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Appl Environ Microbiol, April 1998, p. 1472-1476, Vol. 64, No. 4
0099-2240/98/$04.00+0
Copyright © 1998, American Society for Microbiology. All rights reserved.
Fluorescent Pseudomonad Pyoverdines Bind and
Oxidize Ferrous Ion
Rong
Xiao and
William S.
Kisaalita*
Biological and Agricultural Engineering
Department, Driftmier Engineering Center, University of Georgia,
Athens, Georgia 30602
Received 7 November 1996/Accepted 28 November 1997
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ABSTRACT |
Major pyoverdines from Pseudomonas fluorescens 2-79 (Pf-B), P. aeruginosa ATCC 15692 (Pa-C), and P. putida ATCC 12633 (Pp-C) were examined by absorption and
fluorescence spectroscopic techniques to investigate the interaction
between ferrous ion and the pyoverdine ligand. At physiological pH,
ferrous ion quenched the fluorescence of all three pyoverdines much
faster than ferric ion did. Also, increased absorbance at 460 nm was
observed to be much faster for Fe2+-pyoverdine than for
Fe3+-pyoverdine. At pH 7.4, about 90% of Fe3+
was bound by pyoverdine Pa-C after 24 h whereas Fe2+
was bound by the pyoverdine completely in only 5 min. The possibility that Fe2+ underwent rapid autoxidation before being bound
by pyoverdine was considered unlikely, since the Fe2+
concentration in pyoverdine-free samples remained constant over a 3-min
period at pH 7.4. Incubating excess Fe2+ with pyoverdine in
the presence of 8-hydroxyquinoline, an Fe3+-specific
chelating agent, resulted in the formation of a
Fe3+-hydroxyquinoline complex, suggesting that the iron in
the Fe2+-pyoverdine complex existed in the oxidized form.
These results strongly suggested that pyoverdines bind and oxidize the
ferrous ion.
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INTRODUCTION |
In the early history of the Earth,
the appearance of photosynthesis and an oxidizing atmosphere caused the
soluble ferrous ion to precipitate from solution (8). Due to
the critical need for iron in aerobic metabolism and its tendency to
form a highly insoluble ferric hydroxide, rendering it unavailable for
transport in the ionic form, microorganisms have evolved special
high-affinity systems for acquisition of the metal from the environment
(8, 20). One of the systems involves low-molecular-mass
secondary metabolites termed siderophores, which bind Fe3+
with a high affinity and are excreted, usually in large amounts, when
cells are grown under iron deficiency. Although this high-affinity iron
uptake may vary among different microbial types, in gram-negative bacteria the general process involves an iron-regulated outer membrane
protein which acts as a receptor that is able to recognize specifically
the Fe3+-siderophore complex (19).
Three possible mechanisms have been proposed to explain the removal of
iron from chelates with dissociation constants of the order
10
30: chelator hydrolysis (7), exchange with
another chelator (18), and Fe3+ reduction
(7, 21). Based on qualitative observations (color changes)
involving Fe2+-o-phenanthroline formation in a
mixture containing reduced Ustilago spaerogena siderophore,
Neilands (17) concluded that the ferrous iron is bound only
weakly, if at all, by siderophores and further pointed out that the
extreme difference in the affinity of siderophores for ferrous and
ferric ions offered a mechanism to remove Fe3+ from
siderophores. Subsequently, numerous laboratories have reported siderophore reductases in cell extracts of a variety of microorganisms (9-11). Similar reductase activities also have been found
in cell extracts of Pseudomonas fluorescens (12),
and P. aeruginosa (13).
The major exogenous siderophore of fluorescent pseudomonads is
pyoverdine, a water-soluble yellow-green fluorescent peptide characteristically produced by iron-starved cells. The binding of
Fe3+ by pyoverdine results in pyoverdine fluorescence
quenching. In preliminary experiments, Xiao and Kisaalita
(24) observed fast pyoverdine fluorescence quenching by
Fe2+, indicating the possibility of high pyoverdine
affinity for the ferrous ion and raising questions about
Fe3+ reduction as a possible mechanism of iron release from
the iron-pyoverdine complex. The purpose of the present study was to
use absorption and fluorescence spectroscopic techniques to investigate
Fe2+-pyoverdine complex formation. We report evidence which
strongly suggests that pyoverdines bind and oxidize ferrous ion.
