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Quarterly

2004

Overexpression of genes involved in phytochelatin biosynthesis in Escherichia coli: effects on growth, cadmium accumulation and thiol level �

Vol. 52 No. 1/2005 109–116 QUARTERLY Overexpression of genes involved in phytochelatin biosynthesis in Escherichia coli: effects on growth, cadmium accumulation and thiol level. Anna Wawrzyńska1, Adam Wawrzyński1, Dali Gaganidze2, Edyta Kopera1, Katarzyna Piątek1, Wojciech Bal1 and Agnieszka Sirko1½ 1 Institute of Biochemistry and Biophysics, Polish Academy of Sciences, Warszawa, Poland; 2 Scientific Research Center of Agriculture Biotechnology, Tibilisi 380062, Georgia Received: 23 December, 2004; accepted: 18 February, 2005 Key words: cadmium, glutathione, phytochelatin, thiols In Escherichia coli, heterologous production of Schizosaccharomyces pombe phytochelatin synthase (PCS) along with overproduction of E. coli serine acetyltransferase (SAT) and g-glutamylcysteine synthase (gECS) was achieved and resulted in the accumulation of phytochelatins in bacterial cells. Overproduction of either gECS alone or simultaneous production of all three proteins in bacterial cells were accompanied by reduced growth rate in liquid cultures. Interestingly, bacteria overproducing either gECS or both SAT and gECS (with elevated level of g-glutamylcysteine but not of phytochelatins) were able to accumulate more cadmium per dry weight than the control. However, the most efficient cadmium accumulation was observed in bacteria with elevated levels of all three proteins: SAT, gECS and PCS. Therefore, “pushing” the entire pathway might be the most promising approach in modification of bacteria for potential bioremediation purposes because the level of intermediates, cysteine and glutathione, can limit the rate of production of phytochelatins. However, in such bacteria other metabolic process might become limiting for efficient growth. . This work was partially supported by the EU Commission through funding of FP5 project PHYTAC (QLRT-2001-00429 and QLRT- 2001-02778 [NAS]). D.G. was a holder of a fellowship from the European Fellowships Fund at IBB PAS. ½ Correspondence to: A. Sirko, Institute of Biochemistry and Biophysics, Polish Academy of Sciences, A. Pawińskiego 5A, 02-106 Warszawa, Poland; e-mail: asirko@ibb.waw.pl Abbreviations: AP, alkaline phosphatase; CMQT, 2-chloro-1-methylquinolinium tetrafluoroborate; g-Glu-Cys, g-glutamylcysteine; gECS, g-glutamylcysteine synthase; GSH, glutatione; IPTG, isopropyl b-D-1-thiogalactopyranoside; ORF, open reading frame; PBS, phosphate-buffered saline; PC, phytochelatin; PCS, phytochelatins synthase; rbs, ribosome-binding site; SAT, serine acetyltransferase; TFA, trifluoroacetic acid. 110 A. Wawrzyńska and others Organisms can avoid toxicity of heavy metals by three mechanisms: diminished accumulation, detoxification/reduction or complexation with ligands. An important class of heavy metal binding ligands is a family of phytochelatins (PCs), peptides that consist of repetitions of the g-glutamylcysteine (g-GluCys) dipeptide followed by a terminal glycine — the basic structure being (g-Glu-Cys)n-Gly [(PC)n], where n is generally in the range two to seven. PCs have been identified in a wide variety of plant species and in some microorganisms. The enzyme responsible for their production, phytochelatin synthase (PCS), was first identified by Grill et al. (1989) and characterized in a number of subsequent studies (Chen et al., 1997; Klapheck et al., 1995). The enzyme is a g-Glu-Cys dipeptidyl transpeptidase and catalyses transpeptidation of the g-Glu-Cys moiety of GSH either onto a second glutathione (GSH) molecule to form PC(n=2) or onto a PC molecule to produce a PC(n+1) oligomer. Significant recent advances in understanding of the molecular basis of PC biosynthesis and function have resulted from molecular genetic studies conducted in a number of model organisms. These approaches centered on the identification of Cd-sensitive mutants of the plant Arabidopsis thaliana and the yeasts Schizosaccharomyces pombe and Candida glabrata. In addition, expression of plant cDNAs in Escherichia coli