Strong paramagnetism of gold nanoparticles deposited on a Sulfolobus acidocaldarius S layer.

Magnetic properties of Au nanoparticles deposited on an archaeal S layer are reported. X-ray magnetic circular dichroism and superconducting quantum interference device magnetometries demonstrate that the particles are strongly paramagnetic, without any indication of magnetic blocking down to 16 mK. The average magnetic moment per particle is M(part)=2.36(7) µ(B). This contribution originates at the particle's Au 5d band, in which an increased number of holes with respect to the bulk value is observed. The magnetic moment per Au atom is 25 times larger than any measured in other Au nanoparticles or any other configurations up to date.

Biogeochemical changes induced in uranium mining waste pile samples by uranyl nitrate treatments under anaerobic conditions.

Response of the subsurface soil bacterial community of a uranium mining waste pile to treatments with uranyl nitrate over different periods of time was studied under anaerobic conditions. The fate of the added U(VI) without supplementation with electron donors was investigated as well. By using 16S rRNA gene retrieval, we demonstrated that incubation with uranyl nitrate for 4 weeks resulted in a strong reduction in and even disappearance of some of the most predominant bacterial groups of the original sample. Instead, a strong proliferation of denitrifying and uranium-resistant populations of Rahnella spp. from Gammaproteobacteria and of Firmicutes occurred. After longer incubations for 14 weeks with uranyl nitrate, bacterial diversity increased and populations intrinsic to the untreated samples such as Bacteroidetes and Deltaproteobacteria propagated and replaced the above-mentioned uranium-resistant groups. This indicated that U(VI) was immobilized. Mössbauer spectroscopic analysis revealed an increased Fe(III) reduction by increasing the incubation time from four to 14 weeks. This result signified that Fe(III) was used as an electron acceptor by the bacterial community established at the later stages of the treatment. X-ray absorption spectroscopic analysis demonstrated that no detectable amounts of U(VI) were reduced to U(IV) in the time frames of the performed experiments. The reason for this observation is possibly due to the low level of electron donors in the studied oligotrophic environment. Time-resolved laser-induced fluorescence spectroscopic analysis demonstrated that most of the added U(VI) was bound by organic or inorganic phosphate phases both of biotic origin.

Manufacturing and characterization of Pd nanoparticles formed on immobilized bacterial cells.

AIMS: To fabricate and analyse Pd nanoparticles on immobilized bacterial cells. METHODS AND RESULTS: Biological ceramic composites (biocers) were used as a template to produce Pd(0) nanoparticles. The metal-binding cells of the uranium mining waste pile isolate, Bacillus sphaericus JG-A12 were used as a biological component of the biocers and immobilized by using sol-gel technology. Vegetative cells and surface-layer proteins of this strain are known to bind high amounts of Pd(II) that can be reduced to Pd(0) particles by the addition of a reducing agent. Sorption of Pd(II) by the biocers from a metal complex solution was studied by inductively coupled plasma mass spectroscopy analyses. After embedding into sol-gel ceramics, the cells retained their Pd(II)-binding capability. Pd(0) nanoclusters were produced by the addition of hydrogen as reducing agent after the sorption of Pd(II). The interactions of Pd(0) with the biocers and the formed Pd(0) nanoparticles were investigated by extended X-ray absorption fine structure spectroscopy. The particles had a size of 0.6-0.8 nm. CONCLUSIONS: Bacterial cells that were immobilized by embedding into sol-gel ceramics were used as a template to produce Pd nanoclusters of a size smaller than 1 nm. These particles possess interesting physical and chemical properties. SIGNIFICANCE AND IMPACT OF THE STUDY: The use of embedded bacterial cells as template enabled the fabrication of immobilized Pd(0) nanoparticles. These particles are highly interesting for technical applications, such as the development of novel catalysts.

Metal binding by bacteria from uranium mining waste piles and its technological applications.

Uranium mining waste piles, heavily polluted with radionuclides and other toxic metals, are a reservoir for bacteria that have evolved special strategies to survive in these extreme environments. Understanding the mechanisms of bacterial adaptation may enable the development of novel bioremediation strategies and other technological applications. Cell isolates of Bacillus sphaericus JG-A12 from a uranium mining waste pile in Germany are able to accumulate high amounts of toxic metals such as U, Cu, Pb, Al, and Cd as well as precious metals. Some of these metals, i.e. U, Cu, Pd(II), Pt(II) and Au(III), are also bound by the highly orderd paracrystalline proteinaceous surface layer (S-layer) that envelopes the cells of this strain. These special capabilities of the cells and the S-layer proteins of B. sphaericus JG-A12 are highly interesting for the clean-up of uranium contaminated waste waters, for the recovery of precious metals from electronic wastes, and for the production of metal nanoclusters. The fabricated nanoparticles are promising for the development of novel catalysts. This work reviews the molecular biology of the S-layer of the strain JG-A12 and the S-layer dependent interactions of the bacterial cells with metals. It presents future perspectives for their application in bioremediation and nanotechnology.

