Bacteria associated with yellow lupine grown on a metal-contaminated soil: in vitro screening and in vivo evaluation for their potential to enhance Cd phytoextraction.

In order to stimulate selection for plant-associated bacteria with the potential to improve Cd phytoextraction, yellow lupine plants were grown on a metal-contaminated field soil. It was hypothesised that growing these plants on this contaminated soil, which is a source of bacteria possessing different traits to cope with Cd, could enhance colonisation of lupine with potential plant-associated bacteria that could then be inoculated in Cd-exposed plants to reduce Cd phytotoxicity and enhance Cd uptake. All cultivable bacteria from rhizosphere, root and stem were isolated and genotypically and phenotypically characterised. Many of the rhizobacteria and root endophytes produce siderophores, organic acids, indole-3-acetic acid (IAA) and aminocyclopropane-1-carboxylate (ACC) deaminase, as well as being resistant to Cd and Zn. Most of the stem endophytes could produce organic acids (73.8%) and IAA (74.3%), however, only a minor fraction (up to 0.7%) were Cd or Zn resistant or could produce siderophores or ACC deaminase. A siderophore- and ACC deaminase-producing, highly Cd-resistant Rhizobium sp. from the rhizosphere, a siderophore-, organic acid-, IAA- and ACC deaminase-producing highly Cd-resistant Pseudomonas sp. colonising the roots, a highly Cd- and Zn-resistant organic acid and IAA-producing Clavibacter sp. present in the stem, and a consortium composed of these three strains were inoculated into non-exposed and Cd-exposed yellow lupine plants. Although all selected strains possessed promising in vitro characteristics to improve Cd phytoextraction, inoculation of none of the strains (i) reduced Cd phytotoxicity nor (ii) strongly affected plant Cd uptake. This work highlights that in vitro characterisation of bacteria is not sufficient to predict the in vivo behaviour of bacteria in interaction with their host plants.

Factors influencing the composition of bacterial communities found at abandoned copper-tailings dumps.

AIMS: To study the effect that copper residues exert on bacterial communities and the ability of bacteria to colonize different microhabitats in abandoned tailing dumps. METHODS AND RESULTS: We used the terminal-restriction fragment length polymorphism technique, a culture-independent molecular approach based on PCR amplification of ribosomal genes, to compare the structure of the bacterial communities from samples taken at two nearby located abandoned tailing dumps found in the Mediterranean-climate area of central Chile. Our results show that elevated available copper content in tailings has a strong effect on the bacterial community composition, but that other factors like pH and organic matter content also play an important role in the structure of these communities. We also found that the number of abundant bacteria in these samples was significantly lower than in soils not exposed to metal pollution. CONCLUSIONS: In addition to bioavailable copper, bacterial communities found in copper-tailings dumps are also affected by several other environmental factors. SIGNIFICANCE AND IMPACT OF THE STUDY: This first report on environmental factors influencing microbial communities in copper-tailings dumps will help to devise appropriate restoration procedures in this type of polluted habitat.

Isolation, characterization, and identification of bacteria associated with the zinc hyperaccumulator Thlaspi caerulescens subsp. calaminaria.

We investigated bacterial populations associated with the Zn hyperaccumulator Thlaspi caerulescens subsp. calaminaria grown in a soil collected from an abandoned Zn-Pb mine and smelter in Plombières, Belgium. The bacterial population of the nonrhizospheric soil consisted of typical soil bacteria, some exhibiting multiple heavy-metal resistance characteristics that often are associated with polluted substrates: 7.8% and 4% of the population survived in the presence of elevated levels of Zn (1 mM) and Cd (0.8 mM), respectively. For the bacterial population isolated from the rhizosphere, the comparable survival rates were 88 and 78%. This observation indicates a selective enrichment of the metal-resistant strains due to an increased availability of the metals in soils near the roots compared with nonrhizospheric soil. The endophytic inhabitants of the roots and shoots were isolated, identified, and characterized. Although similar endophytic species were isolated from both compartments, those from the rhizoplane and roots showed lower resistance to Zn and Cd than the endophytic bacteria isolated from the shoots. In addition, root endophytic bacteria had additional requirements. Contrary to the rootresiding inhabitants, the shoot represented a niche rich in metal-resistant bacteria and even seemed to contain species that were exclusively abundant there. These differences in the characteristics of the bacterial microflora associated with T. caerulescens might possibly reflect altered metal speciation in the different soils and plant compartments studied.

