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Guanidino labeling derivatization strategy for global characterization of peptide mixtures by liquid chromatography matrix-assisted laser desorption/ionization mass spectrometry.

Guanidination performed with isotopic isoforms of O-methylisourea was used in combination with reversed-phase liquid chromatography (LC) matrix-assisted laser desorption/ionization to characterize, both qualitatively and quantitatively, protein mixtures. Synthesis of (13)C- and (15)N(2)-labeled O-methylisourea sulfate produces a molecule that is 3 Da heavier than the light isotopic variant. Protein mixtures containing identical components in different concentration are pooled together following parallel derivatization. Relative quantification of protein mixtures is achieved by mass spectrometry. A difference of 3 Da allows negligible interference between the two isotopic clusters for quantification of peptides up to 1400 Da. Under these conditions, the chromatographic resolution achieved allows separation of different pairs of derivatized peptides without altering the retention time of structurally identical isotopic isoforms. Concomitant isolation of both chemically modified precursors is followed by tandem mass analysis. Activation of the ions via collisions with an inert gas produces isotopically derivatized fragment ions, which appear as doublets in the product ion spectrum. Since the modification occurs on the C-terminal lysine, ions incorporating the guanidino moiety on the C-terminus can be distinguished from those containing the original unmodified peptide N-terminus. Knowledge of the location of the proton can be beneficial to data interpretation and peptide sequencing.

Chromatography, Liquid↗

Approach for determining protein ubiquitination sites by MALDI-TOF mass spectrometry.

Protein ubiquitination plays an important role in the degradation and other functional regulation of cellular proteins in organisms ranging from yeasts to mammals. Trypsin digestion of ubiquitin conjugated proteins produces diglycine branched peptides in which the C-terminal Gly-Gly fragment of ubiquitin is attached to the epsilon-amino group of a modified lysine residue within the peptide. This provides a platform for mapping ubiquitination sites using mass spectrometry. Here we report the development of a novel strategy for determining posttraslational protein ubiquitination based on the N-terminal sulfonation of diglycine branched peptides. In contrast to conventional tandem MS spectra of native tryptic peptides, MALDI MS/MS analysis of a sulfonated tryptic peptide containing a diglycine branch generates a unique spectrum composed of a signature portion and a sequence portion. The signature portion of the spectrum consists of several intense ions resulting from the elimination of the tags, the N-terminal residues at the peptide and the branch, and their combination. This unique ion distribution pattern can distinguish ubiquitination modificatons from others and can identify the first N-terminal residues of the peptides as well. The sequence portion consists of an exclusive series of y-type ions and y' ions (differing by the loss of one glycine residue from the sulfonated diglycine branch) that can directly reveal the amino acid sequence of the peptide and the precise location of the ubiquitination site. The technique is demonstrated for a series of synthetic peptides and is validated by a model protein, tetraubiquitin. Our results show that the MALDI MS/MS analysis of sulfonated tryptic peptides can provide a highly effective method for the determination of ubiquitination substrates, ubiquitination sites on protein targets, and modification sites on ubiquitins themselves.

Amino Acid Sequence↗

Improved method for preparing N-hydroxysuccinimide ester-containing polymers for affinity chromatography.

N,N,N',N'-Tetramethyl(succinimido) uronium tetrafluoroborate is proposed as a reagent of choice for the activation of carboxyl groups and formation of N-hydroxysuccinimide esters on polymers. Unlike conventional methods which generate unstable gels, the reaction is appropriate for hydroxy-containing resins like Sepharose, cellulose, and dextran. The yields of activation and subsequent coupling capacity for ligands and proteins are very high. The respective columns can be used for affinity chromatography and immobilization of proteins.

Chromatography, Affinity↗

Kinetic characterization and cross-resistance patterns of HIV-1 protease mutants selected under drug pressure.

