'Clay hutches': a novel interaction between bacteria and clay minerals.

Biofilm formation on a low-energy substratum floating on the surface of a water column overlying a polychlorinated biphenyl (PCB)-contaminated sandy clay soil was followed by light and electron microscopy. The biofilms that developed consisted of a dense lawn of clay aggregates, each one of which contained one or more bacteria, phyllosilicates and grains of iron oxide material, all held together by bacterial extracellular polysaccharides (EPS). The clay leaflets were arranged in the form of 'houses of cards' and gave the aggregates the appearance of 'hutches' housing the bacteria. Interestingly, although the soil is poor in carbon, and the weakly bioavailable PCBs constitute the principal source of carbon in this system, the bacteria contained electron-transparent structures presumed to be carbon storage granules. These, and the EPS material present in the hutches, indicate that carbon is not limiting in this system and, as PCBs have been found associated with the clay mineral fraction of the floating substratum, the clay particles may serve as carbon shuttles. The interesting possibilities that the 'clay hutches' may represent a 'soil microhabitat', a 'minimal nutritional sphere' and an 'effective survival unit' for autochthonous bacteria are noted. The formation of clay hutches by bacteria would seem to merit further investigation, particularly regarding their roles in bacterial processes in soil and in geological processes.

Thermal gradient gel electrophoresis analysis of bioprotection from pollutant shocks in the activated sludge microbial community.

We used a culture-independent approach, namely, thermal gradient gel electrophoresis (TGGE) analysis of ribosomal sequences amplified directly from community DNA, to determine changes in the structure of the microbial community following phenol shocks in the highly complex activated sludge ecosystem. Parallel experimental model sewage plants were given shock loads of chlorinated and methylated phenols and simultaneously were inoculated (i) with a genetically engineered microorganism (GEM) able to degrade the added substituted phenols or (ii) with the nonengineered parental strain. The sludge community DNA was extracted, and 16S rDNA was amplified and analyzed by TGGE. To allow quantitative analysis of TGGE banding patterns, they were normalized to an external standard. The samples were then compared with each other for similarity by using the coefficient of Dice. The Shannon index of diversity, H, was calculated for each sludge sample, which made it possible to determine changes in community diversity. We observed a breakdown in community structure following shock loads of phenols by a decrease in the Shannon index of diversity from 1.13 to 0.22 in the noninoculated system. Inoculation with the GEM (Pseudomonas sp. strain B13 SN45RE) effectively protected the microbial community, as indicated by the maintenance of a high diversity throughout the shock load experiment (H decreased from 1.03 to only 0.82). Inoculation with the nonengineered parental strain, Pseudomonas sp. strain B13, did not protect the microbial community from being severely disturbed; H decreased from 1.22 to 0.46 for a 3-chlorophenol-4-methylphenol shock and from 1.03 to 0.70 for a 4-chlorophenol-4-methylphenol shock. The catabolic trait present in the GEM allowed for bioprotection of the activated sludge community from breakdown caused by toxic shock loading. In-depth TGGE analysis with similarity and diversity algorithms proved to be a very sensitive tool to monitor changes in the structure of the activated sludge microbial community, ranging from subtle shifts during adaptation to laboratory conditions to complete collapse following pollutant shocks.

Characterization of a gene cluster from Ralstonia eutropha JMP134 encoding metabolism of 4-methylmuconolactone.

A 2,585 bp chromosomal DNA segment of Ralstonia eutropha JMP134 (formerly: Alcaligenes eutrophus JMP134) which contains a gene cluster encoding part of the modified ortho-cleavage pathway encodes a putative transport protein for 4-methylmuconolactone, a novel 4-methylmuconolactone methylisomerase and methylmuconolactone isomerase. The putative 4-methylmuconolactone transporter, a protein with a calculated molecular mass of 45.8 kDa, exhibits sequence homology to other members of the major superfamily of transmembrane facilitators and shows the common structural motif of 12 transmembrane-spanning alpha-helical segments and the hallmark amino acid motif characteristic of the superfamily. Consistent with the novelty of the reaction catalyzed by 4-methylmuconolactone methylisomerase, no primary sequence homologies were found between this enzyme or its gene and other proteins or genes in the data banks, suggesting that this enzyme represents a new type of isomerase. The molecular mass of the native 4-methylmuconolactone methylisomerase was determined by gel filtration analysis to be 25 +/- 2 kDa. From the polynucleotide sequence of the gene, a molecular mass of 12.9 kDa was calculated and hence we predict a homodimeric quaternary structure. The high sensitivity of 4-methylmuconolactone methylisomerase to heavy metals and thiol-modifying reagents implicates the involvement of sulfhydryl groups in the catalytic reaction. The methylmuconolactone isomerase - calculated molecular mass 10.3 kDa - has a primary structure related to the classical muconolactone isomerases (EC 5.3.3.4) of Acinetobacter calcoaceticus, of two Pseudomonas putida strains and of Ralstonia eutropha JMP134, suggesting that these are all isoenzymes. Consistent with this proposal is the finding that the purified protein exhibits muconolactone-isomerizing activity.

