Tapio Kotiaho

Electrospray mass and tandem mass spectrometry identification of ozone oxidation products of amino acids and small peptides

Aqueous ozonation of the 22 most common amino acids and some small peptides were studied by electrospray mass (ESI-MS) and tandem mass spectrometry. After 5 min of ozonation only His, Met, Trp, and Tyr form oxidation products clearly detectable by ESI-MS. For His, the main oxidation product is formed by the addition of three oxygen atoms, His + 3O; for Met and Tyr by the addition of one oxygen atom, Met + O and Tyr + O, and for Trp by the addition of two oxygen atoms, Trp + 2O. Ozone oxidation occurs rapidly, products are already detected after 30 s of ozonation, and the reactivity order is Met > Trp > Tyr > His. The structures of the oxygen addition products were investigated by electrospray product ion mass spectra, and by comparing these spectra to those of protonated intact amino acids, and when available, to those of model compounds. His + 3O was assigned as 2-amino-4-oxo-4-(3-formylureido)butanoic acid (1) formed by oxidation of the His imidazole ring, Met + O as methionine sulfoxide (2), Trp + 2O as N-formylkynurenine (4), and Tyr + O as a mixture of dihydroxyphenylalanines (7 and 8). Ozonation of peptides show that the same number of oxygen atoms are added as expected from the ozonation of the free amino acids. The product ion mass spectra of both the protonated intact peptides, MH+, and the main ozonation products (M + nO)H+ (n = 1–3) revealed b and y type ions as the main fragments, which allow one to assign the type and location of modified amino acid in the model peptides.

Comparison of different methods for the determination of volatile organic compounds in water samples.

The aim of this work was to compare the characteristics of three methods, membrane inlet mass spectrometry (MIMS), purge-and-trap gas chromatography-mass spectrometry (P&T) and static headspace gas chromatography (HSGC), for the determination of volatile organic compounds in water samples as used in routine analysis. The characteristics examined included linear dynamic ranges, detection limits of selected environmentally hazardous volatile organic compounds (e.g. toluene, benzene and trichloroethene) in water, required analysis time and reproducibility of the analytical methods. The MIMS and P&T methods had the lowest detection limits for all the tested compounds, ranging from 0.1 to 5 mug 1(-1). Linear dynamic ranges using the MIMS method were about four orders of magnitude and using the P&T method about two orders of magnitude. Detection limits of the HSGC method were 10-100 times higher than those of the other two methods, but the linear dynamic ranges were larger, even up to six orders of magnitude. The analysis time per sample was shortest for the MIMS method, from 5 to 10 min, and ranged around from 35 to 45 min for the HSGC and P&T methods. The reproducibilities of the methods were of the same order of magnitude, in the range of 1-13%. Agreement between the analytical results obtained for spiked samples and for environmental water samples by the three different methods was very good.

Development of a membrane inlet mass spectrometric method for analysis of air samples

A sheet membrane inlet mass spectrometric (MIMS) method for the on-line analysis of volatile organic compounds (VOCs) in air at low μg/m3 levels was developed. The effects of the thickness of the membrane, the temperature of the membrane inlet and the flow rate of the sample on the responses and response times of some selected VOCs were studied in detail. Under optimised conditions the detection limits for the VOCs studied were 0.5–4 g m−3 and linear dynamic ranges were about four orders of magnitude. Response times of only a few seconds were recorded with a thin (25 μm) membrane. The developed MIMS method was applied to an analysis of air samples from an exhaust of a paintshop, where volatile organic solvents were used.

Determination of phenolic compounds in water using membrane inlet mass spectrometry.

Two membrane inlet mass spectrometric (MIMS) methods for determining phenolic compounds in water are described and compared, namely direct analysis and analysis after acetylation of the phenolic compounds. Direct analysis of phenolic compounds in water is a very simple and rapid method and detection limits are relatively low (from 30 mug 1(-1) for phenol to 1000 mug 1(-1) for 4-nitrophenol). Analysis of phenolic compounds after aqueous acetylation is also a very simple and rapid method, and the detection limits are even two orders of magnitude lower than in the direct analysis. For example the detection limit of phenol acetate is 0.5 mug 1(-1) and that of 4-nitrophenol is 10 mug 1(-1). The acetylation method was also tested in the analysis of phenolic compounds from contaminated surface water samples.

Gas-phase Chemistry of Acylium Ions. Seven-to-Five Ring Contraction of 1,3-Dioxepane and 1,3-Dioxep-5-ene

As shown by pentaquadrupole triple-stage mass spectrometric and 18O-labeling experiments, two seven-membered cyclic acetals, 1,3-dioxepane and 1,3-dioxep-5-ene, fail to react by transacetalization with the gaseous acylium ions CH3C+O and (CH3)2NC+O. Instead, a novel and less exothermic but more kinetically favored reaction, seven-to-five ring contraction, occurs predominantly, and to great extents with the most reactive acylium ion, (CH3)2NC+O. 1,3-Dioxepane yields O-acylated tetrahydrofurans; 1,3-dioxep-5-ene yields O-acylated 2,5-dihydrofurans. Copyright

Determination of mono- and sesquiterpenes in water samples by membrane inlet mass spectrometry and static headspace gas chromatography

A membrane inlet mass spectrometric (MIMS) method is presented and compared with a static headspace gas chromatographic method (HSGC) for the determination of terpenes in water. The MIMS method provides a very simple and fast analysis of terpenes in water, detection limits being relatively low, from 0.2 mug l(-1) for monoterpenes to 2 mug l(-1) for geraniol. The analysis of terpenes by the HSGC (equipped with flame ionization detector, FID) method is more time-consuming and the detection limits (2 mug l(-1) for monoterpenes to 100 mug l(-1) for geraniol) are higher than with MIMS. However, the HSGC method has the advantage of determining individual mono- and sesquiterpene compounds, whereas MIMS provides only separation of different classes of terpenes. Both methods were applied to the analysis of mono- and sesquiterpenes in several condensation water samples of pulp and paper mills.

Analysis of residual solvents in pharmaceuticals with purge-and-membrane mass spectrometry

A method using purge-and-membrane mass spectrometry (PAM-MS) was developed for the analysis of residual solvents in pharmaceutical products. The method combines dynamic headspace and membrane inlet mass spectrometry. The limits of detection for the compounds studied, benzene, toluene, chloroform, 2-pentene and 2-methyl- and 3-methylpentane, were 0.05-0.1 mg/kg. In quantitative analysis the method showed good linearity (r(2) > 0.998) and acceptable within-day (RSD = 7.9-18%) and between-day (RSD = 6.8-10%) repeatability. The PAM-MS method combined with the custom-made Solver program was compared with a method using purge-and-trap gas chromatography/mass spectrometry (P&T-GC/MS) for identification of residual solvents from authentic samples. The results showed that PAM-MS/Solver provides reliable identification of the main volatile organic compounds (VOCs) in the pharmaceuticals, but VOCs with low concentrations (below 0.5 mg/kg) were better identified by P&T-GC/MS. Other advantages of the PAM-MS method were short analysis times and non-requirement for pre-treatment of samples.