Implications regarding possible mechanisms of iron removal from
iron-pyoverdine complexes by fluorescent pseudomonads are discussed.
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MATERIALS AND METHODS |
Strains and growth conditions.
P. fluorescens 2-79, P. aeruginosa ATCC 15692, and P. putida ATCC
12633 were grown on a synthetic succinate medium made up of 6.0 g
of K2HPO4, 3.0 g of
KH2PO4, 1.0 g of
(NH4)2SO4, 0.1 g of
MgSO4 · 7H2O, and 4.0 g of succinic
acid per liter and adjusted to pH 7.0 by adding the required volume of
1 N NaOH prior to sterilization (15). Precultures were
prepared by inoculating 125-ml flasks (working volume, 25 ml) with
strain 2-79, ATCC 15692, or ATCC 12633 from slants and incubating them
overnight. A 2-ml volume of the preculture broth was used to inoculate
500-ml flasks (working volume, 100 ml). Incubation was carried out with
shaking at 200 rpm in a New Brunswick Innova 4000 shaker/incubator at
25°C for strains 2-79 and ATCC 12633 and at 37°C for strain ATCC
15692. The incubation was terminated at the end of the log phase
(determined by a decrease in optical density), and the fermentation
broth was centrifuged at 10,000 × g for 10 min at
4°C. The supernatant was further membrane filtered (pore size, 0.25 µm; Amicon) to yield a cell-free solution of crude pyoverdine.
Isolation and purification of pyoverdines.
Pyoverdine
isolation and purification were carried out as previously described
(25). Briefly, the cell-free supernatant was mixed with 1 M
HEPES buffer (pH 7.0) (49:1, vol/vol) and applied to a chelating
Sepharose Fast Flow column (1.5 by 25 cm; Pharmacia LKB Biotechnology).
This column was presaturated with CuSO4 and equilibrated
with 20 mM HEPES buffer (pH 7.0) containing 100 mM NaCl. The eluent
flow rate was set at 100 ml/h. Fractions (10 ml) were collected, and
the absorbance at 400 nm (A400) of each fraction
was determined. The first two peaks of 2-79 crude pyoverdine were
eluted with the same HEPES buffer. The third peak was eluted with 20 mM
acetate buffer (pH 5.0) containing 100 mM NaCl. All fractions for each
peak were separately pooled and lyophilized. The dried material for
each peak was dissolved in small volumes (approximately 1 ml) of
distilled water containing 10 mM EDTA before being applied to a
Sephadex G-15 column (1.5 by 100 cm) that had been preequilibrated with
deionized water. The separation was carried out at eluent (deionized
water) flow rate of 20 ml/h and monitored by measuring the
A400. The ATCC 15692 and ATCC 12633 pyoverdines
were purified in a similar manner, except that for the ATCC 15692 pyoverdine, acetate buffers (pH 6.0 and 5.0) were used to elute
fractions B, C, and D. Purified pyoverdines from consecutive peaks were
designated Pf-A, Pf-B, and Pf-C (2-79 strain); Pa-A, Pa-B, Pa-C, and
Pa-D (ATCC 15692 strain); and Pp-A, Pp-B, and Pp-C (ATCC 12633 strain).
The three main pyoverdines used in this study were Pf-B, Pa-C, and
Pp-C. With the exception of Pf-B, the chemical structures of all the
pyoverdines used have been previously published (5, 6).
Determination of iron-pyoverdine complex formation. (i)
Fluorimetric method.
A 3-ml volume of pyoverdine solution (6.0 µM Pa-C, 6.5 µM Pf-B, or 6.0 µM Pp-C) in 100 mM HEPES buffer (pH
7.4) was incubated at 25°C with stirring. Then 10 µl of
Fe3+ or Fe2+ solution (freshly prepared with 20 mM HCl) was added to a final concentration of 3.3 µM. Fluorescence
quenching due to iron-pyoverdine complex formation was continuously
monitored with a Perkin-Elmer fluorometer (LD 50) at excitation and
emission wavelengths of 400 and 460 nm, respectively.