Time-resolved laser fluorescence spectroscopy study on the interaction of curium(III) with Desulfovibrio äspöensis DSM 10631T.

The influence of microorganisms on migration processes of actinides has to be taken into account for the risk assessment of potential high-level nuclear waste disposal sites. Therefore it is necessary to characterize the actinide-bacteria species formed and to elucidate the reaction mechanisms involved. This work is focused on the sulfate-reducing bacterial (SRB) strain Desulfovibrio äspöensis (D. äspöensis) DSM 10631T which frequently occurs in the deep granitic rock aquifers at the Aspö Hard Rock Laboratory (Aspö HRL), Sweden. We chose Cm(III) due to its high fluorescence spectroscopic sensitivity as a model system for exploring the interactions of trivalent actinides with D. äspöensis in the trace concentration range of 3 x 10(-7) mol/L. A time-resolved laser fluorescence spectroscopy (TRLFS) study has been carried out in the pH range from 3.00 to 7.55 in 0.154 mol/L NaCl. We interpret the pH dependence of the emission spectra with a biosorption forming an inner-sphere surface complex of Cm(III) onto the D. äspöensis cell envelope. This Cm(III)-D. äspöensis-surface complex is characterized by its emission spectrum (peak maximum at 600.1 nm) and its fluorescence lifetime (162 +/- 5 micros). No evidence was found for incorporation of Cm(III) into the bacterial cells under the chosen experimental conditions.

Molecular and atomic analysis of uranium complexes formed by three eco-types of Acidithiobacillus ferrooxidans.

A combination of EXAFS, transmission electron microscopy and energy-dispersive X-ray was used to conduct a molecular and atomic analysis of the uranium complexes formed by Acidithiobacillus ferrooxidans. The results demonstrate that this bacterium accumulates uranium as phosphate compounds. We suggest that at toxic levels when the uranium enters the bacterial cells, A. ferrooxidans can detoxify and efflux this metal by a process in which its polyphosphate bodies are involved.

Interactions of three eco-types of Acidithiobacillus ferrooxidans with U(VI).

The interaction of uranium with cells of three recently described eco-types of Acidithiobacillus ferrooxidans recovered from uranium mining wastes was studied. The uranium sorption studies demonstrated that the strains from these types possess different capabilities to accumulate and tolerate uranium. The amount of uranium biosorbed by all A. ferrooxidans strains increased with considerable concentrations. We have found that the representatives of type II accumulate significantly higher amounts of uranium in comparison to the other A. ferrooxidans strains. The investigations of the tolerance to uranium showed that the types I and III are resistant to 8 and 9 mM of uranium respectively, whereas the type II does not tolerate more than 2 mM of uranium. The recovery of the accumulated uranium by desorption was investigated using various desorbing agents as sodium carbonate, sodium citrate and EDTA at different concentrations. Sodium carbonate was the most efficient desorbing agent, removing 97% of the uranium sorbed from the cells of A. ferrooxidans type III, and 88.33 and 88.50% from the cells of the types I and II, respectively.

Bacterial diversity in soil samples from two uranium waste piles as determined by rep-APD, RISA and 16S rDNA retrieval.

The bacterial diversity in two uranium waste piles was studied. Total DNA was recovered from a large number of soil samples collected from different sites and depths in the piles using two procedures for direct lysis. Significant differences in the bacterial composition of the samples were revealed by the use of rep-APD, RISA and 16S ARDREA. The 16S rDNA analyses showed that the uranium wastes were dominated by Acidithiobacillusferrooxidans and by several Pseudomonas species classified in the gamma-subdivision of the Proteobacteria. The three kinds of A. ferrooxidans 16S and IGS rDNA specific fragments that were found corresponded to the three phylogenetic groups recognised in this species. This microdiversity probably reflects the genetic adaptation of the uranium waste strains to different concentrations of heavy metals.

Sequences around the fragmentation sites of the large subunit ribosomal RNA in the family Rhizobiaceae. 23S-like rRNAs in Rhizobiaceae.

We demonstrated that the representatives of the family Rhizobiaceae possess, instead of one single 23S rRNA molecule, three different sets of 23S-like rRNA fragments with sizes of about: 135 b and 2.6 kb (set 1); 135 b, 400 b, and 2.2 kb (set 2); 135 b and two molecules of about 1.3 kb (set 3). In two of the fragmentations, intervening sequences--IVS I and IVS II--are involved. The IVS I is connected to a cleavage of the 23S rRNA primary transcript into two modules (135 b and 2.6 kb large). The IVS II is located at position 543 of the gene, and it leads to an additional processing of the 2.6 kb rRNA species into two molecules with sizes of about 400 b and 2.2 kb. In contrast to the IVS I, which is a common feature of all rhizobia, the IVS II is present in a limited number of strains only. The primary and secondary structures of the regions of the unmatured 23S rRNA transcript possessing IVS I (helix 9) and IVS II (helix 25) were analysed. On the basis of our analyses we propose secondary structure models of the parts of the matured 23S rRNA-like molecules of rhizobia corresponding to the helices 9 and 25. The third fragmentation of the rhizobial 23S rRNA represents a break in the central part of the 2.6 kb-large rRNA and it leads to an occurrence of two fragments with approximately equal size of about 1.3 kb. We have demonstrated that the central fragmentation is not connected to the presence of IVSs but probably to a minor change in the nucleotide sequence in the central part of the 2.6 rRNA.