and Saccharomyces cerevisiae cells was particularly useful in the identification and analysis of genes involved in functions related to heavy metal detoxification. PC biosynthesis may be regulated by a number of mechanisms. For example, in Brassica juncea, exposure to Cd produces a requirement for both cysteine and GSH for PC biosynthesis that is met by coordinate transcriptional regulation of genes involved in sulfur transport and assimilation (Heiss et al., 1999; Lee & Leustek, 1999) as well as GSH biosynthesis (Schafer et al., 1998). The prominent function of g-Glu-Cys peptides is sequestration of metals. It results in creation of 2005 metal-containing complexes that are accretions of multiple peptides of various lengths with metal ions. The PC synthase (PCS) activity is thought to be the major determinant of the rate of PC synthesis. Kinetic studies using plant cell cultures exposed to Cd demonstrated that PC biosynthesis occurs within minutes of exposure to the heavy metal and is independent of de novo protein synthesis (Rauser, 1999). PCS is activated by Cd2+, Cu2+, Ag+, Hg2+, Zn2+ and Pb2+ ions (Chen et al., 1997; Klapheck et al., 1995). The mechanism by which PCS is activated appears to be relatively non-specific with respect to the activating metal ion, although some metals are more effective than others. Overproduction of PCS from wheat in S. cerevisiae enhances tolerance to and accumulation of cadmium (Clemens et al., 1999). Recently, E. coli cells expressing A. thaliana PCS gene showed a marked accumulation of phytochelatins that in turn caused, after exposure, accumulation of heavy metals such as cadmium or metalloid arsenic (Sauge-Merle et al., 2003). The authors observed a rapid depletion of glutathione in these bacteria. This result is in agreement with the observation that transgenic Arabidopsis overexpressing an Arabidopsis phytochelatin synthase gene (AtPCS1) showed, paradoxically, hypersensitivity to Cd or Zn (Lee et al., 2003), which disappeared when GSH was supplemented in the medium. Thus, the level of the substrate for PCS, GSH-Cd, might be the limiting factor determining the rate of phytochelatin synthesis. It is also possible that the antioxidative system in plants might have been affected by overexpression of AtPCS1 and this may have resulted in the observed hypersensitivity. The oxidative stress might have been generated in those plants by cadmium, as its phytotoxicity is generally ascribed to its reactivity with ligands containing oxygen, nitrogen and sulfur that often produce reactive oxygen species (Sanita di Toppi & Gabbrielli, 1999). Although this clearly demonstrates that PCs Vol. 52 Phytochelatin production and cadmium accumulation in bacteria can have an important role in detoxification, it remains to be determined whether this is their primary or incidental function. Other proposed roles for PCs include their involvement in essential heavy metal homeostasis, iron metabolism and sulfur metabolism (Rauser, 1999; Zenk, 1996). The aim of this work was to investigate the effects of simultaneous overproduction in E. coli cells of three enzymes involved in phytochelatin biosynthesis: PCS from S. pombe and two proteins from E. coli, serine acetyltransferase (SAT) and g-glutamylcysteine synthase (gECS). SAT is involved in the production of O-acetylserine and is supposed to limit the synthesis of cysteine, while gECS is involved in the first step of glutathione synthesis assumed to be much more limiting than the second step catalyzed by glutathione synthase. MATERIALS AND METHODS Bacterial growth and culture conditions. E. coli strain BL21(DE3) was transformed with plasmids indicated: pET28a, pGCP, pGCE or pGSH. Bacteria were grown in LB medium in the presence of kanamycin (50 mg/ml). O/N cultures were usually grown at 37°C, then refreshed (1:100) in the same medium and grown at 30°C with rotary shaking. b-D-1-thiogalactopyranoside (IPTG) was added to the cultures at A600 0.3–0.5 to a final concentration of 1 mM. After one hour of induction, CdCl2 was added to the concentrations indicated. Cadmium content in bacteria was measured always in cultures grown for 5 h in the presence of 0.5 