Cloning and functional analysis of the pbr lead resistance determinant of Ralstonia metallidurans CH34.

The lead resistance operon, pbr, of Ralstonia metallidurans (formerly Alcaligenes eutrophus) strain CH34 is unique, as it combines functions involved in uptake, efflux, and accumulation of Pb(II). The pbr lead resistance locus contains the following structural resistance genes: (i) pbrT, which encodes a Pb(II) uptake protein; (ii) pbrA, which encodes a P-type Pb(II) efflux ATPase; (iii) pbrB, which encodes a predicted integral membrane protein of unknown function; and (iv) pbrC, which encodes a predicted prolipoprotein signal peptidase. Downstream of pbrC, the pbrD gene, encoding a Pb(II)-binding protein, was identified in a region of DNA, which was essential for functional lead sequestration. Pb(II)-dependent inducible transcription of pbrABCD from the PpbrA promoter is regulated by PbrR, which belongs to the MerR family of metal ion-sensing regulatory proteins. This is the first report of a mechanism for specific lead resistance in any bacterial genus.

A microbial biosensor to predict bioavailable nickel in soil and its transfer to plants.

Ralstonia eutropha strain AE2515 was constructed and optimised to serve as a whole-cell biosensor for the detection of bioavailable concentrations of Ni2+ and Co2+ in soil samples. Strain AE2515 is a Ralstonia eutropha CH34 derivative containing pMOL1550, in which the cnrYXH regulatory genes are transcriptionally fused to the bioluminescent luxCDABE reporter system. Strain AE2515 was standardised for its specific responses to Co2+ and Ni2+. The detection limits for AE2515 were 0.1 microM Ni2+ and 9 microM Co2+, respectively. The signal to noise (S/N) bioluminescence response and the metal cation concentration could be linearly correlated: for Ni2+ this was applicable within the range 0.1-60 microM, and between 9 and 400 microM for Co2+. The AE2515 biosensor strain was found to be highly selective for nickel and cobalt: no induction was observed with Zn(II), Cd(II), Mn(II), Cu(III) and Cr(VI). In mixed metal solutions, the bioluminescent response always corresponded to the nickel concentrations. Only in the presence of high concentrations of Co2+ (2 mM), the sensitivity to nickel was reduced due to metal toxicity. AE2515 was used to quantify the metal bioavailability in various nickel-enriched soils, which had been treated with additives for in situ metal immobilisation. The data obtained with strain AE2515 confirmed that the bioavailability of nickel was greatly reduced following the treatment of the soils with the additives beringite and steel shots. Furthermore, the data were found to correlate linearly with those on the biological accumulation of Ni2+ in specific parts of important agricultural crops, such as maize and potato. Therefore, the test can be used to assess the potential transfer of nickel to organisms of higher trophic levels, in this case maize and potato plants grown on nickel-enriched soils, and the potential risk of transfer of these elements to the food chain.

Development of molecular monitoring methods for the evaluation of the activity of sulfate- and metal reducing bacteria (SMRBS) as an indication of the in situ immobilisation of heavy metals and metalloids.

Sulfate- and metal reducing bacteria (SMRBs) are known for their capacity to reduce and precipitate heavy metals and metalloids (HMM) as metalsulfides (Luptáková A et al, 1998), which have the characteristic of forming stable precipitates due to their very low solubility product. Therefore, we examined the potential of using the activity of SMRBs to create a bioreactive zone or barrier for the in situ precepitation of heavy metals as a remediation strategy for heavy metal contaminated groundwater. In order to obtain insight in the ongoing biological processes for using this information to direct or optimize the in situ HMM- precipitation process, a monitoring strategy for sulfate- reduction activity of SMRBs must be designed using molecular methods. Here, we report the results of batch and column experiments which demonstrate the feasibility to stimulate the endogenous SRB- population, resulting in the in situ precipitation of HMM as sulfide complexes. Moreover, the sustainability of the in situ HMM precipitation wa s shown. For the development of molecular monitoring methods, the community structures of different bacterial consortia, obtained from bioreactors, was analysed by shotgun cloning of total community DNA followed by sequencing of the 16S rRNA- gene. The SRB- specific 16S rRNA- primerset SRB385R- 907F was used but this specificity to specifically amplify the 16S rRNA- gene of SRBs was low. Also, the dsr (dissimilatory sulfite reductase)- gene specific DSR1F- DSR4R primerset showed sometimes after amplification of the dsr- genes as part of the community structure analysis satellite bands on agarose gel. Present work is concentrating on the isolation and identification of SRB- strains in the different bacterial cultures. Shotgun cloning of the 16S rRNA- and dsr- gene of the strains and total community DNA will give the information that is necessary for the optimization of existing SRB- specific primers and design of new primers. These primers will be used for the development of monitoring techniques.