(ii) Spectrophotometric method.
Iron-pyoverdine complex
formation also was investigated by measuring absorbance changes.
Pyoverdine Pa-C (30 µM, 1.6 ml) in various buffers (100 mM acetate
[pH 5.0 and 6.0] and HEPES [pH 7.4]) was incubated at 25°C with
stirring. The reaction was initiated by adding 5 µl of
Fe3+ or Fe2+ solution to a final concentration
of 20 µM. The change in A460 due to
pyoverdine-iron complex formation was measured with a Beckman DU 650 spectrophotometer continuously or at desired time intervals.
(iii) Determination of ferrous ion concentrations.
The
Fe2+ concentration was determined by the ferrozine method
(2). The ferrozine reagent was obtained from Sigma. There
was no statistically significant difference between iron concentration profiles (ferrozine method) in samples that were deoxygenated and
continuously flushed with argon and those that were not. This showed
that oxidation of Fe2+ under our experimental conditions
was negligible.
(iv) Investigation of Fe3+-Pa-C complex
formation.
Fe3+-Pa-C complex formation at pH 7.4 was
investigated by combining 5 µl of Fe3+ (final
concentration, 20 µM) with pyoverdine Pa-C (final concentration, 30 µM) in 100 mM HEPES buffer (pH 7.4 with or without 10 mM ascorbic acid). Ascorbic acid was added 30 s after the Fe3+ and
pyoverdine were mixed. In both cases, changes in the
A460 were measured continuously. The oxidation
of Fe2+ was confirmed by using 100 mM HEPES buffer (pH 7.4)
with or without 10 mM ferrozine. Ferrozine was added 30 s after
the Fe2+ addition. Changes in the
A562 were measured continuously. The effect of
ascorbic acid on Fe3+ reduction in the absence of
pyoverdine also was investigated with ferrozine in a similar manner.
Determination of Fe2+ oxidation.
Addition of
aqueous solution of ferric ion to 8-hydroxyquinoline produces a black
complex with a maximal absorption at 600 nm. The specificity of this
reaction was confirmed by adding 1 mM Fe2+ or
Fe3+ (in 20 mM HCl) to a cuvette containing 1 mM
8-hydroxyquinoline in 100 mM acetate buffer (pH 4.0) to a final volume
of 1 ml. After incubation for 10 min at room temperature, the
A600 was measured. This reaction was used to
determine the extent of Fe2+ oxidation to Fe3+
during the Fe2+-pyoverdine reaction. A
pyoverdine-Fe2+ reaction mixture containing 0.5 mM
Fe2+ and 50 µM pyoverdine Pa-C in 100 mM acetate buffer
(pH 4.0) was preincubated at room temperature for 20 min. Then
8-hydroxyquinoline was added to a final concentration of 1.0 mM, and
the increase in the A600 was monitored
continuously. One of the reactants (Fe2+ or pyoverdine) was
omitted in each of the two controls included in each experiment.
 |
RESULTS |
Comparison of Fe2+- and Fe3+-pyoverdine
complex formation.
