Characterization of microsomal electron transport components from control, phenobarbital- and 3-methylcholanthrene-treated mice. II. Improved resolution and quantitation of major components in ammonium sulfate fractions from total liver microsomes.

Quantitation of microsomal components in ammonium sulfate fractions using a high-resolution sodium dodecyl sulfate-polyacrylamide gel electrophoresis system, and a comparison of these results with those from similar experiments on total liver microsomes has enabled us to identify and better characterize the interactions between microsomal electron transport components. It was found that: (1) phenobarbital decreased the amount of one protein component of approximately 50 000 molecular weight while increasing a component of very similar molecular weight; (2) only two proteins appeared to be associated with CO binding; (3) another protein of approximately 68 000 molecular weight, one of the glycoproteins found in liver microsomes, appears to be induced by phenobarbital pretreatment; (4) the induction of NADPH-cytochrome c reductase activity after phenobarbital pretreatment is not dependent on an increase in the known NADPH-dependent flavoprotein, but rather on the increase in some component found predominately in our most soluble sub-microsomal fraction. A very good separation of the above components was achieved by ammonium sulfate fractionation, e.g. simply on the basis of their solubility. This and the fact that the more-or-less soluble proteins were induced by phenobarbital or 3-methylcholanthrene respectively indicate that the solubility of membrane proteins plays a major role in the structure and function of microsomal membranes.     

Molecular analysis of 16 Turkish families with DHPR deficiency using denaturing gradient gel electrophoresis (DGGE)

Dihydropteridine reductase (DHPR) catalyses the conversion of quinonoid dihydrobiopterin (qBH2) to tetrahydrobiopterin (BH4), which serves as the obligatory cofactor for the aromatic amino acid hydroxylases. DHPR deficiency, caused by mutations in the QDPR gene, results in hyperphenylalaninemia and deficiency of various neurotransmitters in the central nervous system, with severe neurological symptoms as a consequence. We have studied, at the clinical and molecular levels, 17 patients belonging to 16 Turkish families with DHPR deficiency. The patients were detected at neonatal screening for hyperphenylalaninemia or upon the development of neurological symptoms. To identify the disease causing molecular defects, we developed a sensitive screening method that rapidly scans the entire open reading frame and all splice sites of the QDPR gene. This method combines PCR amplification and "GC-clamping" of each of the seven exonic regions of QDPR, resolution of mutations by denaturing gradient gel electrophoresis (DGGE), and identification of mutations by direct sequence analysis. A total of ten different mutations were identified, of which three are known (G23D, Y150C, R221X) and the remaining are novel (G17R, G18D, W35fs, Q66R, W90X, S97fs and G149R). Six of these mutations are missense variants, two are nonsense mutations, and two are frameshift mutations. All patients had homoallelic genotypes, which allowed the establishment of genotype-phenotype associations. Our findings suggest that DGGE is a fast and efficient method for detection of mutations in the QDPR gene, which may be useful for confirmatory DNA-based diagnosis, genetic counselling and prenatal diagnosis in DHPR deficiency.     

Method for Spiking Soil Samples with Organic Compounds

We examined the harmful side effects on indigenous soil microorganisms of two organic solvents, acetone and dichloromethane, that are normally used for spiking of soil with polycyclic aromatic hydrocarbons for experimental purposes. The solvents were applied in two contamination protocols to either the whole soil sample or 25% of the soil volume, which was subsequently mixed with 75% untreated soil. For dichloromethane, we included a third protocol, which involved application to 80% of the soil volume with or without phenanthrene and introduction of Pseudomonas fluorescens VKI171 SJ132 genetically tagged with luxAB::Tn5. For both solvents, application to the whole sample resulted in severe side effects on both indigenous protozoa and bacteria. Application of dichloromethane to the whole soil volume immediately reduced the number of protozoa to below the detection limit. In one of the soils, the protozoan population was able to recover to the initial level within 2 weeks, in terms of numbers of protozoa; protozoan diversity, however, remained low. In soil spiked with dichloromethane with or without phenanthrene, the introduced P. fluorescens VKI171 SJ132 was able to grow to a density 1,000-fold higher than in control soil, probably due mainly to release of predation from indigenous protozoa. In order to minimize solvent effects on indigenous soil microorganisms when spiking native soil samples with compounds having a low water solubility, we propose a common protocol in which the contaminant dissolved in acetone is added to 25% of the soil sample, followed by evaporation of the solvent and mixing with the remaining 75% of the soil sample.     