Eleven different recombinant, drug-resistant HIV-1 protease (HIV PR) mutants--R8Q, V32I, M46I, V82A, V82F, V82I, I84V, V32I/I84V, M46I/V82F, M46I/I84V, and V32I/K45I/F53L/A71V/I84V/L89M--were generated on the basis of results of in vitro selection experiments using the inhibitors A-77003, A-84538, and KNI-272. Kinetic parameters of mutant and wild-type (WT) enzymes were measured along with inhibition constants (Ki) toward the inhibitors A-77003, A-84538, KNI-272, L-735,524, and Ro31-8959. The catalytic efficiency, kcat/Km, for the mutants decreased relative to WT by a factor of 1.2-14.8 and was mainly due to the elevation of Km. The effects of specific mutations on Ki values were unique with respect to both inhibitor and mutant enzyme. A new property, termed vitality, defined as the ratio (Kikcat/Km)mutant/(Kikcat/Km)WT was introduced to compare the selective advantage of different mutants in the presence of a given inhibitor. High vitality values were generally observed with mutations that emerged during in vitro selection studies. The kinetic model along with the panel of mutants described here should be useful for evaluating and predicting patterns of resistance for HIV PR inhibitors and may aid in the selection of inhibitor combinations to combat drug resistance.

Amino Acid Sequence↗

Unfolding free energy changes determined by the linear extrapolation method. 1. Unfolding of phenylmethanesulfonyl alpha-chymotrypsin using different denaturants.

Characteristics and properties of the unfolding free energy change, delta G degrees N-U, as determined by the linear extrapolation method are assessed for the unfolding of phenylmethanesulfonyl chymotrypsin (PMS-Ct). Difference spectral measurements at 293 nm were used to define PMS-Ct unfolding brought about with guanidinium chloride, urea, and 1,3-dimethylurea. All three denaturants were shown to give identical extinction coefficient differences (delta epsilon N-U) between native and unfolded forms of the protein in the limit of zero concentration of denaturant. The independence of delta epsilon N-U on denaturant supports the linear extension of pre- and postdenaturational base lines into the transition zone, allowing evaluation of unfolding equilibrium constants based on the two-state assumption. An expression, based on the linear extrapolation method, was used to provide estimates of delta G degrees N-U for the three denaturants using nonlinear least-squares fitting of the primary data, delta epsilon versus [denaturant]. The three delta G degrees N-U values were identical, within error, suggesting that the free energy change is a property of the protein system and independent of denaturant. It is suggested that the error in delta G degrees N-U determined from use of the linear extrapolation method is significantly larger than commonly reported in the literature.

Binding Sites↗

Modeling of an annular photocatalytic reactor for water purification: oxidation of pesticides.

Photocatalytic oxidation (PCO) over titanium dioxide (TiO2) is a "green" sustainable process for the treatment and purification of water and wastewater. However, the application of PCO for wastewater treatment on an industrial scale is currently hindered by a lack of simple mathematical models that can be readily applied to reactor design. Current models are either too simplistic or too rigorous to be useful in photocatalytic reactor design, scale-up, and optimization. In this paper a simple mathematical model is presented for slurry, annular, photocatalytic reactors that still retains the essential elements of a rigorous approach while providing simple solutions. The model extends the applicability of the thin-film model of photocatalytic reactors previously presented to include the case of geometrically thick photoreactors (i.e., those reactors in which the thickness of the annular zone is significant as compared to the outer radius of the reactor). The model uses a novel six-flux absorption-scattering model to represent the radiation field in the reaction space, which assumes that scattered photons follow the route of the six directions of the Cartesian coordinates. The model was successfully validated with experimental results from the photocatalytic oxidation of the pesticide isoproturon in an experimental reactor. The mathematical model presented may be used as a tool for the design, scale-up, and optimization of annular photocatalytic reactors for water treatment and purification.

Catalysis↗

Chromium(V) peptide complexes: synthesis and spectroscopic characterization.