Figure 1 shows
fluorescence quenching of pyoverdine Pf-B, Pa-C, and Pp-C by
Fe2+ and Fe3+ at physiological pH. As
previously reported by Xiao and Kisaalita (24),
Fe2+ quenched the pyoverdine fluorescence much faster than
Fe3+ did in all cases. At 10 s after the
Fe2+ addition, the fluorescence of pyoverdine Pf-B, Pa-C,
and Pp-C was quenched to approximately 50% (Fig. 1). In comparison,
Fe3+ quenched the fluorescence of the three pyoverdines to
less than 10% of their maximum fluorescence after 100 s of
incubation. It is well known that the formation of the
Fe3+-pyoverdine complex results in a shift in the maximum
absorption of the free pyoverdine absorption spectrum as well as in the
appearance of a pronounced shoulder at 460 nm (15). The
increase in A460 was used to further confirm
Fe2+- and Fe3+-pyoverdine complex formation. As
shown in Fig. 2a, at physiological pH,
the A460 increased rapidly after
Fe2+ was added to the pyoverdine Pa-C solution and reached
a steady state after only 6 min of incubation, indicating that
Fe2+ was completely bound to pyoverdine Pa-C in a very
short period. However, less than 10% of Fe3+ was bound by
pyoverdine (Fig. 2b) at pH 7.4 after 10 min of incubation. When the
incubation was carried out over 24 h, about 90% of
Fe3+ was bound by pyoverdine (data not shown). Figure 2
also shows the effect of pH on the iron-pyoverdine complex formation
rate. The Fe2+-pyoverdine formation was pH independent,
while the Fe3+-pyoverdine formation was dramatically
increased when the pH was decreased from 7.4 to 5.0.

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FIG. 1.
Fluorescence quenching of pyoverdine Pf-B (a), Pa-C (b),
and Pp-C (c) by Fe2+ and Fe3+ at physiological
pH. Samples (3 ml) of pyoverdine solution (6.5 µM Pf-B, 6.0 µM
Pa-C, and 6.0 µM Pp-C) in 100 mM HEPES buffer (pH 7.4) were incubated
at 25°C with stirring. A 10-µl volume of Fe2+ or
Fe3+ solution was added to the reaction mixture to a final
concentration of 3.3 µM. Fluorescence quenching was measured
continuously at emission and excitation wavelengths of 460 and 400 nm,
respectively.
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FIG. 2.
Effect of pH on iron-pyoverdine Pa-C complex formation.
Pyoverdine Pa-C (30 µM, 1.6 ml) in various buffers (100 mM acetate
buffer [pH 5.0 and 6.0] and HEPES buffer [pH 7.4]) was incubated at
25°C with stirring. The reaction was initiated by adding 5 µl of
Fe2+ (a) or Fe3+ (b) solution to a final
concentration of 20 µM. The change in A460 due
to pyoverdine-iron complex formation was measured continuously.
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The slower association between pyoverdine and Fe
3+ at pH
7.4 was attributed to limited Fe
3+ solubility. As shown in
Fig.
3, addition of Fe
3+ to a
reaction mixture containing a reducing agent (ascorbic acid)
resulted
in a sudden increase in
A460, which was similar
to that
obtained with Fe
2+. When ascorbic acid was added to
the same reaction mixture 30
s after Fe
3+ addition, a
meager change in
A460 was observed in comparison
to the control (no ascorbic acid). The effect of ascorbic acid
addition
on Fe
3+ reduction in the absence of pyoverdine was further
investigated
by using ferrozine. A significant amount of
Fe
2+ was detected in the reaction mixture when
Fe
3+ was added to an ascorbic acid-containing solution
(Fig.
4). A
smaller amount of
Fe
2+ was detected when ascorbic acid was added to an
Fe
3+-containing reaction mixture.

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FIG. 3.
Effect of ascorbic acid on the
Fe3+-pyoverdine reaction. Pyoverdine Pa-C (30 µM) in 100 mM HEPES buffer (pH 7.4) (1.6 ml) was incubated at 25°C with
stirring. The change in A460 was measured
continuously. Fe3+ (5 µl) was added to a final
concentration of 20 µM in the presence of 10 mM ascorbic acid (curve
1), in the absence of ascorbic acid (curve 2), or 30 s before
addition of ascorbic acid (10 mM) (curve 3).
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FIG. 4.
Effect of ascorbic acid on Fe3+ reduction.
Ferrozine (10 mM) in 100 mM HEPES buffer (pH 7.4) (1.6 ml) was
incubated at 25°C with stirring. The A562 was
continuously measured. Fe3+ was added to the reaction
mixture to a final concentration of 20 µM, either in the presence of
10 mM ascorbic acid (curve 1) or 30 s before ascorbic acid
addition (curve 2).
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Fe2+-pyoverdine interactions.
