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Applied and Environmental Microbiology, March 2008, p. 1829-1835, Vol. 74, No. 6
0099-2240/08/$08.00+0 doi:10.1128/AEM.02101-07
Copyright © 2008, American Society for Microbiology. All Rights Reserved.
,
Fernando Pagliai,
Nicolas Guiliani, and
Carlos A. Jerez*
Laboratory of Molecular Microbiology and Biotechnology, Department of Biology, and Millennium Institute for Cell Dynamics and Biotechnology, Faculty of Sciences, University of Chile, Santiago, Chile
Received 13 September 2007/ Accepted 5 January 2008
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Genetic capabilities to degrade Pn are present in gram-negative and some gram-positive bacteria. Four classes of enzymes involved in Pn metabolism have been characterized: phosphonoacetate hydrolase, which cleaves specifically phosphonoacetate (17); phosphonopyruvate hydrolase (27); phosphonatase, which cleaves phosphonoacetaldehyde, the transamination product of 2-aminoethyl phosphonic acid (14); and C-P lyase, which is the most widespread enzymatic pathway for Pn degradation, cleaving the C-P bond of a broad spectrum of Pn (32). In Escherichia coli, all the functions for phosphonate transport and degradation are encoded by an operon (composed of 14 genes and named phnCDEFGHIJKLMNOP) whose expression is induced by phosphate starvation as part of the Pho regulon (34). In this bacterium, C-P lyase is a multienzyme complex encoded by seven genes, phnGHIJKLM, and enzymatic activity has been detected only in whole permeabilized cells; it has never been detected in cell extracts (18, 32).
Acidithiobacillus ferrooxidans is a chemolithoautotrophic acidophilic bacterium that obtains its energy from the oxidation of hydrogen, ferrous iron, elemental sulfur, or partially oxidized sulfur compounds (23, 30). This ability makes it of great industrial importance due to its applications in biomining. During these industrial processes, microorganisms are normally subjected to stressing circumstances in their environment, such as temperature and pH changes, nutrient starvation, and the presence of toxic heavy metals, which can affect their physiological conditions. Phosphorus plays an essential part of cell structure and metabolism, forming part of nucleic acids, phospholipids, lipopolysaccharides, nucleotide cofactors, and some proteins, where it is incorporated through posttranslational modification (28). The lack of phosphate (Pi) may therefore greatly affect the bioleaching of minerals (21). Bacteria meet their phosphorus requirements through the assimilation of Pi and the accumulation of various phosphorus containing compounds, such as polyphosphates (polyP) (13). However, Pn can also be used as an alternative phosphorus source when the microorganisms possess the genetic capabilities to transport and degrade them (12, 25, 34).
We have previously studied the Pi starvation response (24) and the metabolism of inorganic polyP in A. ferrooxidans (2). By using two-dimensional polyacrylamide gel electrophoresis, we isolated a PstS protein which was induced in cultures starved of Pi and found in this acidophilic bacterium orthologs to the E. coli Pho regulon genes (31). Further analysis revealed the presence of a complete gene cluster with high identity to the C-P lyase genes from E. coli, suggesting that A. ferrooxidans may also have the ability to degrade Pn and use them as valuable phosphorus sources.
In this work, we found that A. ferrooxidans was able to grow on methyl-phosphonate (M-Pn) or ethyl-phosphonate (E-Pn) as the only phosphorus source. Furthermore, the increased expression levels of C-P lyase genes when the microorganism was grown on M-Pn indicate that A. ferrooxidans may utilize the environmental Pn pool, a capacity that confers it a growth and survival advantage relative to other microorganisms unable to utilize Pn in their natural environments. This advantage, in turn, may be important in industrial biomining operations.
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PolyP quantification.
PolyP was quantified by using a two-step conversion into ATP by recombinant E. coli polyP kinase (PPK) and quantification of the ATP formed by luciferase to generate light (3). First, polyP was extracted from cell extracts by using glass milk and then it was assayed by using the reverse reaction of PPK in ADP excess. Finally, the ATP content was assayed by using the firefly luciferase ATP assay and the luminescence was measured by using a luminometer (BioScan Lumi/96). Concentration of polyP is given in terms of Pi residues.