mM CdCl2. DNA cloning and plasmid construction. Standard molecular cloning techniques were performed as described (Sambrook et al., 1989). The following oligonucleotides were used for amplification of the E. coli cysE (EXEC1: 5¢-cgt cta gaa agg aga tat acc atg tcg tgt gaa gaa ctg gaa a-3¢ and EXEC2: 5¢-gct cta gag tcg act tag atc cca tcc cca tact ca-3¢) and 111 gshA (GSH1: 5¢-cgg gat cca tgg tcc cgg acg tat ca gag-3¢ and GSH2: 5¢-aac tgc agt cta gat cag gcg tgt ttt tcc ag-3¢) and S. pombe PCS (EXPC1: 5¢-cgg tcg aca agg aga tat acc atg gac att gtt aaa cga gca gtc-3¢ and EXPC2: 5¢-gcg tcg act cac gta ttt tta cag cag ctt ga-3¢) genes using the respective genomic DNA. Western blots. Proteins were resolved in SDS/polyacrylamide 12.5% gels. Electrophoresis was carried out using conditions recommended by the manufacturer of the electrophoresis apparatus (BioRad). The separated proteins were electroblotted onto either nitrocellulose membrane (Amersham) or PVDF membrane (Schleicher & Schuell) using an apparatus for “wet transfer” (Kucharczyk T.E., Poland) following the manufacturer’s protocol. Membranes carrying immobilized proteins were incubated for 1 h in a blocking solution (5% non-fat milk in PBS (10 mM Na/KPO4 buffer, 0.15 M NaCl, pH 7.4)) to saturate non-specific binding sites. Then they were incubated for 1 h in a solution of specific rabbit polyclonal antibody (primary antibody) diluted in PBS, followed by four washes (5 min each) in PBS. As a secondary antibody, anti-rabbit IgG conjugated with alkaline phosphatase (AP) were used (Sigma). The 60 min incubation with secondary antibody was followed by four washes (5 min each) in PBS and finally, NBT/BCIP (Promega) was used as the substrate for the AP enzymatic reaction. Determination of thiols in bacterial samples. Bacteria from 100 ml cultures were centrifuged (8 000 ´ g, 10 min, 4oC), washed in 0.9% NaCl, resuspended in 500 ml of 0.1 M HCl, sonicated 3 times (5 min each) and centrifuged (14 000 ´ g, 15 min, 4°C) to remove debris. To 200 ml of the extract, 28 ml of 1 M NaOH and 8 ml of 6 M NaBH4 was added. The mixture was vortexed and stored for 2 min. Then, 20 ml of 3 M HCl was added in order to decompose the excess of NaBH4. The mixture was centrifuged (14 000 ´ g, 1 min). Next, 400 ml of 0.2 M phosphate buffer, pH 7.6, and 10 ml of 0.1 M 2-chloro-1-methylquinolinium 112 A. Wawrzyńska and others tetrafluoroborate (CMQT) was added, the mixture was vortexed, put aside for 4 min, and acidified by adding 100 ml of 3 M HCl, followed by centrifugation (12 000 ´ g, 3 min) and filtration through a 0.22 mm filter. Aliquots of 50 ml of the final solution were injected into an HPLC system (Waters Breeze) via an autosampler and separated on a C-18 column (Waters Symmetry, 4.6 ´ 150 mm). Elution buffer A was 0.1% (v/v) trifluoroacetic acid (TFA) in H2O and buffer B was 90% (v/v) acetonitrile in H2O, 0.1% TFA. The gradient used for these experiments was 0–50% buffer B in 25 min, flow rate 1 ml/min, detection by absorption at 354 nm. Determination of cadmium in bacterial cells. Dried samples (bacterial cells), after suspending in 9 ml of 65% HNO3 supplemented with 0.9 ml 35% H2O2, were mineralized for 25 min (180°C, 942 W) in a laboratory microwave oven ETHOS PLUS (Milestone). Then the samples were cooled and 0.1 ml of 35% H2O2 was added. Cd content in bacterial cells was measured using Flame Atomic Absorption Spectrophotometry (SOLAAR M6, TJA Solutions), mixture of air/acetylene, absorption at 228.8 nm. The samples were measured in triplicates. RESULTS Construction of plasmids containing genes involved in phytochelatin biosynthesis Plasmids containing cysE and gshA genes from E. coli or PCS from S. pombe previously cloned in our laboratory (B³aszczyk, 2004) served as templates in polymerase chain reaction (PCR). The pairs of primers EXEC1/ EXEC2, GSH1/GSH2 and EXPC1/EXPC2 were used to obtain cysE, gshA and PCS open reading frame (ORF) fragments, respectively. The PCR products (0.8 kb for cysE, 1.6 kb for gshA and 1.2 kb for PCS) were digested with appropriate restriction enzymes, cloned separately into pUC19 and sequenced. Sequencing 2005 confirmed the presence of the respective