Poly(acrylonitrile)chitosan composite membranes for urease immobilization

(Poly)acrylonitrile/chitosan (PANCHI) composite membranes were prepared. The chitosan layer was deposited on the surface as well as on the pore walls of the base membrane. This resulted in the reduction of the pore size of the membrane and in an increase of their hydrophilicity. The pore structure of PAN and PANCHI membranes were determined by TEM and SEM analyses. It was found that the average size of the pore under a selective layer base PAN membrane is 7 microm, while the membrane coated with 0.25% chitosan shows a reduced pore size--small or equal to 5 microm and with 0.35% chitosan--about 4 microm. The amounts of the functional groups, the degree of hydrophilicity and transport characteristics of PAN/Chitosan composite membranes were determined. Urease was covalently immobilized onto all kinds of PAN/chitosan composite membranes using glutaraldehyde. Both the amount of bound protein and relative activity of immobilized urease were measured. The highest activity (94%) was measured for urease bound to PANCHI2 membranes (0.25% chitosan). The basic characteristics (pH(opt), pH(stability), T(opt), T(stability), heat inactivation and storage stability) of immobilized urease were determined. The obtained results show that the poly(acrylonitrile)chitosan composite membranes are suitable for enzyme immobilization.     

Alkalitolerant micromycetes in acidic and neutral soils of the temperate zone

A wide diversity of micromycetes from various taxonomic groups in acidic and neutral soils is known from the literature data. In the present work, the fungi isolated from these soils and capable of growth at high pH are analyzed. The fungi were isolated from acidic sod-podzol and neutral cultivated soils by plating on alkaline agar (pH 10.0–10.5). Their identification was carried out using morphological, cultural, and molecular genetic criteria. Phylogenetic analysis was performed and the rates of linear growth within a broad pH range (4.0–10.4) were determined. The isolates represented a polyphyletic group of ascomycetes (Sordariomycetes), which included members of Plectosphaerellaceae (5 species) and various families of Hypocreales (4 species). The most common species were Gibellulopsis nigrescens, Acrostalagmus luteoalbus, Chordomyces antarcticum, and Plectosphaerella spp. Investigation of fungal growth at different pH values revealed all isolates to be alkalitolerant, with no alkaliphilic fungi isolated from acidic sod-podzol and neutral cultivated soils. Although the group of isolates was polyphyletic and its members originated from different ecological and trophic niches, most alkalitolerant isolates exhibited common morphological traits with acremonium- and verticillium-like conidial spore formation, abundant slime formation, and a tendency for aggregation of their mycelium in bundles. Our research confirmed the presence of fungi with alkalitolerant adaptation to external pH in the sod-podzolic and cultivated soils of the Moscow region.     

Quantitative analysis of N-terminal valine peptide adducts specific for 1,2-epoxy-3-butene

Butadiene (BD) metabolism shows gender, species and concentration dependency, making the extrapolation of animal results to humans complex. BD is metabolized mainly by cytochrome P450 2E1 to three epoxides, 1,2-epoxy-3-butene (EB), 1,2;3,4-diepoxybutane (DEB) and 1,2-epoxy-butanediol (EB-diol). For accurate risk assessment it is important to elucidate species differences in the internal formation of the individual epoxides in order to assign the relative risks associated with their different mutagenic potencies. Analysis of N-terminal globin adducts is a common approach for monitoring the internal formation of BD derived epoxides. Our long term strategy is to develop an LC-MS/MS method for simultaneous detection of all three BD hemoglobin adducts. This approach is modeled after the recently reported immunoaffinity LC-MS/MS method for the cyclic N,N-(2,3-dihydroxy-1,4-butadyil)-valine (pyr-Val, derived from DEB). We report herein the analysis of the EB-derived 2-hydroxyl-3-butenyl-valine peptide (HB-Val). The procedure utilizes trypsin hydrolysis of globin and immunoaffinity (IA) purification of alkylated heptapeptides. Quantitation is based on LC-MS/MS monitoring of the transition from the singly charged molecular ion of HB-Val (1-7) to the a(1) fragment. Human HB-Val (1-11) was synthesized and used for antibody production. As internal standard, the labeled rat-[(13)C(5)(15)N]-Val (1-11) was prepared through direct alkylation of the corresponding peptide with EB. Standards were characterized and quantified by LC-MS/MS and LC-UV. The method was validated with different amounts of human HB-Val standard. The recovery was >75% and coefficient of variation <25%. The LOQ was set to 100 fmol/injection. For a proof of principal experiment, globin samples from male and female rats exposed to 1000 ppm BD for 90 days were analyzed. The amounts of HB-Val present were 268.2+/-56 and 350+/-70 pmol/g (mean+/-S.D.) for males and females, respectively. No HB-Val was detected in controls. These data are much lower compared to previously reported values measured by GC-MS/MS. The difference may be due higher specificity of the LC-MS/MS method to the N-terminal peptide from the alpha-chain versus derivatization of both alpha- and beta-chain by Edman degradation, and possible instability of HB-Val adducts during long term storage (about 10 years) between the analyses. These differences will be resolved by examining recently collected samples, using the same internal standard for parallel analysis by GC-MS/MS and LC-MS/MS. Based on our experience with pyr-Val adduct assay we anticipate that this assay will be suitable for evaluation of HB-Val in multiple species.     

Effect of gamma rays on T. ovis cysticerci

The influence of gamma-radiation (0.2 to 2 kGy) on T. ovis cysticerci has been studied. Irradiation of flesh pieces invaded with T. ovis with doses ranging from 0.2 to 1.2 kGy does not affect the viability of cysticerci; the doses of 1.4 to 1.8 kGy have a minor effect, and the dose of 2 kGy produces a 100-per cent effect on the viability and invasive capacity of cysticerci. This effect of radiation is not influenced by the volume of the muscular flesh mass exposed, age and localization of cysticerci. With lower doses, the radiation effect is manifested 15-20 days following irradiation.