbicides from water was observed after the chemical treatment, while 3,4-dichloroaniline and 3,4-dichlorophenyl isocyanate were identified as the main by-products of the degradation process. Complete TOC removal was achieved after biological treatment in a SBR using a hydraulic retention time (HRT) of 2 days.

Biodegradation, Environmental↗

Kinetics of the chemical degradation of diuron.

The influence of pH and buffer concentration on the chemical degradation of diuron in water has been analysed over a wide temperature range. The process irreversibly gives 3,4-dichloroaniline as the only product containing the phenyl ring. H+, OH- and phosphate buffer are efficient catalysts of the reaction. The rate constant first increases rapidly at low buffer concentrations and then gradually levels off at higher ones. At 40 degrees C and high phosphate concentration (>0.01 M), or in the extreme pH regions, the half-life is approximately 4 months and the activation energy is 127 +/- 2 kJmol(-1).

Diuron↗

Liquid chromatographic determination of the herbicide diuron and its metabolite 3,4-dichloroaniline in asparagus.

A liquid chromatographic method is presented for the determination of the phenylurea herbicide diuron and its major metabolite, 3,4-dichloroaniline in asparagus. The method involves a simple isolation step using dichloromethane extraction, followed by reversed phase chromatography on a C18 column, using a basic aqueous-organic eluent and UV detection at 254 nm. The limit of determination is 0.02 mg/kg for both analytes.

Aniline Compounds↗

Identification of diuron and four of its metabolites in human postmortem plasma and urine by LC/MS with a moving-belt interface.

Unknown compounds that were not amenable to GC/MS were found during routine benzodiazepine HPLC screening in a postmortem case. The apparent thermolability made the application of liquid chromatography with mass spectrometry mandatory. The moving-belt interface was used because of its value for identification based on the use of both electron impact and chemical ionization, which provided information on both structure and molecular weight. The herbicide diuron and four of its metabolites were identified in plasma and urine and had a total concentration as high as 100 mg/L. Metabolism via demethylation and hydroxylation appeared to be the major routes.

Chromatography, High Pressure Liquid↗

HPLC analysis of diuron and metabolites in blood and urine.

A high-pressure liquid chromatographic method for the determination of diuron and its metabolites in human urine and blood is presented. The synthesis of different metabolites and of a suitable internal standard is described and the structure of the compounds is determined by mass spectrometry and nuclear magnetic resonance spectroscopy. The method is applied to an overdose case.

Adult↗

The Pesticide 3-(3,4-Dichlorophenyl)-1,1-dimethylurea (Diuron) Immobilized on Silica Gel Surface.

A route for 3-(3,4-dichlorophenyl)-1,1-dimethylurea (diuron) immobilization on silica gel was established after reacting at the first stage the precursor silylant agent 3-trimethoxysilylpropylamine to the support. The pesticide was covalently bonded to available amine groups of the precursor, giving 1.03 mmol of amine per gram of silica. Infrared, (13)C, and (29)Si NMR spectra are in agreement with the proposed reaction between nitrogen of the amine group of the previously anchored silica to carbon on the para-position of the aromatic ring of the pesticide. The immobilization is clearly affected by the presence or absence of disprotonating agent, to give 12.50 and 68.40% reaction yield, respectively; these results were confirmed through elemental analysis. Copyright 2001 Academic Press.

Journal Article↗

Interaction of chloroplasts with inhibitors: induction of chlorosis by diuron during prolonged illumination in vitro.

A primary symptom of diuron (DCMU) phytotoxicity in plants is the destruction of chlorophyll. To study this process in vitro, chloroplasts from pea leaves (Pisum sativum L.) have been incubated in the light with DCMU for periods of up to 34 hours. The sequence of photodestruction of chlorophylls and carotenoids has been followed to try and establish the nature of the chloroplast protection mechanisms that are destroyed by DCMU. beta-Carotene decays most rapidly, followed by chlorophyll a and xanthophylls which are destroyed in a constant ratio, followed finally by chlorophyll b. Bypassing the DCMU block in the electron transport system with an artificial electron donor provides complete protection against chlorophyll and carotenoid photodestruction. The same protection by this electron donor system is afforded to stroma-free lamellae from which soluble reductants have been removed so that NADPH formation, which has been proposed as an essential part of a protective xanthophyll cycle, is not possible. Both this and the simultaneous loss of chlorophyll a and xanthophylls tend to preclude the breakdown of a xanthophyll cycle from the possible protective mechanisms inhibited or destroyed by DCMU.Cofactors of cyclic electron transport also protect against DCMU-induced photodestruction of pigments. Their concentration dependence for this protection appears to reflect their various abilities to catalyze cyclic photophosphorylation. The extent to which the chlorophylls are destroyed in the major pigment-protein complexes from chloroplasts illuminated with and without DCMU has been measured. In the absence of DCMU, the light-harvesting chlorophyll a/b protein complex is destroyed most rapidly. In the presence of DCMU, the losses of chlorophyll a from the photosystem I P700-chlorophyll a protein and the chlorophyll a/b complex are about the same. Chlorophyll losses are matched by simultaneous losses of the protein moieties; spectral analyses show that the remaining chlorophyll a is held in a loose association with the protein. Phenazine methosulfate protects the chlorophyll of the light-harvesting complex in DCMU-treated chloroplasts more than it protects that in photosystem I. Data published on DCMU-induced fluorescence and its quenching are used to interpret the longer term DCMU-induced chlorosis and its protection. By blocking electron transport, conformational changes in the membrane that allow spillover of excitation energy from photosystem II to photosystem I (and quenching of fluorescence by this means) are prevented. The mechanism that normally protects the chloroplast against excessive illumination is then overloaded which impairs the harmless dissipation of absorbed light energy; consequently, the pigments are destroyed. When photosystem I is allowed to function again through cyclic electron flow, a necessary conformational change is believed to be reintroduced that once again allows the harmless dissipation of excitation energy through spillover. A functional electron transport system associated with photosystem I will protect against DCMU-induced chlorosis when the thylakoid membranes are intact, but when the P700-chlorophyll a protein complex is in isolation, there is only a limited degree of protection.

Journal Article↗

Atrazine, bromacil, and diuron resistance in chlamydomonas: a single non-mendelian genetic locus controls the structure of the thylakoid binding site.

A series of Chlamydomonas reinhardii mutants were selected for resistance to the herbicides atrazine, bromacil, and diuron. Four of these have reduced herbicide binding to the thylakoid membranes and show the non-Mendelian inheritance pattern characteristic of chloroplast genes. These mutants show a variety of selective alterations in binding of the three herbicides. These changes account for the observed patterns of in vivo cross-resistance. Analyses of chloroplast gene recombination indicate that these four mutations are in the same gene. Overall, the results suggest that this gene codes for a protein component of the herbicide binding site. One of the mutants has slow phototrophic growth and altered electron transport as has been observed in atrazine-resistant higher plant varieties, but the others are normal in these respects. The slow growth characteristic of this mutant seems to be the consequence of the same mutation which confers herbicide resistance.The mutants isolated also include a large number which achieve resistance by some secondary mechanism. These are all nuclear gene mutations, and represent numerous loci. They also show a variety of patterns of cross-resistance, but the mechanisms behind them have not yet been investigated.

Journal Article↗