ORFs without errors. The subsequent multistep cloning into pET28a vector resulted in the construction of the plasmids schematically shown in Fig. 1. Plasmid pGSH contains gshA gene transcribed as a monocistronic transcript from a T7 polymerase-dependent Figure 1. Schematic map of the inserts present in the plasmids used in this work. The vector in all cases is pET28a. Only the restriction sites used for final cloning are shown. PT7, promoter of T7 bacteriophage; 6 x His, histidine tag; T, transcription terminator; gshA, cysE and PCS, sequences encoding E. coli g-glutamylcysteine synthase (gECS), serine acetyltransferase (SAT) and S. pombe phytochelatin synthase (PCS), respectively. promoter. Polycistronic transcripts can be formed in the case of pGCE and pGCP containing gshA/cysE and gshA/cysE/PCS, respectively. Efficient translation of each ORF is assured by separate ribosome-binding sites (rbs) introduced upstream of the coding regions of cysE and PCS, while gshA can be translated using the rbs present in pET28a. Comparison of growth rates, accumulation of cadmium and the level of non-protein thiols in bacteria transformed with the constructed plasmids Plasmids pET28a, pGCP, pGCE or pGSH were introduced into E. coli and the transformants were grown in LB medium containing 0.5 mM CdCl2 in order to identify the plasmid causing the strongest cadmium accumulation in bacterial cells. The growth of the bacterial cultures was monitored by measurement of absorbance at 600 nm (Fig. 2B) and Vol. 52 Phytochelatin production and cadmium accumulation in bacteria cadmium accumulation was assayed and calculated per mg of dry mass of bacterial cells (Fig. 2C). In parallel, cultures were grown in the LB medium without cadmium (Fig. 2A). 113 cadmium varied depending on the plasmid, which can be ordered as follow: pGCP, pGSH, pGCE and pET28a from the slowest to the best growers (Fig. 2B). Surprisingly, overproduction of either gECS alone or of all three proteins resulted in growth retardation, even without cadmium in the medium. Overproduction of SAT together with gECS resulted in a growth rate similar to the control. To monitor the effects of the overproduction of the proteins in question on the levels of non-protein thiols, acid extracts from bacterial cells were analyzed by HPLC after derivatization of SH-groups with CMQT (Fig. 3). The identity of the marked peaks Figure 2. Growth rates of E. coli transformants at 30°C in LB medium without (A) and with 0.5 mM CdCl2 (B), and cadmium contents in dry weight (DW) of bacteria (C). For the growth rates, one representative of three independent cultures is shown with arrows indicating the time of addition of IPTG and CdCl2. For the cadmium contents, average values from three independent cultures (each measured in triplicate) are shown with standard deviations indicated. PET, pET28a (vector); GCP, pGCP (cysE gshA PCS); GCE, pGCE (cysE gshA); GSH, pGSH (gshA). The results indicated that bacteria harboring pGCP accumulated more cadmium than the other transformants, next were bacteria transformed with pGCE and pGSH, the latter being only a bit more effective than the bacteria transformed with pET28a. The growth of the transformants in the medium containing Figure 3. HPLC chromatograms of acidic extracts of bacterial samples. Peaks due to non-thiol compounds are marked with (*). Positions of identified thiols are indicated. The bacteria strains are transformed with the plasmids indicated. (gGlu-Cys, GSH, PC2, PC3, PC4, PC5, PC6, PC7) was confirmed by mass-spectroscopy analysis (not shown). The results clearly demonstrate that (i) phytochelatins are produced in bacteria transformed with pGCP, but not in those transformed with the other plasmids, 114 A. Wawrzyńska and others 2005 (ii) GSH level in these bacteria is lower than in the other strains, (iii) in bacteria transformed with plasmid pGCE containing two genes — cysE and gshA — a strong increase of gGlu-Cys level is observed, and (iv) a much smaller elevation of gGlu-Cys level is observed in bacteria transformed with pGSH. Detection of the proteins encoded by the polycistronic transcript of the pGCP plasmid A polycistronic transcript