RNA techniques.
Total RNA was prepared from A. ferrooxidans cultures by a hot-phenol method (8), with some modifications. The RNA was subsequently extracted twice with chloroform and precipitated overnight at –80°C. RNA pellets were washed twice with 70% ethanol and resuspended in nuclease-free water. DNA was eliminated by the addition of 30 U RNase-free DNase (Amersham). RNAs were stored at –80°C. For the cotranscription experiments, a reverse primer hybridizing to the phnM gene was used and the cDNA synthesis was carried out with 1 µg of total RNA from a culture grown with M-Pn. PCR amplifications were performed with 1 µl of a 1/20 dilution of the cDNA and 25 pmol of each primer. Amplification conditions included an initial 3-min denaturation at 95°C, followed by 35 cycles of 30 s at 95°C, 30 s at 55°C and 1 min at 72°C and finished by 3 min at 72°C. All primers used are shown in Table 1.
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TABLE 1. Oligonucleotides used in this work
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-32P]dCTP (Amersham Biosciences). In vitro-transcribed, "spiked" RNA was added to the labeling reaction for normalization purposes (1, 8). After the RT reaction, the RNA template was degraded by alkaline treatment and the cDNA probes were purified by using MicroSpin S-200 columns (Amersham Pharmacia Biotech). After hybridization and washing, the membranes were air dried and exposed to PhosphorImager screens for variable times. The screens were then scanned on a PhosphorImager (Molecular Imager FX system; Bio-Rad) at a resolution of 50 µm/pixel. Analysis and quantification of the spot signals were performed with VersArray 1.0 software (Bio-Rad).
Real time RT-PCR.
Primers for real-time reverse transcription-PCR (RT-PCR) were designed with the LightCycler probe design software (Roche). For the cDNA synthesis, 0.5 µg of total RNA was reverse transcribed for 1 h at 42°C by using Moloney murine leukemia virus-RT (Promega) and 10 pmol of an ORF-specific reverse primer. PCR was carried out by using the LightCycler system (Roche). Twenty-microliter reaction mixtures were set up in LightCycler capillaries by using the FastStart DNA Master SYBR green mix. Following the manufacturer's instructions, the reaction mixture contained 1 µl of a 1/20 dilution of the cDNA as the template and 0.5 µl of each corresponding primer. Standard curves for the pho84l, phnG, and phnM genes were constructed by using serial dilutions of genomic DNA from A. ferrooxidans ATCC 23270, ranging from 10 ng to 1 pg, as the template and each corresponding primer pair. Thermal cycling conditions were an initial denaturation at 95°C for 10 min, followed by 40 cycles at 95°C for 5 s, 60 to 61°C for 5 s, and 72°C for 16 s. Fluorescence measurements were recorded at the end of each extension step.
Search for putative pho boxes in A. ferrooxidans genome.
Sequences 250 bp upstream of the putative A. ferrooxidans pstS1 and pstS2 genes were analyzed by using the MAST algorithm (4) for searching conserved motifs. After the identification of two putative motifs related to pho boxes in each promoter region of these genes, respectively, these four sequences were aligned using ClustalW. A hidden Markov model was constructed using the HMMER package of programs, version 2.3 (7). Subsequently, the hidden Markov model of pho boxes was used to search multiple nonoverlapping matching hits in the complete A. ferrooxidans genome sequence (www.tigr.org/db.shtml). After manual inspection of the putative A. ferrooxidans pho boxes with respect to their position and distance to their closest gene, 22 were selected for additional analysis.
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FIG. 1. Comparison of the physical organization of phn operons from A. ferrooxidans type strain (A) and E. coli (B). Black arrows indicate A. ferrooxidans genes homologous to E. coli phn genes. The white arrows indicate genes from E. coli phn genes that are not present in A. ferrooxidans. Shaded arrows indicate those A. ferrooxidans genes not present in E. coli.
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A. ferrooxidans can grow using M-Pn or E-Pn as the sole phosphorus sources.
