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.
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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
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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. We are
grateful
to
Professor
Aleksandra
Sk³odowska, Laboratory of Environmental
Pollution Analysis, Faculty of Biology, Warsaw University (Poland) for performing the
assays of cadmium.
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