PubMed Health⌕ Search

PubMed · 775257

[Function of surface membrane structures in Thiobacillus thiooxidans].

Abstract

The function of the surface membrane structures was studied with cytochemical techniques on ultrathin sections of Thiobacillus thiooxidans. The transport of elementary sulphur inside the cell involves the surface membrane structures, while oxidation of the sulphur to sulphuric acid takes place on the outer surface of the cytoplasmic membrane. The surface membrane structures are supposed also to participate in the primary dissolution of elementary sulphur at the site of contact of the cells with the mineral.

Explore related subjects

Keep this discovery

Explore connections, maps & timelines

BibTeXRIS

T A Pivovarova, G I Karavaĭko. [Function of surface membrane structures in Thiobacillus thiooxidans].. https://pubmed.ncbi.nlm.nih.gov/775257/

Cite the original work for its findings. Save a collection to share your selection of sources.

KEEP EXPLORING

Related citations

Succession of sulfur-oxidizing bacteria in the microbial community on corroding concrete in sewer systems.

Microbially induced concrete corrosion (MICC) in sewer systems has been a serious problem for a long time. A better understanding of the succession of microbial community members responsible for the production of sulfuric acid is essential for the efficient control of MICC. In this study, the succession of sulfur-oxidizing bacteria (SOB) in the bacterial community on corroding concrete in a sewer system in situ was investigated over 1 year by culture-independent 16S rRNA gene-based molecular techniques. Results revealed that at least six phylotypes of SOB species were involved in the MICC process, and the predominant SOB species shifted in the following order: Thiothrix sp., Thiobacillus plumbophilus, Thiomonas intermedia, Halothiobacillus neapolitanus, Acidiphilium acidophilum, and Acidithiobacillus thiooxidans. A. thiooxidans, a hyperacidophilic SOB, was the most dominant (accounting for 70% of EUB338-mixed probe-hybridized cells) in the heavily corroded concrete after 1 year. This succession of SOB species could be dependent on the pH of the concrete surface as well as on trophic properties (e.g., autotrophic or mixotrophic) and on the ability of the SOB to utilize different sulfur compounds (e.g., H2S, S0, and S2O3(2-)). In addition, diverse heterotrophic bacterial species (e.g., halo-tolerant, neutrophilic, and acidophilic bacteria) were associated with these SOB. The microbial succession of these microorganisms was involved in the colonization of the concrete and the production of sulfuric acid. Furthermore, the vertical distribution of microbial community members revealed that A. thiooxidans was the most dominant throughout the heavily corroded concrete (gypsum) layer and that A. thiooxidans was most abundant at the highest surface (1.5-mm) layer and decreased logarithmically with depth because of oxygen and H2S transport limitations. This suggested that the production of sulfuric acid by A. thiooxidans occurred mainly on the concrete surface and the sulfuric acid produced penetrated through the corroded concrete layer and reacted with the sound concrete below.

Acidithiobacillus thiooxidans↗

Microbially-influenced degradation of solidified/stabilized metal waste.

In the present study, a refined microbially-influenced degradation method was used to evaluate the stability of a solidified synthetic waste containing chromium salt, cement and fly ash in two different proportions. The experimental samples showed evidence of microbial growth by leaching of sulfate. Chromium leached by Thiobacillus thiooxidans from the experimental samples 'C1' (10.26% CrCl3 .6H2O; 89.74% cement) and 'FC1' (10.26% CrCl3 .6H2O; 10% fly ash; 79.74% cement), after 30 days of exposure was 14.53 mg/g and 9.53 mg/g, respectively. The corresponding concentration of chromium in the leachate was 0.189 mg/l and 0.124 mg/l, respectively, which was lower than the toxicity characteristic leaching procedure (TCLP), regulatory limit (5 mg/l). Replacement of cement by 10% fly ash in FC1 restricted the leaching of chromium more effectively. Model equations based on two shrinking core models namely, acid dissolution and bulk diffusion model, were used to analyze the kinetics of microbial degradation. Of the two approaches, the bulk diffusion model fit the data better than the acid dissolution model as indicated by the correlation coefficients of >0.97.

Acidithiobacillus thiooxidans↗

Expression, purification and molecular modelling of the Iro protein from Acidithiobacillus ferrooxidans Fe-1.

The Iro protein was proposed to be involved in the iron respiratory electron transport chain in Acidithiobacillus ferrooxidans, it is a member of HiPIP family with the iron-sulfur cluster for electron transfer. The gene of Iro protein from A. ferrooxidans Fe-1 was cloned and then successfully expressed in Escherichia coli, finally purified by one-step affinity chromatography to homogeneity. The recombinant protein was observed to be dimer. The molecular mass of a monomer containing the [Fe4S4] cluster was 6847.35 Da by MALDI-TOF-MS. The optical and EPR spectra results of the recombinant protein confirmed that the iron-sulfur cluster was correctly inserted into the active site of the protein. Molecular modelling for the protein revealed that Cys20, Cys23, Cys32 and Cys45 were in ligation with the iron-sulfur cluster, and Tyr10 was important for the stability of the [Fe4S4] cluster. As we know, this is the first report of expression in E. coli of the Iro protein from A. ferrooxidans Fe-1.

Acidithiobacillus thiooxidans↗