The ability of A. ferrooxidans to grow in M-Pn or E-Pn was analyzed (Fig. 2). It is clear that the microorganism was able to grow in both types of Pn as the sole phosphorus sources (Fig. 2A and B). On the other hand, minimal growth of the bacteria was observed in control subcultures carried out in the absence of Pi. Bacterial growth was sustained for more than three subcultures with each of these Pn (data not shown). It has previously been stated that an important physiological feature of phosphonate degradation is the necessary "adaptation" of cells to these compounds. Thus, it has been shown that the degradation of and cell growth on Pn as the sole phosphorus sources begin after a prolonged latent phase, which varies strongly depending on the culture and nature of the phosphonate (12). A similar situation was observed when M-Pn and E-Pn were used by A. ferrooxidans, with different lag periods and cell numbers reached during the second subcultures (Fig. 2). The cell numbers attained after growth in the tested Pn were similar to those reached by the standard growth of A. ferrooxidans in the presence of Pi (2 x 108 to 4 x 108 cells/ml). Bacteria grew faster during the first subcultures in Pn compared with the second and additional subcultures (data not shown). This may be explained because A. ferrooxidans is a polyP-accumulating organism (2), and these polymers are utilized as a phosphorus source during growth in the first subculture in the presence of Pn. In subsequent subcultures, the microorganisms should not have an excess of Pi to store in the form of polyP, as suggested by Fig. 2. To additionally test this idea, we measured polyP levels in cells grown in M-Pn during two subcultures and compared them with those in cells grown in the presence of Pi. Cells grown in the presence of Pi had polyP levels of 55 nmol ATP/mg of protein, whereas M-Pn-grown cells had only 3% of the polyP levels found in control cells. A similar polyP reduction was observed in cells grown in E-Pn (results not shown). The capability to use Pn, which in some environments constitutes a substantial fraction of dissolved organic phosphorus (6, 12, 25), would provide A. ferrooxidans a competitive advantage in an environment, such as the one found in commercial biomining operations that may periodically experience a scarcity of Pi. Under the presence of excess phosphate, A. ferrooxidans accumulates massive amounts of polyP (2), a phenomenon clearly not taking place during growth in the presence of Pn.
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FIG. 2. Growth of A. ferrooxidans type strain using Pn as the sole phosphorus source. (A) Cells grown in thiosulfate as the energy source were inoculated in medium in which Pi was replaced by 1 mM M-Pn or in medium with no Pi added as control. Cells grown under these conditions in a first subculture were then inoculated in a second subculture under the same M-Pn concentration as that used in the first subculture (open circles) or in the absence of Pi (open squares). (B) Conditions were the same as described in the legend for panel A, except that E-Pn was used as phosphonate and the cells were grown in ferrous iron as the energy source. After being grown in the last condition for a first subculture, second subcultures were carried out in E-Pn (closed circles) or in the absence of Pi (closed squares). The error bars indicate the standard deviations based on three different experimental values.
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FIG. 3. A. ferrooxidans phn genes are cotranscribed. (A) cDNA was synthesized with a reverse primer hybridizing to the phnM gene (thicker black arrow) and A. ferrooxidans total RNA extracted at the exponential phase from a culture grown in M-Pn. (B) PCR amplifications were carried out with this cDNA and each corresponding primer pair (thin black arrows). Determination of the cotranscription for each pair of adjacent genes was carried out by using primers labeled D1 (upstream genes) and R1 (downstream genes) in Table 1. The results shown were obtained after 32 PCR cycles. PCRs using cDNA templates synthesized in the presence (+) or absence (–) of reverse transcriptase to detect the possible presence of genomic DNA contamination are shown.
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FIG. 4. Induction of expression of phn genes in A. ferrooxidans type strain as determined by DNA macroarray experiments. (A) Control membrane hybridized with cDNA prepared from a culture grown in the presence of Pi. (B) Membrane hybridized with cDNA obtained from a culture grown in 1 mM M-Pn. Numbers under the spots indicate the increase in the transcript levels for each gene expressed as the ratio of normalized intensities.
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TABLE 2. Induction of transcript levels for some phn genes from the type strain of A. ferrooxidans as determined by real-time RT-PCRa
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In our studies of the phosphate starvation response of A. ferrooxidans, we have determined that the biosynthesis of the PstS2 protein was highly induced in response to Pi starvation (31). A 10-fold induction of this transcript was also observed in cultures grown in M-Pn as the only phosphorus source (Fig. 4), most likely due to a Pi starvation condition, as mentioned previously.