Chemical and biological parameters as tools to evaluate and improve heavy metal phytoremediation.

In this review, chemical and biological parameters are discussed that strongly influence the speciation of heavy metals, their availability to biological systems and, consequently, the possibilities to use bioremediation as a cleanup tool for heavy metal polluted sites. In order to assess heavy metal availability, a need exists for rapid, cost-effective systems that reliably predict this parameter and, based on this, the feasibility of using biological remediation techniques for site management and restoration. Special attention is paid to phytoremediation as an emerging technology for stabilization and remediation of heavy metal pollution. In order to improve phytoremediation of heavy metal polluted sites, several important points relevant to the process have to be elucidated. These include the speciation and bioavailability of the heavy metals in the soil determined by many chemical and biological parameters, the role of plant-associated soil microorganisms and fungi in phytoremediation, and the plants. Several options are described how plant-associated soil microorganisms can be used to improve heavy metal phytoremediation.

Evidence that Ralstonia eutropha (Alcaligenes eutrophus) contains a functional homologue of the Ralstonia solanacearum Phc cell density sensing system.

In the phytopathogen Ralstonia (Pseudomonas) solanacearum, control of many virulence genes is partly mediated by the Phc cell density sensing system. Phc uses a novel self-produced signal molecule [3-hydroxypalmitic acid methyl ester (3-OH PAME)], an atypical two-component system (PhcS/PhcR), and a LysR-type activator (PhcA) to regulate a reversible switching between two different physiological states. While Phc is present in most R. solanacearum strains, it is apparently absent from other pseudomonad plant pathogens and prokaryotic genomes that have been sequenced. Here, we report discovery of a phcA orthologue in the non-pathogenic, facultative chemolithoautotroph Ralstonia eutropha (Alcaligenes eutrophus) that fully complements R. solanacearum phcA mutants. We also demonstrate that some R. eutropha produce an extracellular factor that complements R. solanacearum mutants deficient in production of the 3-OH PAME signal molecule that controls phcA. Additionally, Southern blot hybridization analysis suggested that R. eutropha harbours other Phc components, such as PhcB (a biosynthetic enzyme for 3-OH PAME) and PhcS (a 3-OH PAME-responsive sensor kinase). Analysis of a phcA-null mutant of R. eutropha showed that phcA (and probably Phc) positively activates motility, in contrast to R. solanacearum where it represses motility. Similarly, the R. eutropha phcA mutant was unaffected in siderophore production, whereas inactivation of phcA in R. solanacearum increases siderophore production. Although our data strongly suggest that R. eutropha has a functional Phc-like system and support the phylogeny of Ralstonia, it implies that Phc may have a different physiological and ecological function in R. eutropha.

Regulation of the cnr cobalt and nickel resistance determinant of Ralstonia eutropha (Alcaligenes eutrophus) CH34.