The possibility that
Fe2+ underwent rapid autoxidation before being bound by
pyoverdine was investigated. As shown in Fig.
5, the profile of
A562 plotted against time for pyoverdine-free
samples was independent of the order of Fe2+ and ferrozine
addition at pH 7.4, indicating that Fe2+ autoxidation was
negligible under these experimental conditions.

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FIG. 5.
Determination of Fe2+ by using ferrozine.
Fe2+ (10 µl) was added to a ferrozine solution (10 mM in
100 mM HEPES buffer [pH 7.4]) to a final concentration of 25 µM,
and the A562 was monitored continuously (curve
A). The oxidation of Fe2+ was investigated by adding
ferrozine to the 100 mM HEPES buffer (pH 7.4) 30 s after
Fe2+ addition and monitoring the
A562 (curve B).
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To find out whether Fe
2+ remains in its reduced state or is
oxidized to Fe
3+ after being bound by pyoverdine, two
approaches were used. First,
the rates of iron removal from
Fe
2+- or Fe
3+-pyoverdine complexes by EDTA were
measured. These removal rates
were almost identical (Fig.
6), suggesting that either
Fe
2+ was oxidized on being bound by Pa-C or there was no
difference
in the iron dissociation rates between Fe
2+- and
Fe
3+-pyoverdine complexes. Second, 8-hydroxyquinoline, a
chelator
that binds Fe
3+ but has negligible
Fe
2+ affinity (Fig.
7), was
used to confirm whether Fe
3+ can be detected in
iron-pyoverdine complexes formed in Fe
2+-pyoverdine
samples. Figure
8 shows that there was no
change in
A600 when 8-hydroxyquinoline was
reacted with pyoverdine Pa-C
and a relatively small increase when
8-hydroxyquinoline was reacted
with 0.5 mM Fe
2+ (attributed
to Fe
3+ contamination, also seen in the Fe
2+
curve in Fig.
7). However, a relatively larger increase in the
A600 was observed when 8-hydroxyquinoline was
added to the Fe
2+-pyoverdine sample. The increase in
A600 observed in Fe
2+-pyoverdine
samples suggested that Fe
2+ was oxidized after being bound
by pyoverdine Pa-C.

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FIG. 6.
Iron dissociation from iron-pyoverdine complexes by
EDTA. EDTA was added to Fe2+- or
Fe3+-pyoverdine solution (20 µM in 100 mM HEPES buffer
[pH 7.4]) to a final concentration of 10 mM. The decrease in
A460 was monitored continuously.
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FIG. 7.
Standard curve for determination of Fe3+ and
Fe2+ by using 8-hydroxyquinoline. The experiments were
carried out in triplicate, and error bars represent the standard error.
The samples were prepared by adding 1 mM Fe2+ or
Fe3+ (in 20 mM HCl) to a cuvette containing 1 mM
8-hydroxyquinoline in 100 mM acetate buffer (pH 4.0) to a final volume
of 1 ml. After incubation for 10 min at room temperature, the
A600 was measured.
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FIG. 8.
Fe3+ dissociation from the
Fe2+-pyoverdine Pa-C mixture by 8-hydroxyquinoline (8-HQ).
A reaction mixture containing Fe2+ (0.5 mM) and pyoverdine
Pa-C (50 µM) in 100 mM acetate buffer (pH 4.0) was preincubated at
room temperature for 20 min, and 8-hydroxyquinoline was then added to a
final concentration of 1 mM. The increase in
A600 was monitored continuously. Two control
experiments, where either Fe2+ or pyoverdine Pa-C was
omitted, were also performed.
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DISCUSSION |
Two types of evidence support the conclusion that pyoverdines have
affinity for Fe2+ as well as Fe3+. First,
incubation of Fe2+ and Fe3+ with the three
pyoverdines at physiological pH resulted in faster fluorescence
quenching by Fe2+ than by Fe3+ (Fig. 1).