Excitation energy transfer kinetics and efficiency in phototrophic green sulfur bacteria

A series of spectroscopic measurements were performed on membrane fractions and detergent-solubilized complexes from the green sulfur bacterium (GSB) Chlorobaculum (Cba.) tepidum. The excitation migration through the entire GSB photosynthetic apparatus cannot be observed upon excitation of membranes in the chlorosome region at 77?K. In order to observe energy transfer from the Fenna-Matthews-Olson (FMO) protein to the reaction center (RC), FMO was directly excited at ~800?nm in transient absorption experiments. However, interpretation of the results is complicated by the spectral overlap between FMO and the RC. The availability of the Y16F FMO mutant, whose absorption spectrum is drastically different from that of the WT, has enabled the selection of spectral regions where either only FMO or the RC contributes. The application of a directed kinetic modeling approach, or target analysis, revealed the various decay and energy transfer pathways within the pigment-protein complexes. The calculated FMO-to-RC excitation energy transfer efficiencies are approximately 25% and 48% for the Y16F and WT samples, respectively.     

Remobilization of toxic heavy metals adsorbed to bacterial wall-clay composites

Significant quantities of Ag(I), Cu(II), and Cr(III) were bound to isolated Bacillus subtilis 168 walls, Escherichia coli K-12 envelopes, kaolinite and smectite clays, and the corresponding organic material-clay aggregates (1:1, wt/wt). These sorbed metals were leached with HNO3, Ca(NO3)2, EDTA, fulvic acid, and lysozyme at several concentrations over 48 h at room temperature. The remobilization of the sorbed metals depended on the physical properties of the organic and clay surfaces and on the character and concentration of the leaching agents. In general, the order of remobilization of metals was Cr much less than Ag less than Cu. Cr was very stable in the wall, clay, and composite systems; pH 3.0, 500 microM EDTA, 120-ppm [mg liter-1] fulvic acid, and 160-ppm Ca remobilized less than 32% (wt/wt) of sorbed Cr. Ag (45 to 87%) and Cu (up to 100%) were readily removed by these agents. Although each leaching agent was effective at mobilizing certain metals, elevated Ca or acidic pH produced the greatest overall mobility. The organic chelators were less effective. Lysozyme digestion of Bacillus walls remobilized Cu from walls and Cu-wall-kaolinite composites, but Ag, Cr, and smectite partially inhibited enzyme activity, and the metals remained insoluble. The extent of metal remobilization was not always dependent on increasing concentrations of leaching agents; for example, Ag mobility decreased with some clays and some composites treated with high fulvic acid, EDTA, and lysozyme concentrations. Sometimes the organic material-clay composites reacted in a manner distinctly different from that of their individual counterparts; e.g., 25% less Cu was remobilized from wall- and envelope-smectite composites than from walls, envelopes, or smectite individually in 500 microM EDTA. Alternatively, treatment with 160-ppm Ca removed 1.5 to 10 times more Ag from envelope-kaolinite composites than from the individual components. The particle size of the deposited metal may account for some of the stability changes; those metals that formed large, compact aggregates (Cr and Ag) as seen by transmission electron microscopy were less likely to be remobilized. In summary, it is apparent that remobilization of toxic heavy metals in sediments, soils, and the vadose zone is a complicated issue. Predictions based on single inorganic or organic component systems are too simplistic.     

Characterization of the dnaA, gyrB and other genes in the dnaA region of the Escherichia coli chromosome on specialized transducing phages lambda tna.