The linked resistance to nickel and cobalt of Ralstonia eutropha-like strain CH34 (Alcaligenes eutrophus CH34) is encoded by the cnr operon, which is localized on the megaplasmid pMOL28. The regulatory genes cnrYXH have been cloned, overexpressed, and purified in Escherichia coli. CnrY fractionated as a 10.7-kDa protein in in vitro translation assays. CnrX, a periplasmic protein of 16.5 kDa, was overproduced and purified as a histidine-tagged fusion protein in E. coli. His-CnrX was found to possess a secondary structure content rich in alpha-helical and beta-sheet structures. CnrH, a sigma factor of the extracytoplasmic function family, was purified as an N-terminally histidine-tagged fusion. In gel shift mobility assays, His-CnrH, in the presence of E. coli core RNA polymerase enzyme, could retard at least two different promoter DNA targets, cnrYp and cnrHp, localized within the cnrYXH locus. These promoters and their transcription start sites were confirmed by primer extension. Purified His-CnrX did not inhibit the DNA-binding activity of His-CnrH and is therefore unlikely to be an anti-sigma factor, as previously hypothesized (EMBL M91650 description entry). To study the transcriptional response of the regulatory locus to metals and to probe promoter regions, transcriptional fusions were constructed between fragments of cnrYXH and the luxCDABE, luciferase reporter genes. Nickel and cobalt specifically induced the cnrYXH-luxCDABE fusion at optimal concentrations of 0.3 mM Ni(2+) and 2.0 mM Co(2+) in a noncomplexing medium for metals. The two promoter regions P(Y) (upstream cnrY) and P(H) (upstream cnrH) were probed and characterized using this vector and were found to control the nickel-inducible regulatory response of the cnr operon. The cnrHp promoter was responsible for full transcription of the cnrCBA structural resistance genes, while the cnrYp promoter was necessary to obtain metal-inducible transcription from the cnrHp promoter. The zinc resistance phenotype (ZinB) of a spontaneous cnr mutant strain, AE963, was investigated and could be attributed to an insertion of IS1087, a member of the IS2 family of insertion elements, within the cnrY gene.

Genetic engineering in the improvement of plants for phytoremediation of metal polluted soils.

Metal concentrations in soils are locally quite high, and are still increasing due to many human activities, leading to elevated risk for health and the environment. Phytoremediation may offer a viable solution to this problem, and the approach is gaining increasing interest. Improvement of plants by genetic engineering, i.e. by modifying characteristics like metal uptake, transport and accumulation as well as metal tolerance, opens up new possibilities for phytoremediation. So far, only a few cases have been reported where one or more of these characteristics have been successfully altered; e.g. mercuric ion reduction causing improved resistance and phytoextraction, and metallothionein causing enhanced cadmium tolerance. These, together with other approaches and potentially promising genes for transformation of target plants are discussed.

Identification of a gene cluster, czr, involved in cadmium and zinc resistance in Pseudomonas aeruginosa.

Pseudomonas aeruginosa CMG103 was isolated from a metal-polluted river in Pakistan and displayed a high level of Zn and Cd resistance. An omega-Km transposon mutant of strain CMG103, which showed a substantial decrease in resistance to Zn and Cd, was obtained. A 12.8 kb region determining Zn and Cd resistance in strain CM103 was cloned by complementing the mutant strain, and its nt sequence was determined. Five genes, czrSRCBA, involved in Zn and Cd resistance, were identified. The predicted gene products of czrCBA show a significant similarity with the proteins encoded by the plasmid borne metal resistant determinants czc, cnr and ncc of Ralstonia strains, which determine a chemiosmotic cation-antiporter efflux system. The predicted CzrS and CzrR proteins show a significant similarity to the sensor and regulatory protein, respectively, of two component regulatory systems, such as CopS/CopR and PcoS/PcoR involved in the regulation of plasmid-borne Cu-resistant determinants, and CzcS/CzcR involved in the regulation of czc. The cloned czr region contained downstream of czrCBA additional ORFs whose predicted gene products are similar to proteins involved in catabolism of aromatic compounds. DNA-DNA hybridization indicated strong conservation of czr in other environmental P. aeruginosa isolates and in the P. aeruginosa type strain PAO1, a clinical isolate. This was confirmed by a comparison of the sequence of the CMG103 czr region with the currently available genome sequence of strain PAO1. A high sequence identity (till 99% at the nt level) and organizatory conservation of the czr region of CMG103 was found in PAO1 as well regarding coding sequences as intervening sequences between ORFs. The czr locus was localized between coordinates 2400 and 2550 kb on the physical map of the chromosome of PAO1.

VITOTOX bacterial genotoxicity and toxicity test for the rapid screening of chemicals.

The VITOTOX test is a new bacterial genotoxicity test that was previously shown to be very rapid and sensitive. Initially only one Salmonella typhimurium strain (TA104 recN2-4) was used in the test. In this paper we introduce a second strain (TA104pr1) that can be used as an internal control to further enhance the reliability of the test. We demonstrate the usefulness of this pr1 strain in genotoxicity and toxicity testing. We also report on the results of a study where the VITOTOX test was performed on newly synthesized pharmaceutical compounds, or intermediate products in the synthesis of drug candidates. We demonstrate that the test gives identical results when performed independently in two different laboratories and that it correlates well with either the Ames test or SOS chromotest.