Surprisingly, we did not find a Pit-like transporter in this bacterium; instead we found an ORF coding for a protein similar to the Pho84 Pi transporter from S. cerevisiae (2). Pho84 and Pho89 are the major Pi transporters in the yeast S. cerevisiae. Pho84, like Pit, belongs to the family of Pi:H+ symporters and is a member of the major facilitator superfamily. The Pho84 transporter is functional only in acidic environmental conditions (19). It is remarkable that A. ferrooxidans, being an acidophilic microorganism, possesses a putative yeast Pho84 Pi transporter. In this regard, only proteins similar to Pho84, but not to Pit (or Pho89) are present in the genomes of other acidophilic microorganisms (2). Since A. ferrooxidans does not possess the genes phnCDE, which in E. coli code for a putative phosphonate transport system for the utilization of Pn as phosphorus sources, it is tempting to speculate that pho84, whose expression was also induced in the presence of phosphonate (Table 2), may also be able to transport these compounds to the interior of A. ferrooxidans. In this connection, it is known that a strain of the yeast Kluyveromyces fragilis is able to utilize an organophosphonate as a nitrogen source (26).
Under Pi limitation conditions, most A. ferrooxidans phn genes showed a rather limited degree of induction under our experimental conditions (data not shown). This result, compared with the strong induction of these genes in the presence of M-Pn (Fig. 4), suggests that in addition to Pi starvation, Pn themselves may also play a role in the induction of the genes that the cell expresses to cope with their presence. In this regard, it has recently been shown that N-(phosphonometyl) glycine (glyphosate) induces the expression of the gene coding for a porin-like protein in Bradyrhizobium sp. (Lupinus) (5). Obviously, additional genetic experiments would be required to verify our suggestions. Unfortunately, this is not currently feasible, as at the time of writing, there are no efficient genetic systems for A. ferrooxidans to obtain mutants in each of these genes to demonstrate the functional genetic controls during Pi starvation and Pn metabolism responses.
Presence of phn genes in other biomining organisms: genomic and environmental aspects.
Pn are ubiquitous in nature, but not all microorganisms possess the genetic capabilities needed to degrade and use them as phosphorus sources. A search for phn genes in 140 complete bacterial genomes showed that homologous clusters for C-P lyase have great structural and compositional variation among microorganisms, suggesting that these degradative pathways have been subjected to extensive lateral gene transfers during their evolution (11). Nevertheless, phnGHIJKLM genes, which are essential for Pn cleavage, are generally linked together. Recently, it was reported that the presence of C-P lyase genes would confer an ecological advantage to Trichodesmium sp. in their colonization of marine environments, where Pi is generally present in nanomolar concentrations. It was demonstrated that these genes are expressed under Pi starvation conditions, and similar results were obtained with environmental Trichodesmium populations isolated from the western North Atlantic (6).
To our knowledge, this is the first report of an acidophilic chemolithoautotrophic microorganism that is able to use Pn as a valuable phosphorus source. We undertook a search for C-P lyase genes in the total and partial genomes of other biomining microorganisms from environmental samples covering mine drainage metagenome, an acid mine drainage biofilm community (15, 29) and the complete genome of Ferroplasma acidarmanus (9). However, we did not find genes related to phosphonate degradation in these microorganisms. When more genome sequences from biomining microorganisms are available, it will be of great interest to search for the presence of C-P lyase genes. This search will allow us to determine whether their presence is a unique characteristic of A. ferrooxidans or whether they are also present in other acidophilic microorganisms, conferring all of them the advantage of accessing the unique phosphorus pool derived from Pn in their extreme environments.
We also thank F. P. Chávez for helpful discussions and M. Handford for proofreading the manuscript.
Published ahead of print on 18 January 2008. ![]()
Dedicated to the memory of Arthur Kornberg, a great scientist and friend who introduced us to the "polyP world." ![]()
Present address: Aquatic Biotechnology, Biofilm Centre, University Duisburg-Essen, Geibelstr. 41, D-47057 Duisburg, Germany. ![]()
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