Previous Article | Next Article 
Applied and Environmental Microbiology, March 1999, p. 1092-1098, Vol. 65, No. 3
0099-2240/99/$04.00+0
Copyright © 1999, American Society for Microbiology. All rights reserved.
Enhanced Bioaccumulation of Heavy Metal Ions by Bacterial
Cells Due to Surface Display of Short Metal Binding
Peptides
Pavel
Kotrba,1
Lucie
Dole
ková,2
Víctor
de Lorenzo,3 and
Tomas
Ruml1,*
Department of Biochemistry and Microbiology,
Institute of Chemical Technology, 166 28 Prague,1 and Department of Biochemistry,
Institute of Organic Chemistry and Biochemistry CAS, 166 10 Prague,2 Czech Republic, and Centro
Nacional de Biotecnologia, CSIC, 28049 Madrid,
Spain3
Received 7 August 1998/Accepted 18 December 1998
 |
ABSTRACT |
Metal binding peptides of sequences Gly-His-His-Pro-His-Gly (named
HP) and Gly-Cys-Gly-Cys-Pro-Cys-Gly-Cys-Gly (named CP) were genetically
engineered into LamB protein and expressed in Escherichia
coli. The Cd2+-to-HP and Cd2+-to-CP
stoichiometries of peptides were 1:1 and 3:1, respectively. Hybrid LamB
proteins were found to be properly folded in the outer membrane of
E. coli. Isolated cell envelopes of E. coli
bearing newly added metal binding peptides showed an up to 1.8-fold
increase in Cd2+ binding capacity. The bioaccumulation of
Cd2+, Cu2+, and Zn2+ by E. coli was evaluated. Surface display of CP multiplied the ability
of E. coli to bind Cd2+ from growth medium
fourfold. Display of HP peptide did not contribute to an increase in
the accumulation of Cu2+ and Zn2+. However,
Cu2+ ceased contribution of HP for Cd2+
accumulation, probably due to the strong binding of Cu2+ to
HP. Thus, considering the cooperation of cell structures with inserted
peptides, the relative affinities of metal binding peptide and, for
example, the cell wall to metal ion should be taken into account in the
rational design of peptide sequences possessing specificity for a
particular metal.
 |
INTRODUCTION |
During the last few decades
extensive attention has been paid to the hazards arising from
contamination of the environment by heavy metals (35).
Decontamination of heavy metals in the soil and water around industrial
plants has been a challenge for a long time. The use of microorganisms
for the recovery of metals from waste streams (15, 17, 30,
31), as well as the employment of plants for landfill application
(47), has achieved growing attention. Lower cost and higher
efficiency at low metal concentrations make biotechnological processes
very attractive in comparison to physicochemical methods for heavy
metal removal (17).
The microbial processes for bioremediation of toxic metals and
radionuclides from waste streams employ living cells, nonliving biomass, or biopolymers as biosorbents (17, 30, 46).
Specific metabolic pathways resulting in bioprecipitation of heavy
metals or their biotransformation to less toxic or easily recoverable forms have been described (15, 17, 30, 31). A wide variety of fungi, algae, and bacteria are now under study or are already in use
as biosorbents for heavy metal remediation (17, 30, 46).
Metal binding by biomolecules of structural components or excreted
polymers is fortuitous, and relative efficiencies depend on attributes
of the metal ion, as well as on the reactivity of the provided ligands.
The macromolecular composition of biosorbent could be manipulated by
cultivation conditions (e.g., stress-inducible fungal melanins
[30]) to improve its metal binding properties.
The principles governing the selectivity of biomolecules for metal ions
are described by semiempirical and qualitative theories, such as the
HSAB (hard and soft acids and bases) principle and the Irwing-Williams
series of stability constants for divalent ions (26).
Anchoring of particular amino acid sequences to biosorbent material
could contribute to the selectivity for specific metal ions.
Biosorbents could be enriched with amino acids classified by HSAB
principles to be stronger ligands of transition metals than those
naturally present on the microbial surfaces (26, 30). The
principal benefit of selectivity should provide preference of
particular metal ions for its specific coordination preferences (1), exploiting peptides with known fold. Surface exposure of metal binding peptides could improve metal binding properties of
microorganisms employed in various systems based not only on biosorption but also on the metabolic activities located on the cell
surface (15, 31).
A number of vehicles, including subunits of cellular appendages or
outer membrane proteins, are now in use for the display and action of
enzymes, peptide libraries, antigenic determinants, or single-chain
antibodies on the surface of gram-negative bacteria (19).
The Escherichia coli maltoporin (LamB) has been well
characterized. The LamB protein is a trimeric outer membrane (OM)
protein of E. coli sustaining two biological functions. It
is used as a surface receptor by a number of coliphages, including
phage
(6, 12, 14), and participates in the transport of
maltose and maltodextrins across the OM (45). LamB tolerates
insertions of long heterologous peptides at a permissive loop (between
structural codons 153 and 154) exposed to the external medium without a
loss of function (5, 9, 11, 13, 21, 43, 44). Successful
attempts to introduce polyhistidine tails (41), as well as
yeast and human metallothioneins (42), to LamB have been
reported. The surface display of the polyhistidine tail and/or
metallothioneins led to a significant increase in the accumulation of
divalent heavy metal ions. The LamB protein was also used to search for repeating peptides responsible for a specific adhesion of E. coli to gold, chromium, or iron oxide (7, 8).
We examined metal binding properties of E. coli strains
displaying short peptides as a fusion to LamB protein. The
histidine-rich sequence Gly-His-His-Pro-His-Gly employed in this study
was named HP. HP represents one to three multiple repeats along the
C-terminal part of the human plasma metal transport protein known as
the histidine rich-glycoprotein (HRG) (28). The HRG binds
heme and various divalent heavy metal ions with the following apparent order of affinity: Cu2+ ~ Hg2+ > Zn2+ > Ni2+ > Cd2+ > Co2+ (35). The HP sequence is believed to form
surface metal binding sites (MBSs) of HRG, and it has been also
successfully used to immobilize Cu2+ and Zn2+
on IMAC columns (27). The cysteine-rich amino acid sequence, named CP (Gly-Cys-Gly-Cys-Pro-Cys-Gly-Cys-Gly), was previously selected
in our laboratory as a result of screening of synthetic peptides
consisting of cysteine and histidine residues for Cd2+
binding (29). CP was further characterized and employed for display on the E. coli surface.
 |
MATERIALS AND METHODS |
Chemical synthesis of peptides.