Summary Specialized transducing phages tna (tryptophanase) harboring chromosomal DNA and genetic markers from the dnaA region of the Escherichia coli chromosome were isolated. Transductional analysis showed that some of these tnaA transducing phages carry two genes important in DNA replication, namely the dnaA gene (initiation of chromosome replication) and the gyrB gene (subunit B of DNA gyrase), formerly designated cou ^R. The following clockwise order of genetic markers was found: uhp, gyrB, dnaA, rimA, tnaA, bglB.The gene-protein relationship was established by the determination of the gene products encoded on the chromosomal DNA of the different tna. A 54 kD and a 91 kD polypeptide appear to be coded for by the dnaA and gyrB genes, respectively; the 91 kD protein is encoded on a region in which coumermycin sensitivity maps and is with respect to electrophoretic behavior identical to subunit B of DNA gyrase. The 54 kD protein is encoded on the region in which different independently isolated dnaA(Ts) mutations (dnaA5, dnaA46, dnaA167, dnaA203, dnaA204, dnaA205, dnaA211, dnaA508) are located. Additional genes which code for polypeptides with hitherto unknown functions were identified and mapped. The acriflavin sensitivity mutation acrB1 was found to be an allele of the gyrB gene (see Note Added in Proof).     

Molecular basis for the functional interaction of dynein light chain with the nuclear-pore complex

Nucleocytoplasmic transport occurs through nuclear pore complexes (NPCs) embedded in the nuclear envelope. Here, we discovered an unexpected role for yeast dynein light chain (Dyn2) in the NPC. Dyn2 is a previously undescribed nucleoporin that functions as molecular glue to dimerize and stabilize the Nup82-Nsp1-Nup159 complex, a module of the cytoplasmic pore filaments. Biochemical analyses showed that Dyn2 binds to a linear motif (termed DID(Nup159)) inserted between the Phe-Gly repeat and coiled-coil domain of Nup159. Electron microscopy revealed that the reconstituted Dyn2-DID(Nup159) complex forms a rigid rod-like structure, in which five Dyn2 homodimers align like 'pearls on a string' between two extented DID(Nup159) strands. These findings imply that the rigid 20 nm long Dyn2-DID(Nup159) filament projects the Nup159 Phe-Gly repeats from the Nup82 module. Thus, it is possible that dynein light chain plays a role in organizing natively unfolded Phe-Gly repeats within the NPC scaffold to facilitate nucleocytoplasmic transport.     

Identification of genetic markers for differentiation of Shiga toxin-producing, enteropathogenic, and avirulent strains of Escherichia coli O26

Shiga toxin-producing Escherichia coli (STEC) O26 is one of the top five enterohemorrhagic E. coli (EHEC) O groups most often associated with hemorrhagic colitis and hemolytic uremic syndrome (HUS) worldwide. STEC O26 is considered to have evolved from enteropathogenic (EPEC) O26 strains through the acquisition of Shiga toxin (Stx)-encoding genes. Our PCR data identified several STEC-like strains expressing all features of STEC except Stx production and carrying remnants of Stx phages that were probably derivatives of EHEC O26. EHEC and EPEC O26 strains phenotypically resemble O26 EHEC-like and apathogenic E. coli O26 strains and are therefore undistinguishable by cultural methods. A clear discrimination between the different O26 groups is required for diagnostics in patients and for control of food safety. To develop an assay for specific detection of EHEC and EHEC-like O26 strains, we used a high-throughput PCR approach for selection of discriminative genetic markers among 33 tested genes mostly encoding type III secretion system effector proteins. The genes ECs1822, nleH1-2, nleA, nleC, nleH1-1, nleG, nleG2, nleG6-1, nleG6-2, espJ, espM2, nleG8-2, espG, ent (or espL2), nleB, nleE, efa1, and espB were detected at different frequencies in O26 EHEC, EHEC-like, and EPEC strains, indicating the possible role of these genes in virulence of human pathogenic O26 strains. The espK and espN genes were detected only in EHEC and EHEC-like O26 strains. espK was present in 99.14% of EHEC and 91.14% of EHEC-like O26 strains and was hence the best candidate as a genetic marker for characterizing these pathogroups. These data were corroborated by a genotyping real-time PCR test based on allelic discrimination of the arcA (aerobic respiratory control protein A) gene. The results indicate that a combination of molecular detection tools for O26 wzx (wzx(O26)), eae-beta, stx, espK, and arcA genotyping is highly discriminative for clear identification of EHEC and EHEC-like E. coli O26 strains. This simple diagnostic test might be applicable in hospital service laboratories or public health laboratories to test strains isolated from stools of patients suffering from diarrhea.