Effect of the siderophore alcaligin E on the bioavailability of Cd to Alcaligenes eutrophus CH34.

Alcaligin E, the siderophore of the heavy metal-resistant A. eutrophus strain CH34, was shown to interact with Cd and consequently affect its bioavailability and toxicity. The addition of alcaligin E markedly stimulated the growth in the presence of Cd of an alcaligin E-deficient CH34 derivative. Using bioluminescence assays, this effect could be assigned to a decrease in bioavailability of Cd in the presence of alcaligin E. However, Cd-uptake studies showed no influence of alcaligin E on the cellular concentration of Cd. Furthermore, by scanning electron microscopy, the morphology of precipitated Cd crystals was shown to be altered by alcaligin E. These data suggest that alcaligin E, besides its function in iron supply to the cell, provides a protection against heavy metal toxicity. A link between the A. eutrophus CH34 siderophore system and the czc-mediated Cd-efflux system is hypothesized.

The VITOTOX test, an SOS bioluminescence Salmonella typhimurium test to measure genotoxicity kinetics.

A new test to detect genotoxicity, that we refer to as the VITOTOX test, was developed. Four gene fusions that are based on the Escherichia coli recN promoter were constructed and evaluated for their SOS response-dependent induction. The wild-type recN promoter, a derivative mutated in the second LexA binding site, a derivative with a mutated -35 region, and a derivative from which both the second LexA binding site and the -35 region were mutated, were cloned upstream of the promoterless Vibrio fischeri luxCDABE operon of pMOL877, in such a way that lux became under transcriptional control of the recN promoter derivatives. The inducibility by the SOS response of the promoter constructs was tested in both E. coli and in the Ames test Salmonella typhimurium strains TA98, TA100 and TA104. In all strains, the highest sensitivity and induction was observed with the plasmids pMOL1067 and pMOL1068, that contain the lux operon under control of the recN promoter mutated in the second LexA binding site, or a recN promoter with a mutated -35 region, respectively. Therefore, strains containing pMOL1067 or pMOL1068 were further used for genotoxicity testing. With the VITOTOX test, genotoxicity was detected within 1-4 h. The VITOTOX test is very sensitive: for most products tested, the minimal detectable concentration (MDC) values were considerably lower (5 to > 100 times) than those described for the Ames test and the SOS chromotest. A good correlation was observed with the results from the Ames tests, but certain PAHs that are not mutagenic in the Ames test were genotoxic in the VITOTOX test. With the VITOTOX strains, the kinetics of SOS induction can be determined. This feature made it possible to distinguish between compounds in mixtures of genotoxic products so long as they had different induction kinetics.

Two-component regulatory system involved in transcriptional control of heavy-metal homoeostasis in Alcaligenes eutrophus.

The czc determinant, which mediates resistance to Co2+, Zn2+ and Cd2+ in Alcaligenes eutrophus CH34 by cation efflux, is regulated by a two-component regulatory system composed of the sensor histidine kinase CzcS and the response activator CzcR (in addition to other components previously described). Regulatory genes are arranged in an upstream regulatory region (URR) and a downstream regulatory region (DRR). Transcription of czcCBA and of the URR was regulated by heavy-metal cations. DNA sequencing of the region downstream of czcD revealed the presence of the czcR and czcS genes which together with czcD form the DRR. Regulation of the DRR was studied with a czcD::lacZ translational fusion and a czcS::lux transcriptional fusion. Expression of both genes is also regulated by heavy metals. The genes of the URR yielded three mRNAs of approx. 1200, 500 and 200 nucleotides, respectively. The genes czcCBA for the cation/proton antiporter CzcCBA were transcribed by one operon as a transcript of 6200 nucleotides.

Genetic and physical maps of the Alcaligenes eutrophus CH34 megaplasmid pMOL28 and its derivative pMOL50 obtained after temperature-induced mutagenesis and mortality.