The standard Merrifield
solid-phase technique with
diisopropylcarbodiimide-1-hydroxybenzotriazole activation chemistry
was used for the synthesis of the CP peptide of the sequence
AcOGly-Cys-Gly-Cys-Pro-Cys-Gly-Cys-resin and the HP peptide of the
sequence AcOGly-His-His-Pro-His-Gly-resin. The peptides were
synthesized on TentaGel resin without cleavable linker (Rapp polymere).
FMOC (9-fluorenylmethoxy carbonyl)-tertiary butyl-protected amino acids
(Senn Chemicals) were added to the peptide-conjugated resin in a
threefold molar excess to amino groups at a concentration of 0.3 M. Coupling was continued for 1 h, and each position was doubly
coupled. The FMOC group was deprotected with 20%
piperidine-dimethylformamide (the first treatment was for 2 min,
followed by the second for 20 min). After coupling of the last amino
acid, the N terminus was acetylated. The deprotection of the peptide
side chains was accomplished by treatment with 90% trifluoroacetic
acid-2.5% thioanisole-2.5% ethanedithiol-2.5 triisopropylsilane-2.5% water for 2 h. The resin was then washed and neutralized with 10% diisopropylethylamine (in dimethylformamide). Peptides were subjected to amino acid analysis in order to verify the
amino acid composition of peptide and to determine amount of peptide on
carrier. The sulfhydryl groups of CP peptide were determined by using a
reaction with 5,5'-dithiobis(2-nitrobenzoic acid) (DTNB)
(37). An appropriate amount of TentaGel with CP peptide was
incubated with 1 mM DTNB in 0.1 M phosphate buffer (pH 7.27) for 1 h with shaking. The absorption was read at 412 nm (
412 = 13,700 M
1 cm
1) after the completed reaction.
Strains, plasmids, general procedures, and media.
E.
coli TG1 (supE hsd
5 thi
[lac-proAB]
F'[traD36 proAB+ lacIq
lacZ
M15]) was used to host and multiply recombinant
plasmids. The lamB mutant E. coli strain pop6510
(supE thr leu tonB thi lacY1 recA dex5 metA) was used as a
recipient of all expression vectors bearing LamB variants. The R type
of lipopolysaccharide (LPS) of this strain was determined by silver
staining (21). E. coli LE392 (supE supF58
hsdR514 galK2 galT22 metB1 trpR55 lacY1) was used to propagate
phages. Lambda phages
h+ (wild type),
h0
(single mutant), and
hh* (double mutant) have been described elsewhere (6, 12). The vector pLBB9 used for the expression of LamB variants has been described previously (9). pLBB9 is a derivative of pSC101-based, chloramphenicol (Cm)-resistant vector pVDL8 carrying a promoterless lamB-153 gene that is
expressed through the Plac promoter of the vector.
Insertions between the positions 153 and 154 of the amino acid sequence
of LamB protein have been constructed via a unique BamHI
site of the plasmid. Recombinant DNA techniques were carried out
according to a standard protocol (38). The orientation of
the insertions was verified by restriction analysis, and positive
clones were subjected to DNA sequencing.
Minimal MJS medium (12.5 mM HEPES, pH 7.1; 50 mM NaCl; 20 mM
NH4Cl; 1 mM KCl; 1 mM MgCl2; 0.1 mM
CaCl2; 0.05 mM MnCl2; 0.8% Casamino Acids;
0.4% glycerol; 0.005% thiamine) and complete Luria-Bertani (LB)
medium were supplemented with 30 µg of Cm per ml and 10 or 100 µM
IPTG (isopropyl-
-D-thiogalactopyranoside) when required.
Construction and expression of hybrid LamB proteins.
Two
complementary pairs of oligonucleotides encoding peptide insertions to
lamB-153 were designed. Both pairs were flanked at 5' and 3'
ends by BamHI and BglII cohesive termini,
respectively. Such a design allows specific insertions into a unique
BamHI site of the lamB-153 gene which
reconstitute only one BamHI site (at the 5' end) and allows
successive insertions of another DNA fragment in tandem. The
5'-GATCCAGCTGGTCATCATCCACACGGTGCT-3' (plus strand) encodes
the N-Ala-Gly-His-His-Pro-His-Gly-Ala-C sequence, which has been named
HP. The 5'-GATCCAGCAGGCTGCGGTTGTCCATGCGGTTGTGGCGCT-3' (plus
strand) encodes the N-Ala-Gly-Cys-Gly-Cys-Pro-Cys-Gly-Cys-Gly-Ala-C sequence, which has been named CP. By using this approach, DNA fragments encoding HP peptide and CP peptide were inserted into lamB-153 of the vector pLBB9, resulting in
lamB-HP (plasmid pLBHP) and lamB-CP (plasmid
pLBCP), respectively. Subsequently, the next DNA fragments encoding HP
peptide and CP peptide were inserted into lamB-HP, resulting
in lamB-HP2 (plasmid pLBHP2) and lamB-HPCP (plasmid pLBHPCP), respectively (see Fig. 2a).
Expression of LamB derivatives (those with a genetic insertion of a
metal binding site are further called LamB-MBS) was performed in MJS or
LB media supplemented with 30 µg of Cm per ml and 100 µM IPTG.
Sensitivity of E. coli to
phage variants.
High-titer phage lysates were prepared by infection and lysis of the
permissive strain E. coli LE392 as reported elsewhere (40, 42). Approximately 100 µl of lysate (titer of
~1010 PFU/ml) was streaked in a line across the surface
of LB agar plates (supplemented with 5 mM [each] CaCl2
and MgSO4, 30 µg of Cm per ml, and 10 µM IPTG) and
allowed to dry. E. coli pop6510 bearing each of the plasmids
encoding LamB variants was then streaked perpendicular to and across
the phage line in a single swatch. The sensitivity was evaluated after
overnight incubation at 37°C.
Preparation of E. coli envelopes.
The method for
the preparation of cell envelopes of E. coli for metal
binding studies has been described elsewhere (2). Briefly,
E. coli pop6510 expressing LamB or LamB-MBSs was harvested from 500 ml of LB media supplemented with 30 µg of Cm per ml and 100 µM IPTG. The pellet was resuspended in 3 ml of 50 mM HEPES (pH 7.2),
and the cells were disintegrated by using X-press (LKB, Stockholm,
Sweden). Unbroken cells were removed by low-speed centrifugation (1,500 × g for 10 min at 4°C). Supernatant
(disrupted cells) was incubated with RNase (100 µg/ml) and DNase (50 µg/ml) in the presence of MgCl2 (5 mM). Envelopes were
separated at 48,000 × g for 30 min at 4°C, washed
five times with 6 ml of ice-cold demineralized water, and then
freeze-dried.