Alteration of the symbiotic properties of Rhizobium meliloti by plasmid manipulations.

Mutants with symbiotic activity were obtained by random Tn5-Mob mutagenesis of Rhizobium meliloti 41. The place of the Tn5 insertion was localized on a cryptic middle-sized plasmid pRme41a. Mobilization of the labelled plasmid pRme41a::Tn5-Mob into R. meliloti 114, which did not contain such a plasmid led to a complete loss of the nodulation ability of the recipient strain. The Nod-phenotype was a result of a large deletion in the symbiotic (pSym) plasmid of R. meliloti 114.

Characterization of Rhizobium 'hedysari' by RFLP analysis of PCR amplified rDNA and by genomic PCR fingerprinting.

The taxonomic and discriminatory power of RFLP analysis of PCR amplified parts of rhizobial rrn operons was compared to those of genomic PCR fingerprinting with arbitrary and repetitive primers. For this purpose, the two methods were applied for characterization of a group of bacterial isolates referred to as Rhizobium 'hedysari'. As outgroups, representatives of the family Rhizobiaceae, belonging to the Rhizobium galegae, Rhizobium meliloti, Rhizobium leguminosarum and Agrobacterium tumefaciens species were used. By the RFLP analysis of the PCR products corresponding to the variable 5'-half of the 23S rRNA gene and of the amplified spacer region between the 16S and 23S rRNA genes all Rh. 'hedysari' strains studied were tightly clustered together while the outgroups were placed in an outer position. The PCR products of the 3' end parts of the 23S rDNA did not show significant RFL polymorphism and no species differentiation on their basis was possible. In parallel, analysis of the same strains was performed by PCR amplification of their DNA with 19, 18 and 10 bp long arbitrary primers (AP-PCR) as well as with single primers corresponding to several bacterial repetitive sequences (rep-PCR). By both AP and rep-PCR an identification of every particular strain was achieved. In general, all primers provided taxonomic results that are in agreement with the species and group assignments based on the RFLP analysis of the rrn operons. On the basis of the results presented here it can be concluded that AP and rep-PCR are more informative and discriminative than rDNA and RFLP analysis of the rhizobial strains studied.

Fragmentations of the large-subunit rRNA in the family Rhizobiaceae.

A 130-nucleotide-long rRNA species corresponding to the 5' end of the 23S rRNA gene was found in 96 strains belonging to different Rhizobium, Bradyrhizobium, and Agrobacterium species. Additional fragmentation in the central region of the large-subunit rRNA occurred in all agrobacteria, except Agrobacterium vitis, and in most Rhizobium leguminosarum and Rhizobium etli strains but did not occur in any of the other rhizobia and bradyrhizobia studied.

Variability of the 5'-end of the large subunit rDNA and presence of a new short class of rRNA in Rhizobiaceae.

A highly variable region of DNA was found between positions 115 and 388 (Escherichia coli numeration) of the large subunit (ls) rRNA genes of 55 rhizobial and agrobacterial strains. In each case this heterogeneity was accompanied by the presence of a new rRNA species approximately 130 bp long. This novel rRNA species corresponded to the 5'-end of the ls rRNA genes. An additional rRNA processing site was located in the central region of the remaining ls rRNA of many of the Rhizobium leguminosarum and Rh. etli strains, and in all of the agrobacteria studied, excepting the type strain of Agrobacterium vitis NCPPB 3554 and Agrobacterium sp. strain ChAg4.

Strain-specific fingerprints of Rhizobium galegae generated by PCR with arbitrary and repetitive primers.

Strain-specific genomic patterns of Rhizobium galegae were generated by PCR using both arbitrary and repetitive (BOX, ERIC and REP) primers. The identification of the strains was achieved also by RFLP analysis. However, the PCR genomic fingerprinting has significant advantages: it is not only simpler and faster, but it is also much more discriminative because it deals with the full bacterial genome and not only with parts of it as is the case with RFLP. In addition, both kinds of PCR fingerprinting (using arbitrary or repetitive primers) generated highly specific and reproducible patterns when parallel reactions with total bacterial DNA, extracted from independent liquid cultures were performed. The latter shows that AP- and rep-PCR are convenient for controlling the production and application of Rhizobium inoculants.