We describe the construction of restriction and genetic maps of plasmid pMOL28, which has a size of approximately 180 kb. To do so, partial BamHI-digested DNA of pMOL28 was cloned into cosmid pLAFR3, which can package up to 20-30 kb inserted DNA. Subsequently, a cosmid walking strategy, combined with BamHI or EcoRI restriction analysis and hybridization, was used to construct the restriction maps for both enzymes. On these maps, 35 BamHI fragments and 29 EcoRI fragments were placed, accounting for a total size of approximately 180 kb. We also analyzed several rearranged derivatives of pMOL28 that were obtained after a process of temperature-induced mortality and mutagenesis (TIMM), which is characteristic for Alcaligenes eutrophus CH34 and related strains. The restriction and genetic maps of pMOL50 (222 kb), an enlarged derivative of pMOL28 obtained after TIMM, were constructed. By comparing the pMOL28 and pMOL50 maps, at least two transposable elements were identified which participated in the formation of pMOL50 from pMOL28 during TIMM. These transposable elements were IS1086, which was recently sequenced, and a new element named IS1089, which is located on the 44-kb inserted DNA fragment in pMOL50. Partial sequencing of IS1089 revealed similarity of this element with IS1071 of the chlorobenzoate catabolic transposon Tn5271 of Alcaligenes sp. BR60.

Siderophore-mediated iron uptake in Alcaligenes eutrophus CH34 and identification of aleB encoding the ferric iron-alcaligin E receptor.

Siderophore production in response to iron limitation was observed in Alcaligenes eutrophus CH34, and the corresponding siderophore was named alcaligin E. Alcaligin E was characterized as a phenolate-type siderophore containing neither catecholate nor hydroxamate groups. Alcaligin E promoted the growth of siderophore-deficient A. eutrophus mutants under iron-restricted conditions and promoted 59Fe uptake by iron-limited cells. However, the growth of the Sid- mutant AE1152, which was obtained from CH34 by Tn5-Tc mutagenesis, was completely inhibited by the addition of alcaligin E. AE1152 also showed strongly reduced 59Fe uptake in the presence of alcaligin E. This indicates that a gene, designated aleB, which is involved in transport of ferric iron-alcaligin E across the membrane is inactivated. The aleB gene was cloned, and its putative amino acid sequence showed strong similarity to those of ferric iron-siderophore receptor proteins. Both wild-type strain CH34 and aleB mutant AE1152 were able to use the same heterologous siderophores, indicating that AleB is involved only in ferric iron-alcaligin E uptake. Interestingly, no utilization of pyochelin, which is also a phenolate-type siderophore, was observed for A. eutrophus CH34. Genetic studies of different Sid- mutants, obtained after transposon mutagenesis, showed that the genes involved in alcaligin E and ferric iron-alcaligin E receptor biosynthesis are clustered in a 20-kb region on the A. eutrophus CH34 chromosome in the proximity of the cys-232 locus.

Identification of a partition and replication region in the Alcaligenes eutrophus megaplasmid pMOL28.

A 4.64 kb region of the 180 kb heavy metal resistance plasmid pMOL28 of Alcaligenes eutrophus CH34, previously shown to be able to replicate autonomously, was sequenced and analyzed. Three genes involved in plasmid maintenance were identified: parA28 and parB28 are involved in plasmid partitioning and stability, while repA28 encodes a protein required for replication. In addition to the par AB28 genes, a third locus, parS28, required in cis active partitioning was identified. The parABS28 locus of pMOL28 shows strong similarity in organization to the sop, par and rep regions, respectively, of the Escherichia coli F-factor, the E.coli P1 and P7 prophages and the Agrobacterium pTiB6S3 and pRiA4b plasmids. The ParAB28 proteins of pMOL28 also show similarity to the proteins encoded by two conserved open reading frames present in the replication regions of the Pseudomonas putida and Bacillus subtilis chromosomes. The functionality of the pMOL28 par region was examined by performing stability and incompatibility tests between pMOL28 and pMOL846 or pMOL850 which contain the 4.64 EcoRI replicon fragment of pMOL28, cloned in opposite orientations into pSUP202, which is itself unable to replicate in A. eutrophus. The RepA2 8 replication protein showed similarity to the RepL protein of P1, which is required for lytic replication of this E. coli phage. The replication origin of pMOL28, oriV28, seems to be located within the repA28 coding region, and pMOL28 replication may depend on transcriptional activation of oriV28.