We also used Percoll gradient separation as described before
(33) for the small-scale preparation of OM and inner
membrane (IM) fractions in order to determine the localization of
LamB-MBS proteins.
Protein techniques.
Whole-cell extracts and/or equivalent
portions of cell envelopes, membrane preparations, or cytoplasmic
fractions were examined by electrophoresis in a denaturing
polyacrylamide gel. Proteins were alternatively electroblotted on
nitrocellulose membranes blocked with 10% skim milk in TBS (20 mM
Tris-Cl, pH 7.4; 250 mM NaCl; 3 mM KCl) for 1 h. Anti-LamB serum
(a kind gift of M. Hofnung) preadsorbed with cell extract of E. coli pop6510 was applied at a 1:2,000 dilution in TBST (TBS with
0.1% Tween 20) with 2% skim milk for 2 h. Membranes were washed
with TBST and incubated with goat anti-rabbit antibody conjugated with
alkaline phosphatase added at a 1:5,000 dilution in TBST with 2% skim
milk. Membranes were washed with TBST, and LamB variants were
visualized by using 5-bromo-4-chloro-3-indolyl phosphate as a substrate
along with nitroblue tetrazolium.
Metal binding studies.
Cd2+-to-HP and
Cd2+-to-CP stoichiometry was determined by using synthetic
peptides immobilized on TentaGel resin. Approximately 1.2 (for HP) or
0.6 (for CP) µmol of peptides was incubated at room temperature for
4 h with shaking in 1 ml of 0.1 to 5 mM CdCl2 in 50 mM
Tris-Cl (pH 7.4). The constant level of ionic strength was maintained
by the addition of the background electrolyte (0.2 M KNO3)
into the reaction mixture in order to support saturation of HP peptide
at the lower Cd2+ concentrations. Beads were then
sedimented by gravity, and the metal concentration was determined by
atomic absorption spectrometry (Varian Spectra A300).
Next, 3 mg (dry weight) of envelopes was incubated at room temperature
for 30 min in 3 ml of 5 mM CdCl2 in 25 mM HEPES (pH 7.0) in
order to determine the extent of Cd2+ binding by E. coli envelopes containing LamB-MBSs. Envelopes were pelleted at
40,000 × g for 30 min at 4°C and then washed five
times with 3 ml of ice-cold 25 mM HEPES (pH 7.0). Envelopes were then
mineralized with 70% nitric acid overnight under atmospheric pressure
at room temperature. The mineralized product was then diluted with
dimineralized water, and precipitated proteins were removed by
centrifugation. The metal concentration was determined by atomic
absorption spectrometry.
Bioaccumulation of metals (Cd2+, Cu2+, and
Zn2+) was measured in cells growing in MJS medium with Cm.
The low-phosphate MJS medium (employed in order to avoid the
precipitation of heavy metals) was supplemented with the heavy metal of
interest at a nontoxic concentration. The metal chlorides were used in
order to prefer biosorption of metal on the cell surface to its
intracellular uptake (18). We did not detect any
precipitation of heavy metals in the media or any measurable sorption
of metals on the glassware surface under these conditions. The cells
were induced with IPTG (100 µM) at an optical density at 590 nm
(OD590) corresponding to 0.3. The metal chloride(s) added
up to a total concentration of 30 µM (i.e., either a 30 µM
concentration of a single metal or a 15 µM concentration of each
metal in a double-metal assay) at an OD590 of 0.4. The
cultures were grown for another 3.5 h. Prior to the determination
of the metal content, the cells were pelleted, washed twice with 0.85%
NaCl in 5 mM HEPES (pH 7.1), and then mineralized overnight with 70%
nitric acid. Mineralized cells were further treated as described above.
Alternatively, washed cells were incubated for 15 min with an excess
volume of ice-cold 5 mM EDTA in 0.85% NaCl (pH 7.1) in order to remove
the surface-bound metal. The cells were then pelleted and treated as
described above.
 |
RESULTS |
Stoichiometry of Cd2+ binding to synthetic
peptides.
Two peptides predicted to be candidates for the
engineering of bacterial surface for enhanced heavy metal binding were
synthesized. The amino acid sequences were Gly-His-His-Pro-His-Gly
(i.e., HP) and Gly-Cys-Gly-Cys-Pro-Cys-Gly-Cys-Gly (i.e., CP). The
correct amino acid composition and the amount of peptide bound on
TentaGel resin were evaluated by amino acid analysis after total
peptide hydrolysis. The sulfhydryl content of CP peptide was also
determined. These analyses confirmed that peptides were synthesized as
correct full-length sequences. The amounts of peptide were found to be 138 and 118 nmol per mg of carrier for HP and CP peptide, respectively. The yield represented approximately 50% of the theoretical yield.
The Cd2+-to-peptide stoichiometry was determined from the
plot of the initial metal concentration against the molar ratio of bound cadmium to peptide (Fig. 1). The
resulting Cd2+-to-HP peptide stoichiometry of 1:1 indicated
the presence of a single metal binding site. On the other hand, CP
peptide was found to bind three equivalents of Cd2+. These
data suggested that both HP and CP peptides provide potent MBSs.

View larger version (12K):
[in this window]
[in a new window]
|
FIG. 1.
The Cd2+-to-peptide stoichiometry expressed
as the plot of initial Cd2+ concentration against the
complexed Cd2+-to-peptide molar ratio. A total of 0.6 µmol of CP peptide (squares) and/or 1.2 µmol of HP peptide
(circles) were incubated on TentaGel resin in 1 ml of Cd2+
containing 50 mM Tris-Cl (pH 7.4). In the case of HP peptide metal
binding studies, 0.2 M KNO3 was added as a background
electrolyte. The portion of unbound Cd2+ was determined by
atomic absorption spectrometry.
|
|
Expression of LamB hybrid proteins.
DNA fragments encoding
predicted MBSs were engineered into the lamB-153 gene at a
permissive position equivalent to the protein loop exposed on the cell
surface (Fig. 2a). Corresponding
expression vectors carrying the chimeric gene lamB-mbs were
named pLBHP (one HP sequence), pLBHP2 (two HP sequences), pLBCP (one CP
sequence), and pLBHPCP (a combination of HP and CP sequences).

View larger version (27K):
[in this window]
[in a new window]
|
FIG. 2.