A series of stable Cr(V) model complexes that mimic the binding of Cr(V) to peptide backbones at the C-terminus of proteins have been prepared for N,N-dimethylurea derivatives of the tripeptides Aib3-DMF, AibLAlaAib-DMF, and AibDAlaAib-DMF (Aib = 2-amino-2-methylpropanoic acid, DMF = N,N-dimethylformamide). The Cr(ll) precursor complexes were synthesized by the initial deprotonation of the amide and acid groups of the peptide ligands in DMF with potassium tert-butoxide in the presence of CrCl2. The Cr(II) intermediates thus formed were then immediately oxidized to Cr(V) using tert-butyl hydroperoxide. Spectroscopic and mass-spectrometric analyses of the Cr(V) complexes showed that a new metal-directed organic transformation of the ligand had occurred. This involved a DMF solvent molecule becoming covalently bound to the amine group of the peptide ligand, yielding a urea group, and a third coordinated deprotonated urea nitrogen donor. A metal-directed oxidative coupling has been proposed as a possible mechanism for the organic transformation. The Cr(V/IV) reduction potential was determined for the three Cr(V) complexes using cyclic voltammetry, and in all cases it was quasi-reversible. These are the first isolated and fully characterized Cr(V) complexes with non-sulfur-containing peptide ligands.

Amides↗

Modeling of single-step and multistep adsorption isotherms of organic pesticides on soil.

The aim of this study was to investigate the sorption behavior and mechanisms of the organic pesticides on soil. To establish the sorption isotherms of six commonly used pesticides (acetochlor, atrazine, diazinon, carbendazim, imidacloprid, and isoproturon), laboratory equilibrium studies were performed at extended concentration ranges on brown forest soil using the batch equilibrium technique. The pesticide concentrations in the equilibrated liquid phase were quantified with high-performance liquid chromatograph by ultraviolet detection. The adsorption processes could be described by a single-step (Langmuir) isotherm for acetochlor and carbendazim, by a two-step curve for diazinon, isoproturon, and atrazine, and by a three-step curve for imidacloprid. A nonlinear mathematical model-derived from the Langmuir equation-has been developed that represents well the detected single-step and multistep shaped adsorption isotherms. The interpreted model was found to fit the experimental data well and allows the description of the adsorption profile with great precision. The altered adsorption activity, which was indicated by the step arising on the plot, may represent the existence/occurrence of a different specific type of adsorption mechanism. This binding force starts to operate simultaneously at a critical concentration of solute in the studied soil-pesticide system. The parameters calculated from the equation provide an opportunity to estimate the extent of absorption constant, adsorption capacity, and concentration limit characteristic to the measured stepwise isotherms.

Adsorption↗

Controlled release of the herbicide, fluometuron, from matrix granules based on fractionated organosolv lignins.

An organosolv lignin and several of its fractions were used to prepare controlled release matrix granules with fluometuron using a melt process. Release profiles of fluometuron from these granules and a commercial granular formulation were studied in vitro. The release rates of fluometuron were considerably reduced from all lignin-based granules as compared to the commercial formulation. The release rates markedly varied with the lignin fraction used in the fluometuron-lignin matrix systems with the corresponding times for 50% release (T(50)) values ranging from 2.37 to 11.2 days. The variation in release rate of fluometuron was related to the high proportion of low molecular weight lignin and its associated water soluble lignin in the lignin-based granules, in terms of the hydrophobicity of matrix, the content, and release rate of soluble lignin. The release kinetics were fitted to the generalized model for up to 60% release of fluometuron; the kinetics of fluometuron were of the anomalous type for all matrixes in which release rates increased following a delay.

Chemical Fractionation↗

Degradation of pesticides in biobeds: the effect of concentration and pesticide mixtures.

Biobeds aim to create an environment whereby any pesticide spills are retained and then degraded, thus reducing the potential for surface or groundwater contamination. Biobeds may receive high concentrations of relatively complex mixtures of pesticides. The effects of concentration and pesticide interaction on degradation rate were therefore investigated. At concentrations up to 20 times the maximum recommended application rate for isoproturon and chlorothalonil, the rate of degradation in topsoil and biomix decreased with increasing concentration. With the exception of isoproturon at concentrations above 11 mg kg(-1), degradation was quicker in biomix (a composted mixture of topsoil, compost, and wheat straw) than in topsoil. One possible explanation for faster isoproturon degradation in topsoil as compared to biomix may be that previous treatments of isoproturon applied to the field soil as part of normal agricultural practices had resulted in proliferation of microbial communities specifically adapted to use isoproturon as an energy source. Such microbial adaptation could enhance the performance of a biobed. Studies with a mixture of isoproturon and chlorothalonil showed that interactions between pesticides are possible. In biomix, the degradation of either isoproturon or chlorothalonil was unaffected by the presence of the other pesticide, whereas in topsoil, isoproturon DT(50) values increased from 18.5 to 71.5 days in the presence of chlorothalonil. These studies suggest that biobeds appear capable of treating high concentrations of more than one pesticide.