Plasmid stability of recombinant Pseudomonas sp. B13 FR1 pFRC20P in continuous culture.

Plasmid stability of recombinant Pseudomonas sp. B13 FR1 pFRC20P, a strain capable of mineralizing 3- and 4-chlorobenzoate and 4-methylbenzoate, was investigated in continuous culture. The hybrid cosmid pFRC20P enables the strain to mineralize 4-methylbenzoate. Rapid plasmid loss was observed under nonselective conditions using 3-chlorobenzoate as the substrate. Plasmid stability decreased with increasing dilution rate. Despite the growth advantage of the generated plasmid free cells a total depletion of plasmid bearing cells was not observed. After approximately 50 generations the fraction of plasmid bearing cells reached a constant level of 10%, which was stably maintained during the next 25 generations. Cells from this stage were used to inoculate a new culture that resulted in a stable level of 50% plasmid bearing cells. By a temporary substrate change to selective conditions (4-methylbenzoate), this level could be further increased to 70%. Literature models on plasmid stability could not be applied to describe the experimental data. Therefore, a new but unstructured model was developed to describe the experimental results. The model is based on the existence of three subpopulations: a plasmid free one, an original plasmid bearing one with a growth disadvantage compared to plasmid free cells, and a second plasmid bearing subpopulation with increased stability that is generated from the original one and has a growth rate comparable to the plasmid free cells.

Bioprotection of microbial communities from toxic phenol mixtures by a genetically designed pseudomonad.

Pseudomonas sp. B13 SN45RE is a genetically engineered microorganism (GEM) that is able to simultaneously degrade mixtures of chloro- and methylaromatics ordinarily toxic for microbial communities via a designed novel ortho-cleavage pathway. The utility of the GEM was investigated in a laboratory scale sewage plant fed with mixtures of either 4-chlorophenol and 4-methyphenol or 3-chlorophenol and 4-methylphenol. In the model system the GEM significantly increased the rate and extent of degradation of the phenol mixtures. In the absence of the GEM, shock loads of the phenol mixtures (1 mM of each compound) reduced the numbers of culturable bacteria by three orders of magnitude, completely eliminated protozoa and metazoa, and caused a drastic decrease in oxygen consumption, whereas the presence of the GEM protected the indigenous microbial community and assured continued functioning of the sewage plant.

Detection of polychlorinated biphenyl degradation genes in polluted sediments by direct DNA extraction and polymerase chain reaction.

It was the aim of this study to specifically detect the DNA sequences for the bphC gene, the meta-cleavage enzyme of the aerobic catabolic pathway for biphenyl and polychlorinated biphenyl degradation, in aquatic sediments without prior cultivation of microorganisms by using extraction of total DNA, PCR amplification of bphC sequences, and detection with specific gene probes. The direct DNA extraction protocol used was modified to enhance lysis efficiency. Crude extracts of DNA were further purified by gel filtration, which yielded DNA that could be used for the PCR. PCR primers were designed for conserved regions of the bphC gene from a sequence alignment of five known sequences. The specificity of PCR amplification was verified by using digoxigenin-labeled DNA probes which were located internal to the amplified gene sequence. The detection limit for the bphC gene of Pseudomonas paucimobilis Q1 and Pseudomonas sp. strain LB400 was 100 cells per g (wet weight) or approximately five copies of the target sequence per PCR reaction mixture. In total-DNA extracts of aerobic top layers of sediment samples obtained from three different sampling sites along the Elbe River, which has a long history of anthropogenic pollution, Pseudomonas sp. strain LB 400-like sequences for the bphC gene were detected, but P. paucimobilis Q1 sequences were not detected. No bphC sequences were detected in an unpolluted lake sediment. A restriction analysis did not reveal any heterogeneity in the PCR product, and the possibility that sequences highly related to the bphC gene (namely, nahC and todE) were present was excluded.(ABSTRACT TRUNCATED AT 250 WORDS)