(a) Organization of the lamB-mbs gene within
the pLBB9 expression vector (a derivative of the low-copy-number vector
pVDL8 bearing lamB-153 gene expressed throughout the
lac promoter). The orientation of the promoter is marked by
an arrow. The ribosome binding site (SD), the initiation codon (ATG),
and the stop codon (TAA) of lamB-153 are indicated. The
plasmids relevant to the specific genetic insertions of mbs
indicated are listed on the left. For the amino acid compositions of
the MBSs see Table 1. (b) Expression of LamB-MBD in E. coli
pop6510. Crude extracts of approximately 2 × 108
cells of E. coli pop6510 expressing LamB variants were
resolved by sodium dodecyl sulfate-polyacrylamide gel electrophoresis,
probed with preadsorbed polyclonal rabbit anti-LamB serum, and
visualized with goat anti-rabbit antibody conjugated with alkaline
phosphatase. The arrow indicates the position of wild-type LamB
protein. The drawing shows the desired targeting of LamB-MBSs into the
OM of E. coli. The LamB protein consists of 18 transmembrane
domains, and the MBSs are introduced between transmembrane domains 7 and 8 of the protein.
|
|
The LamB-MBS proteins were expressed in lamB-defective
E. coli pop6510 as full-length products, with no signs of
proteolytic degradation, as demonstrated by immunoblot analysis of the
crude cell extracts with anti-LamB serum (Fig. 2b). The growth rate of
cells expressing LamB-MBS was not altered compared to cells expressing
LamB during the exponential phase. However, a slight depression of the
biomass yield (about 20%) was observed with cells expressing LamB-CP
and LamB-HPCP.
Localization of LamB-MBS and functional tolerance of LamB to
specific insertions of HP and CP sequences.
To address the issue
of the effect of insertion of HP and CP sequences and/or their
combination on the targeting of LamB-MBS into outer membrane, we
fractionated envelopes of E. coli pop6510 expressing
LamB-MBS. We noted a sharp, white, high-density band resulting from
Percoll gradient centrifugation of the disintegrated cells
corresponding to the OM of E. coli (33) (Fig.
3a). A band close to the top of the
gradient as a fraction consisting of the IM was also separated out. The
majority of the LamB-MBS proteins were present in the fraction
corresponding to the OM of E. coli, i.e., at the site of its
natural destination (Fig. 3 shows LamB-HP2 as an example).

View larger version (47K):
[in this window]
[in a new window]
|
FIG. 3.
Localization of LamB-HP2 protein in E. coli.
(a) Sodium dodecyl sulfate-polyacrylamide gel electrophoresis of the OM
and the IM fractions resulting from Percoll gradient centrifugation.
Proteins of resolved membrane vesicles of approximately 5 × 109 cells were precipitated with acetone and run in a 12%
denaturing polyacrylamide gel. Asterisks indicate the major OM proteins
identified on a molecular-size basis (LamB-HP2, 48.8 kDa; OmpC, 38.2 kDa; OmpF, 37.0 kDa; OmpA, 35.1 kDa). (b) Immunochemical detection of
LamB-HP2 in the same membrane fractions. CYT, aliquot portion of
cytoplasm resulting from high-speed centrifugation of disrupted
cells.
|
|
The sensitivity of E. coli pop6510 expressing LamB-MBS to
lambda phages
h+ (wild type),
h0, and
hh* was determined in order to evaluate the effect of specific insertions (MBSs) on the folding of the LamB protein. No changes of the
sensitivity to lambda phages were detected in the chimeric LamB.
Metal binding properties of isolated envelopes containing
LamB-MBSs.
Cell envelopes were prepared by a method described
elsewhere (2). The presence of the LamB-MBSs was determined
by immunoblot analysis. No significant differences in LamB-MBS content
were observed among all of the preparations (data not shown). We did not detect any contamination of the envelopes with nucleic acids. The
reaction of the envelopes with Cd2+ was performed as
described in Materials and Methods in an arrangement similar to that
described elsewhere (2, 23, 24), but the pH was set to 7.0. This value remained unchanged during the reaction. As shown in Table
1, E. coli envelopes
containing any of the LamB-MBSs bound significantly higher amounts of
Cd2+ than did those of cells expressing "wild-type"
LamB protein. The best metal binding capacity showed envelopes
containing LamB-HP2 and/or LamB-CP, which exceeded the natural ability
of E. coli cell envelopes to bind Cd2+ by
1.8-fold.
View this table:
[in this window]
[in a new window]
|
TABLE 1.
The amount of Cd2+ bound by envelopes of
E. coli pop6510 expressing LamB-MBSs and a portion of
Cd2+ removed from the surface by
EDTA treatmenta
|
|
Metal binding properties of E. coli displaying
LamB-MBS.
The increased Cd2+ binding capacity of the
manipulated cell wall of E. coli led us to evaluate the
influence of specific genetic insertions on metal binding by viable
E. coli cells. The accumulation of bivalent metal ions in
the "single metal" (Cd2+, Cu2+, or
Zn2+) system was compared to that of the cells expressing
wild-type LamB protein.
As shown in Fig. 4, cells displaying
LamB-MBSs accumulated Cd2+ with an efficiency higher than
that of the other tested metals. Insertion of MBSs containing both
histidines (HP) and cysteines (CP) into the LamB protein led to the
increase of the amount of accumulated Cd2+ from media
supplemented with 30 µM Cd2+. A more than twofold
increase (2.2 ± 0.3) of Cd2+ bioaccumulation was
observed with LamB-HP. Duplication of the HP sequence (LamB-HP2) led to
the additional increase (3.1 ± 1.0 times) of the amount of
accumulated Cd2+. A nearly fourfold increase (3.8 ± 0.8) of the Cd2+ bioaccumulation occurred in the cells
expressing LamB-CP. However, there was no additive effect of the
combination of HP and CP sequences (LamB-HPCP) on the total amount of
accumulated Cd2+ (Fig. 4). A similar pattern was found for
the accumulation of Cd2+ from medium supplemented with 15 µM Cd2+ (Fig. 5). A slight
increase in the Cd2+ bioaccumulation by uninduced cells was
observed (Fig. 4). This was due to leaking expression of LamB-MBS as
detected by immunoblot.

View larger version (29K):
[in this window]
[in a new window]
|
FIG. 4.
Bioaccumulation of heavy metal ions by E. coli pop6510 expressing LamB-MBSs in a single-metal system.
E. coli transformed with plasmids carying specific
insertions in lamB-153 (see Table 1) or the control plasmid
pLBB9 was grown in MJS medium and induced at OD590 = 0.3 with IPTG except for the control uninduced cells (open bars). Cells
were further grown until OD590 = 0.4, and then a 30 µM
concentration of CdCl2, CuCl2, or
ZnCl2 was added. The metal content was determined by atomic
absorption spectrometry after an additional 3.5 h of cultivation.
The bars represent the mean value of three to five independent
experiments.
|
|

View larger version (26K):
[in this window]
[in a new window]
|
FIG. 5.