Biodegradation, Environmental↗

Enzyme-linked immunosorbent assays based on rabbit polyclonal and rat monoclonal antibodies against isoproturon.

This work describes the production and characterization of rabbit polyclonal antisera (pAb) and rat monoclonal antibodies (mAb) against isoproturon. Coating antigen and enzyme-tracer formats were developed. Standard curves for isoproturon were conducted either in 40 mM phosphate buffered saline (PBS) or in Milli-Q water. PAb 352 together with the best enzyme tracer revealed in the optimized ELISA (enzyme tracer format) a test midpoint of 1.06 +/- 0.34 microg/L (n = 19, standard set up in Milli-Q water) with a detection limit of about 0.1 microg/L. The comparable ELISA with mAb IOC 7E1 had test midpoints of 0.07 +/- 0.04 microg/L (n = 7, standards in Milli-Q water) and 0.11 +/- 0.08 microg/L (n = 33; standards in 40 mM PBS). The limits of detection were about 0.003 and 0.01 microg/L in Milli-Q water and PBS, respectively. Noticeable cross reactivities (CRs) were seen with the major metabolites, namely 4-isopropylaniline, 4-isopropylphenylurea, and 1-(4-isopropylphenyl)-3-methylurea. With pAb 352, these CRs were 5%, 7%, and 31%, respectively, and with mAb IOC 7E1, they were 3%, 5%, and ca. 19%, respectively. All arylurea herbicides had only minor CRs, which ranged from no CR (e.g., chlorosulfuron) to a maximum of 3.3% (chlortoluron). Influences of organic solvents (methanol, ethanol, acetonitrile, and acetone) were evaluated. Both pAb- and mAb-based immunoassays showed the highest tolerance for methanol, up to 5%. Ethanol and acetonitrile could not be used above 2% without an influence on the assays. The same was true for acetone, although tested only in the mAb-based assay. Water samples of different origins and matrices were spiked and analyzed with these pAb and mAb ELISAs. The results demonstrated that these immunoassays are useful screening tools.

Animals↗

Effect of different soil textures on leaching potential and degradation of pesticides in biobeds.

Biobeds can be used to intercept pesticide-contaminated runoff from the mixing/washdown area, creating optimum conditions for sorption and biodegradation such that the amount of pesticide reaching adjacent water bodies is significantly reduced. The biobed is built on the farm using locally available materials, which include, straw, compost, and topsoil. The topsoil acts as the inoculum for the system and is likely to vary in terms of its physical, chemical, and microbiological characteristics from one farm to another. This study therefore investigated the effects of using different soil types on the degradation and leaching potential from biobeds. Three contrasting topsoils were investigated. Leaching studies were performed using isoproturon, dimethoate, and mecoprop-P, which were applied at simulated disposal rates to 1.5 m deep biobeds. Annual average concentrations were similar for each soil type with leaching losses of even the most mobile (Koc = 12-25) pesticide <1.64% of the applied dose. Greater than 98% of the retained pesticides were degraded in all matrices. Degradation studies investigated the persistence of individual pesticides and pesticide mixtures in the different matrices. DT50 values for isoproturon, chlorothalonil, mecoprop-P, and metsulfuron-methyl applied at 4 times the maximum approved rate were similar across the biomix types and were all less than or equal to reported DT50 values for soil treated at approved rates. When applied as a mixture, DT50 values in each biomix increased, indicating that interactions between pesticides are possible. However, DT90 values of <167 days were obtained in all circumstances, indicating a negligible risk of accumulation. Studies therefore indicate that substrate will have little impact on biobed performance so it should be possible to use local soils in the construction process.

2-Methyl-4-chlorophenoxyacetic Acid↗