was expected to be formed upon induction of the T7 polymerase-dependent promoter of the plasmid pGCP. To test if efficient translation of all open reading frames took place, expression of each of the three genes was verified at the protein level by Western blot technique using previously obtained three types of rabbit polyclonal antibodies specifically recognising E. coli SAT, gECS and S. pombe PCS (B³aszczyk, 2004). The genes cysE (encoding SAT) and gshA (encoding gECS) are present in the E. coli genome; however, in the conditions of the experiment no SAT or gECS proteins were detected in control bacteria transformed with the empty plasmid pET28a (Fig. 4C). This is probably due to the low expression of these genes in the rich medium. Concerning the expression from the plasmid pGCP, PCS as well as gECS were expressed quite efficiently, while only a low level of SAT protein was found (Fig. 4C). The level of the proteins was apparently unaffected by the presence of cadmium in the medium. DISCUSSION The growth characteristics of bacteria overproducing SAT, gECS and PCS in various combinations confirm that efficient cysteine production might be the limiting factor for glutathione biosynthesis in bacteria (Li et al., 2004). This would explain the growth reduction of the strain containing pGSH plasmid Figure 4. Selected characteristics of E. coli transformed with pGCP (GCP) and pET28a (PET) o grown at 30 C in LB medium with 0 or 0.5 mM CdCl2. Panel A. Comparison of growth rates; Panel B. Cadmium accumulation in the dry weight (DW) of bacteria; Panel C. Western blot of protein extracts from the bacterial transformants using rabbit polyclonal antibodies as indicated. C-1, C-2 and C-3 are extracts from transformants containing appropriate plasmids with single genes, cysE, gshA and PCS, respectively. Protein extract from bacteria containing: 1, pGCP, grown with IPTG in the presence of 0.5 mM CdCl2; 2, pGCP, grown with IPTG without cadmium; 3, pGCP, without IPTG and without cadmium; 4, pET28a, with IPTG and 0.5 mM CdCl2; 5, pET28a, with IPTG without cadmium; 6, pET28a, without IPTG and without cadmium. regardless of the presence of cadmium. An alternative explanation, that the reduced Vol. 52 Phytochelatin production and cadmium accumulation in bacteria growth of bacteria overproducing gECS is a result of ATP depletion (Li et al., 2004) can be ruled out because additional overproduction of SAT not only improves the growth of bacteria with higher gECS level (Fig. 2A, B) but also results in a higher level of gGlu-Cys. Interestingly, the GSH level in these bacteria is not increased in comparison to the control (Fig. 3). The elevation of gGlu-Cys was probably responsible for the increased accumulation of cadmium by bacteria overproducing SAT and gECS (pGCE) and bacteria overproducing gECS alone (pGSH). Simultaneous overproduction of all three proteins resulted in a decrease of glutathione in comparison to all other strains. As the level of gGlu-Cys was higher in this strain than in the control, this observation suggests that the next enzymatic activity, glutathione synthase, was limiting for production of phytochelatins. In summary, bacteria producing phytochelatins due to inducible expression of three genes: S. pombe PCS and E. coli cysE and gshA were obtained. The important observation was that transformants overproducing all three proteins grew slower than the con- 115 trol in medium without cadmium (however, cadmium additionally retarded their growth). Then, overproduction of these proteins did not improve bacterial tolerance to cadmium but resulted in increased cadmium accumulation per dry weight of bacteria. Interestingly, in the analyzed bacteria not only phytochelatins and GSH but apparently also gGlu-Cys is involved in binding of cadmium ions. We gratefully acknowledge Dr. Grazyna Chwatko and Professor Edward Bald from the Department of Enviromental Chemistry, University of Łódź (Poland) for providing us with a batch of 2-chloro-1-methylquinolinium tetrafluoroborate (CMQT) and for sharing their expertise regarding application of CMQT in the HPLC analysis of thiols. 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