Bioaccumulation of heavy metal ions by E. coli pop6510 expressing LamB-MBSs in the double metal system.
E. coli transformed with plasmids carrying specific
insertions in lamB-153 (see Table 1) or the control plasmid
pLBB9 was grown in MJS medium and induced at OD590 = 0.3 with IPTG. Cells were than grown until OD590 = 0.4 and
supplemented with 15 µM CdCl2 and/or equimolar mixtures
(15 µM concentrations of each metal ion) of either CdCl2
and CuCl2 (a) or CdCl2 and ZnCl2
(b). Their metal content was determined by atomic absorption
spectrometry after an additional 3.5 h of cultivation. The second
metal of the mixture is indicated in brackets. The bars represent mean
value of three independent experiments.
|
|
E. coli cells preadsorbed with Cd2+ were
incubated in excess of EDTA (see Materials and Methods) in order to
evaluate the portion of Cd2+ bound to the surface
structures. Such treatment, which may also cause a partial release of
LPSs (31), resulted in removal of 50 to 60% of the total
Cd2+ accumulated by cells expressing LamB-MBSs (Table 1).
The surface display of the histidine-based MBS (LamB-HP and LamB-HP2)
did not enhance the bioaccumulation of both Cu2+ and
Zn2+ in contrast to the accumulation of Cd2+. A
slightly increased bioaccumulation of Cu2+ and
Zn2+ was observed with cells expressing LamB-CP and
LamB-HPCP. However, this increase was less than twice that of the control.
The absence of a contribution from the HP sequence for the
Cu2+ binding was quite unexpected since the imidazolium
group has been described as a ligand with a relatively high affinity
for Cu2+ in biological systems (26). The
competition of Cd2+ with Cu2+ or
Zn2+ for LamB-MBSs in vivo was evaluated in order to
elucidate this phenomenon. As shown in Fig. 5a, the amount of
Cd2+ accumulated by cells expressing LamB-HP and LamB-HP2
from media containing an equimolar mixture of Cd2+ and
Cu2+ (15 µM each) dropped to the level accumulated by
control cells expressing wild-type LamB. The presence of
Zn2+ (15 µM) caused less than a 10% decrease of
bioaccumulation of Cd2+ by cells displaying HP sequences
compared to the same cells grown in the presence of a single 15 µM
Cd2+ (Fig. 5b). The cells expressing LamB-CP and LamB-HPCP
accumulated a greater amount of heavy metals than the control from
equimolar mixtures of both Cd2+ and Cu2+ or
both Cd2+ and Zn2+ (Fig. 5). However, the
decrease in the amount of Cd2+ accumulated due to the
presence of Cu2+ in the medium was significant (Fig. 5a).
An apparently lower effect of Zn2+ on Cd2+
accumulation was observed with cells displaying the CP sequence (Fig.
5b).
 |
DISCUSSION |
The introduction of additional peptides serving as heavy metal
ligands on the microbial surface represents one possible way for
improving the metal binding properties of the biomass in terms of
capacity, kinetics, and selectivity. The metal binding ability of the
E. coli cell wall has been studied in detail previously (2, 16, 23, 24). The specific native groups of the OM participating in metal binding are the polar head groups of
phospholipids acting mainly at the inner layer of the OM and the acidic
groups of the exposed (hydrophilic) polypeptides and at the outer half of the OM LPSs. The LPSs provide both carboxyl and phosphoryl groups as
ligands. However, only the latter group is responsible for the high
affinity of divalent metal ions for LPS (16). The peptidoglycan (PG) layer of E. coli, which is most probably
one molecule thick, binds metal ions via the carboxyl group of the D-glutamic acid of the peptide stem and the hydroxyl groups
of the glycan backbone (23). The two-step deposition process
may increase the apparent metal binding capacity of PG (3,
23) and would include the stoichiometric binding of metal ion,
generating a nucleation site for the subsequent precipitation of metal
above the stoichiometric amounts.
The OM LamB protein of E. coli has been reported to tolerate
the genetic insertions of heterologous peptides at positions between
the structural codons 153 and 154 (5, 9, 11, 13, 22, 42, 43,
44). The genetic insertions of the HP and CP sequences into
lamB-153 resulted in LamB-MBS hybrid proteins located in the
OM. Furthermore, the LamB-MBSs retained their biological function as a
lambda phage port, indicating a maintenance of their overall folding
pattern. The Cd2+-to-peptide stoichiometry determined for
synthetic HP and CP peptides is less than one metal ion per amino acid
residue possessing metal binding properties (Fig. 1). This suggests
specific folding of the sequence around the metal ion(s). The geometry
of the MBSs of both HP and CP peptides is currently under study.
The increase of the metal binding capacity of the E. coli
envelopes was significant (Table 1). Thus, the introduction of metal
binding peptides onto the surface of the microorganism to be used as
nonliving material for bioremediation may improve the process. It could
be hypothesized that such an approach will improve not only the metal
binding capacity of the biosorbent but also the kinetics of the
process. An appropriate carrier for the surface display could be the
only limiting factor. The C-terminal part of
-agglutinin could be
such a carrier in yeast cells (39), which are being
considered for use in the bioremediation of heavy metal ions
(25).
We used E. coli as a model to evaluate changes of the metal
binding properties due to surface display of the metal binding peptides. Surface display of HP and CP sequences resulted in a significant increase in Cd2+ bioaccumulation by growing
E. coli (Fig. 4 and 5). The number of Cd2+
binding sites generated by surface display of polyhistidine or metallothionein did not fully account for the amount of accumulated Cd2+, as has been previously proposed (41, 42).
The amount of LamB used in the expression system ranged from 1,000 to
5,000 molecules of protein per cell. This value is 2 to 3 orders of magnitude lower than the increment in Cd2+ accumulation due
to the insertion of the MBS. It has been suggested that displayed
peptides favor the interaction of Cd2+ with other bacterial
structures by increasing the local concentration of metal ions
(41, 42). The cell wall components involved could be, for
example, LPSs (E. coli pop6510 possesses the R type of LPS),
which are known as compounds that directly interact with the LamB
protein (36) and provide sufficiently effective metal ligands (16). The data on desorption-bound Cd2+
by EDTA treatment suggest that more than one-half of the metal is
located on the surface.
A different situation has been observed for Cu2+ and
Zn2+ bioaccumulation. While E. coli displaying
CP peptide (as LamB-CP or LamB-HPCP) accumulated both Cu2+
and Zn2+ in apparently higher amounts than did the control
cells expressing LamB protein, the surface display of HP did not
promote any increase of bioaccumulation of these two metals (Fig. 4).
The apparent lack of contribution of the HP sequence was unexpected
because histidine residues possess a higher affinity to
Cu2+ than to Cd2+ (26, 34) and
because the HP sequence by itself has been shown to be an effective
ligand for both Cu2+ and Zn2+ (27).
We also did not detect any contribution of HP display to the enhanced
bioaccumulation of Ni2+ and Co2+ (unpublished
observations). Moreover, the presence of Cu2+ in the medium
resulted in the inhibition of Cd2+ binding by cells
displaying HP peptide. This finding confirms the strong binding of
Cu2+ to the HP sequence in vivo. However, no increase of
the Cu2+ accumulation by corresponding cells was observed.
In adopting a model explaining the disproportions between the number of
MBSs and the amount of accumulated Cd2+ (41,
42), it should be considered that such a figure could be due to
the lower affinity of bacterial surface components other than that of
HP to Cu2+. The lack of increase in bioaccumulation of
Zn2+ by cells displaying HP sequences can be explained by
the low relative affinity of cell wall components for Zn2+,
which is otherwise bound to HP sequence less avidly than
Cd2+ (Fig. 5b). Since the affinity of Zn2+ to
HRG is higher than that of Cd2+ (33), the
absence of any significant effect of Zn2+ on the
bioaccumulation of Cd2+ due to HP display is quite
interesting. It could indicate a different conformation of the HP
sequence fused to LamB from that in HRG or the participation of other
amino acid residues in the formation of the metal (Zn2+)
binding site of HRG.
E. coli displaying the CP peptide (either as LamB-CP or
LamB-HPCP) exhibited an accumulation of both Cd2+ and its
counterpart in the equimolar mixture (Cu2+ or
Zn2+) higher than that of the control cells. The results
shown in Fig. 5 are in agreement with the relative affinities of tested metals to imidazolium and sulfhydryl groups (26).
The LamB protein is a very attractive "broad-range" vehicle that
could be efficiently expressed in various gram-negative species (9, 14, 43, 44). The engineering of metal binding peptides on the surface of environmentally acceptable gram-negative bacteria such as Ralstonia eutropha and Pseudomonas
putida, which are already employed in existing systems for heavy
metal bioremediation (15, 30), represents a possible
application. For instance, the metal binding peptides introduced on the
surface of R. eutropha may aid in the process of
precipitation and crystallization of metal carbonates.
The search for novel peptide sequences with attention paid to their
selectivity for specific metal ions is under study in our laboratory.
Several designs for artificial heavy metal binding sites have been
previously reported in the literature. The synthetic peptide
Boc-Cys-Pro-Leu-Cys-OMe, designed as a model for Cys-containing metal
binding sites, has been shown to bind Hg2+,
Zn2+, and Cd2+ via both Cys residues
(48). The Zn2+ binding via His and Glu residues
was described for a model peptide mimicking the metal binding site of
the ribonucleotide reductase (49). Haymore et al.
(20) identified several short chelating sequences containing
His, Cys, and Asp residues which could form energetically stable
chelating sites with specific metal ions. Amino acid sequences forming
a stable coordination sphere around transition metals were also
identified by using a combinatorial peptide library approach
(4). However, the data shown in Fig. 4 and 5 indicate that
not only would the affinity of a peptide or its selectivity determine
the bioaccumulation of a particular metal ion but that the
"reactivity" of the cell wall (and cell compartments) would also
have to be taken into account.
 |
ACKNOWLEDGMENTS |
We are particularly indebted to M. Hofnung (Institut Pasteur,
Paris, France) for the gift of various strains and for the anti-LamB serum.
This work was funded by grants of the Grant Agency of Czech Republic
(203/98/0650), grant VS 96074 of the Ministry of Education of Czech
Republic, and grants ENV4-CT95-0141 and BIO4-CT97-2183.
 |
FOOTNOTES |
*
Corresponding author. Mailing address: Department of
Biochemistry and Microbiology, Institute of Chemical Technology,
Technická 3, 166 28 Prague, Czech Republic. Phone: (420)
2-24353022. Fax: (420) 2-3119990. E-mail:
TOMAS.RUML{at}VSCHT.CZ.
 |
REFERENCES |
| 1.
|
Bertini, I.,
F. Briganti, and A. Scozzafava.
1995.
Specific factors in metal ion-macromolecular ligand interactions, p. 81-92.
In
G. Berthon (ed.), Handbook of metal-ligand interactions in biological fluids, vol. 1. Marcel Dekker, New York, N.Y.
|
| 2.
|
Beveridge, T. J., and S. F. Koval.
1981.
Binding of metals to cell envelopes of Escherichia coli K-12.
Appl. Environ. Microbiol.
42:325-335[Abstract/Free Full Text].
|
| 3.
|
Beveridge, T. J., and R. G. E. Murray.
1976.
Uptake and retention of metals by cell walls of Bacillus subtilis.
J. Bacteriol.
127:1502-1518[Abstract/Free Full Text].
|
| 4.
|
Bianchi, E.,
A. Folgory,
A. Wallace,
M. Nicotra,
S. Acali,
A. Phalipon,
G. Barbato,
R. Bazzo,
R. Cortese,
F. Felici, and A. Pessi.
1995.
A conformationally homogeneous combinatorial peptide library.
J. Mol. Biol.
247:154-160[Medline].
|
| 5.
|
Boulain, J.,
A. Charbit, and M. Hofnung.
1986.
Mutagenesis by random linker insertion into lamB gene of Escherichia coli K12.
Mol. Gen. Genet.
205:339-348[Medline].
|
| 6.
|
Braun-Brenton, C., and M. Hofnung.
1986.
In vivo and in vitro functional alterations of the bacteriophage lambda receptor in lamB missense mutants of Escherichia coli K-12.
J. Bacteriol.
148:845-852.
|
| 7.
|
Brown, S.
1997.
Metal-recognition by repeating polypeptides.
Nat. Biotechnol.
15:269-272[Medline].
|
| 8.
|
Brown, S.
1992.
Engineered iron oxide-adhesion mutants of Escherichia coli phage lambda receptor.
Proc. Natl. Acad. Sci. USA
89:8651-8655[Abstract/Free Full Text].
|
| 9.
|
Cebolla, Á.,
C. Guzmán, and V. de Lorenzo.
1996.
Nondisruptive detection of catabolic promoters of Pseudomonas putida with an antigenic surface reporter system.
Appl. Environ. Microbiol.
62:214-220[Abstract].
|
| 10.
|
Chaney, R. L.,
M. Malik,
Y. L. Li,
S. L. Brown,
E. P. Brewer,
J. S. Angle, and A. J. M. Baker.
1997.
Phytoremediation of soil metals.
Curr. Opin. Biotechnol.
8:279-284[Medline].
|
| 11.
|
Charbit, A.,
J. C. Boulain,
A. Ryter, and M. Hofnung.
1996.
Probing the topology of a bacterial membrane protein by genetic insertion of a foreign epitope: expression at the cell surface.
EMBO J.
5:3029-3037[Medline].
|
| 12.
|
Charbit, A., and M. Hofnung.
1985.
Isolation of different bacteriophages using the LamB protein for adsorption on Escherichia coli K-12.
J. Virol.
53:667-671[Abstract/Free Full Text].
|
| 13.
|
Charbit, A.,
A. Molla,
W. Saurin, and M. Hofnung.
1988.
Versatility of a vector for expression foreign polypeptides at the surface of Gram-negative bacteria.
Gene
70:181-189[Medline].
|
| 14.
|
de Vries, G. E.,
C. K. Raymond, and R. A. Ludwig.
1984.
Extension of bacteriophage host range: selection, cloning, and characterization of a constitutive receptor gene.
Proc. Natl. Acad. Sci. USA
81:6080-6084[Abstract/Free Full Text].
|
| 15.
|
Diels, L.,
S. Van Roy,
M. Mergeay,
W. Doyen,
S. Taghavi, and R. Leysen.
1993.
Immobilization of bacteria in composite membranes and development of tubular membrane reactors for heavy metal recuperation, p. 275-293.
In
R. Peterson (ed.), Effective membrane processes: new perspectives. Kluwer Academic Publishers, Dordrecht, The Netherlands.
|
| 16.
|
Ferris, F. G., and T. J. Beveridge.
1985.
Site specifity of metallic ion binding in Escherichia coli K-12 lipopolysacharide.
Can. J. Microbiol.
32:52-55.
|
| 17.
|
Gadd, G. M.
1992.
Microbial control of heavy metal pollution, p. 59-87.
In
J. C. Fry, G. M. Gadd, R. A. Herbert, C. W. Jones, and I. A. Watson-Craik (ed.), Microbial control of pollution. Cambridge University Press, Cambridge, United Kingdom.
|
| 18.
|
Gelmi, M.,
P. Apostoli,
E. Cabibbo,
S. Porru,
L. Alassio, and A. Turano.
1994.
Resistance to cadmium salts and metal absorption by different microbial species.
Curr. Microbiol.
29:335-341.
|
| 19.
|
Georgiou, G.,
H. L. Poetschke,
C. Stathopoulos, and J. A. Francisco.
1993.
Practical applications of engineering Gram-negative bacterial cell surfaces.
Trends Biotechnol.
11:6-10[Medline].
|
| 20.
|
Haymore, B. L.,
G. S. Bild,
W. J. Salsgiver,
N. R. Staten, and G. G. Krivi.
1992.
Introducing strong metal-binding sites onto surfaces of proteins for facile and efficient metal-affinity purification.
Methods (Companion Methods Enzymol.)
4:25-40.
|
| 21.
|
Hitchcock, P. J., and T. M. Brown.
1983.
Morphological heterogeneity among Salmonella lipopolysacharide chemotypes in silver-stained polyacrylamide gels.
J. Bacteriol.
154:269-277[Abstract/Free Full Text].
|
| 22.
|
Hofnung, M.
1991.
Expression of foreign polypeptides at the Escherichia coli cell surface.
Methods Cell Biol.
4:77-105.
|
| 23.
|
Hoyle, B. D., and T. J. Beveridge.
1984.
Metal binding by the peptidoglycan sacculus of Escherichia coli K-12.
Can. J. Microbiol.
30:204-211[Medline].
|
| 24.
|
Hoyle, B. D., and T. J. Beveridge.
1983.
Binding of metallic ions to the outer membrane of Escherichia coli.
Appl. Environ. Microbiol.
46:749-752[Abstract/Free Full Text].
|
| 25.
|
Huang, C. P.,
D. Westman,
K. Quirk, and J. P. Huang.
1988.
The removal of cadmium (II) from dilute aqueous solutions by fungal absorbent.
Water Sci. Technol.
20:369-376.
|
| 26.
|
Huber, A. L.,
B. E. Holbein, and D. K. Kidby.
1990.
Metal uptake by synthetic and biosynthetic chemicals, p. 249-291.
In
B. Volesky (ed.), Biosorption of heavy metals. CRC Press, Boca Raton, Fla.
|
| 27.
|
Hutchens, T. W., and T.-T. Yip.
1992.
Synthetic metal-binding protein surface domains for metal ion-dependent interaction chromatography.
J. Chromatogr.
604:133-141[Medline].
|
| 28.
|
Koide, T.,
D. Foster,
S. Uoshitake, and E. W. Davie.
1986.
Amino acid sequence of human histidine-rich glycoprotein derived from the nucleotide sequence of its cDNA.
Biochemistry
25:2220-2225[Medline].
|
| 29.
|
Kotrba, P.,
L. Dole ková,
M. Pavlík, and T. Ruml.
1996.
Rapid screening of peptides for heavy metal binding.
Biotechnol. Technol.
10:773-778.
|
| 30.
|
Macaskie, L. E., and A. C. R. Dean.
1990.
Metal sequestering biochemicals, p. 200-248.
In
B. Volesky (ed.), Biosorption of heavy metals. CRC Press, Boca Raton, Fla.
|
| 31.
|
Macaskie, L. E.,
A. C. R. Dean,
A. K. Cheetham,
R. J. B. Jakeman, and A. J. Skarnulis.
1987.
Cadmium accumulation by Citrobacter sp.: the chemical nature of the accumulated metal precipitate and its location on the bacterial cells.
J. Gen. Microbiol.
133:539-544.
|
| 32.
|
Marvin, H. J. P.,
M. B. A. Ter Beest, and B. Wittholt.
1989.
Release of outer membrane fragments from wild-type Escherichia coli and from several E. coli lipopolysacharide mutants by EDTA and heat shock treatments.
J. Bacteriol.
171:5262-5267[Abstract/Free Full Text].
|
| 33.
|
Morein, S.,
D. Henricson, and L. Rifors.
1994.
Separation of inner and outer membrane vesicles from Escherichia coli in self-generating Percoll gradients.
Anal. Biochem.
216:47-51[Medline].
|
| 34.
|
Morgan, W. T.
1984.
The histidine-rich glycoprotein of serum has a domain rich in histidine, proline, and glycine that binds heme and metals.
Biochemistry
24:1496-1501.
|
| 35.
|
Nriagu, J. O., and J. M. Pacyna.
1989.
Quantitative assesment of worldwide contamination of air, water and soils by trace metals.
Nature
333:134-139.
|
| 36.
|
Randall, L. L.
1975.
Quantitation of the loss of the bacteriophage lambda receptor protein from the outer membrane of lipopolysacharide-deficient strains of Escherichia coli.
J. Bacteriol.
123:41-46[Abstract/Free Full Text].
|
| 37.
|
Riddles, P. W.,
R. L. Blakeley, and B. Zerner.
1983.
Reassessment of Ellman's reagent.
Methods Enzymol.
91:49-60[Medline].
|
| 38.
|
Sambrook, J.,
E. F. Fritsch, and T. Maniatis.
1989.
Molecular cloning: a laboratory manual, 2nd ed.
Cold Spring Harbor Laboratory Press, Cold Spring Harbor, N.Y.
|
| 39.
|
Schreuder, M. P.,
A. T. A. Mooren,
H. Y. Toschka,
C. T. Verrips, and F. M. Klis.
1996.
Immobilizing proteins on the surface of yeast cells.
Trends Biotechnol.
14:115-120[Medline].
|
| 40.
|
Silhavy, T. J.,
M. L. Berman, and L. W. Enquist.
1984.
Experiments with gene fusion.
Cold Spring Harbor Laboratory Press, Cold Spring Harbor, N.Y.
|
| 41.
|
Sousa, C.,
A. Cebola, and V. de Lorenzo.
1996.
Enhanced metallosorption of bacterial cells displaying poly-His peptides.
Nat. Biotechnol.
14:1017-1020[Medline].
|
| 42.
|
Sousa, C.,
P. Kotrba,
T. Ruml,
A. Cebola, and V. de Lorenzo.
1998.
Metallosorption by Escherichia coli cells displaying yeast and mammalian metallothioneins anchored to the outer membrane protein LamB.
J. Bacteriol.
180:2280-2284[Abstract/Free Full Text].
|
| 43.
|
Steidler, L.,
E. Remaut, and W. Fiers.
1993.
LamB as a carrier molecule for the functional exposition of IgG-binding domains of the Staphylococcus aureus protein A at the surface of Escherichia coli K12.
Mol. Gen. Genet.
236:187-192[Medline].
|
| 44.
|
Su, G. T.,
H. Brahmbhatt,
J. Wehland,
M. Rohde, and K. N. Timmis.
1992.
Construction of stable LamB-Shiga toxin B subunit hybrids: analysis of the expression in Salmonella typhymurium aroA strains and stimulation of B subunit-specific mucosal and serum antibody responses.
Infect. Immun.
60:3345-3359[Abstract/Free Full Text].
|
| 45.
|
Szmelcman, S., and M. Hofnung.
1975.
Maltose transport in Escherichia coli K-12: involvement of the bacteriophage lambda receptor.
J. Bacteriol.
124:112-118[Abstract/Free Full Text].
|
| 46.
|
Volesky, B., and Z. S. Holan.
1995.
Biosorption of heavy metals.
Biotechnol. Prog.
11:235-250[Medline].
|
| 47.
|
Watanabe, M. E.
1997.
Phytoremediation on the brink of commercialization.
Environ. Sci. Technol.
31:182-186.
|
| 48.
|
Yamamura, T., and T. Watanabe.
1993.
Conformation analyses of (Cys-Pro-Leu-Cys)Hg, [(Cys-Pro-Leu-Cys)(tBuS)Hg]- and [(Cys-Pro-Leu-Cys)Zn(OMe)2]: the model peptides for cysteine-containing metal binding sites of metallo enzymes, p. 281-283.
In
N. Yanaihara (ed.), Peptide chemistry. ESCOM, Leiden, The Netherlands.
|
| 49.
|
Yamamura, T.,
T. Sasaki, and M. Ueki.
1993.
Synthesis of the zinc complex of Boc-Glu-Thr-Ile-His-OMe: the model peptides for the metal binding sites of ribonucleotide reductase, p. 284-286.
In
N. Yanaihara (ed.), Peptide chemistry. ESCOM, Leiden, The Netherlands.
|
Applied and Environmental Microbiology, March 1999, p. 1092-1098, Vol. 65, No. 3
0099-2240/99/$04.00+0
Copyright © 1999, American Society for Microbiology. All rights reserved.
This article has been cited by other articles:
-
Qin, J., Song, L., Brim, H., Daly, M. J., Summers, A. O.
(2006). Hg(II) sequestration and protection by the MerR metal-binding domain (MBD).. Microbiology
152: 709-719
[Abstract]
[Full Text]
-
Yoshino, T., Takahashi, M., Takeyama, H., Okamura, Y., Kato, F., Matsunaga, T.
(2004). Assembly of G Protein-Coupled Receptors onto Nanosized Bacterial Magnetic Particles Using Mms16 as an Anchor Molecule. Appl. Environ. Microbiol.
70: 2880-2885
[Abstract]
[Full Text]
-
Ueki, T., Sakamoto, Y., Yamaguchi, N., Michibata, H.
(2003). Bioaccumulation of Copper Ions by Escherichia coli Expressing Vanabin Genes from the Vanadium-Rich Ascidian Ascidia sydneiensis samea. Appl. Environ. Microbiol.
69: 6442-6446
[Abstract]
[Full Text]
-
Kjaergaard, K., Hasman, H., Schembri, M. A., Klemm, P.
(2002). Antigen 43-Mediated Autotransporter Display, a Versatile Bacterial Cell Surface Presentation System. J. Bacteriol.
184: 4197-4204
[Abstract]
[Full Text]
-
Kjargaard, K., Schembri, M. A., Klemm, P.
(2001). Novel Zn2+-Chelating Peptides Selected from a Fimbria-Displayed Random Peptide Library. Appl. Environ. Microbiol.
67: 5467-5473
[Abstract]
[Full Text]
-
Wernerus, H., Lehtio, J., Teeri, T., Nygren, P.-A., Stahl, S.
(2001). Generation of Metal-Binding Staphylococci through Surface Display of Combinatorially Engineered Cellulose-Binding Domains. Appl. Environ. Microbiol.
67: 4678-4684
[Abstract]
[Full Text]
-
Samuelson, P., Wernérus, H., Svedberg, M., Ståhl, S.
(2000). Staphylococcal Surface Display of Metal-Binding Polyhistidyl Peptides. Appl. Environ. Microbiol.
66: 1243-1248
[Abstract]
[Full Text]
-
Kjærgaard, K., Sørensen, J. K., Schembri, M. A., Klemm, P.
(2000). Sequestration of Zinc Oxide by Fimbrial Designer Chelators. Appl. Environ. Microbiol.
66: 10-14
[Abstract]
[Full Text]