Second, a faster increase in A460 was observed
when Fe2+ was added to the pyoverdine solutions than when
Fe3+ was added (Fig. 2). Pyoverdines seem to be the most
complex siderophores described to date. The chemical structure of the
main pyoverdine used in this study, Pa-C, was published by Demange et
al. (4). Like most pyoverdines, Pa-C possesses the same type
of chromophore, derived from 2,3-diamino-6,7-dihydroxyquinoline, linked
to a small peptide which differs among strains by the number and
composition of amino acids. The three bidentate chelating groups that
bind Fe3+ are the catechol group of the chromophore, the
hydroxamate group of N
-hydroxyornithine, and
either an
-hydroxy acid of hydroxyaspartic acid or the
hydroxamate group of a second
N
-hydroxyornithine (4, 6, 22).
Structurally, pyoverdines are intermediate between the strict
hydroxamates and catechols found in the majority of microorganisms.
Hider (14) showed that electrostatic interactions dominated
the interactions between several divalent metal ions and two (catechol
and hydroxamate) ligands. It is therefore possible that the
Fe2+ complexation is coordinated by two of the three
pyoverdine bidentate chelating groups. It should also be pointed out
that other investigators have observed ion-pyoverdine complex formation
with Fe2+ and other divalent transition metal ions such as
Cu2+, Co2+, Mo2+, and
Ni2+ (16, 23).
Unlike Fe2+-pyoverdine, the Fe3+-pyoverdine
reaction was pH dependent. The reaction rate increased with decreasing
pH from 7.0 to 5.0 (Fig. 2b). This observation is consistent with the
fact that simple ferric salts are hydrolyzed at neutral pH to rapidly form extremely insoluble Fe(OH)3. Since Fe(OH)3
has a solubility product of 4 × 10
36, any free
Fe3+ in excess of 2.5 × 10
18 M would be
precipitated as the hydroxide (1, 20). The slow change in
fluorescence quenching or absorption at 460 nm observed with
Fe3+ in Fig. 1 and 2 was attributed to the low availability
of free Fe3+. Applying a reducing agent (ascorbic acid)
before Fe3+ addition resulted in a significant rise in
absorption due to Fe3+ reduction to the more soluble
Fe2+ (Fig. 3). Since Fe3+ was precipitated as
Fe(OH)3, it was not surprising that the addition of
ascorbic acid after Fe3+ application did not result in
significant iron-pyoverdine complex formation.
The possibility that Fe2+ underwent autoxidation before
reacting with pyoverdine was considered unlikely because the change in
absorption was independent of the order in which Fe2+ and
ferrozine were added (Fig. 5), suggesting that the
Fe2+-autoxidation reaction under the experimental
conditions was insignificant. In addition, the higher pyoverdine
binding rate exhibited with Fe2+ than with Fe3+
conclusively ruled out the possibility of Fe2+ autoxidation
followed by Fe3+-pyoverdine complex formation.
Given that EDTA has a higher association rate with Fe3+
(log K1 = 24.23) than with Fe2+ (log
K1 = 14.33) (3), it was hypothesized
that differences in EDTA-iron titration from Fe2+- and
Fe3+-pyoverdine complexes would suggest that the iron in
the iron-pyoverdine complex formed from the Fe2+-pyoverdine
reaction existed in its reduced form. However, identical EDTA-iron
titration rates from iron-pyoverdine complexes formed from
Fe2+-pyoverdine and Fe3+-pyoverdine reaction
mixtures (Fig. 6) suggest that the iron in the complex formed from the
Fe2+-pyoverdine mixture existed as Fe3+. This
was further confirmed by the 8-hydroxyquinoline assay, which showed the
presence of Fe3+ in this complex (Fig. 8).
The results reported in this study have important implications for
possible mechanisms of iron removal from iron-pyoverdine complexes by
fluorescent pseudomonads in natural environments. In view of the
observed spontaneous complexation and oxidation of the ferrous ion by
pyoverdine in this study, it can be suggested that successful release
of ferric ion from the iron-pyoverdine complex by ferripyoverdine
reductases, as previously reported (12), would require an
Fe2+ chelator. Further, a strong case can be made that the
iron exchange and reduction mechanisms in fluorescent pseudomonads may
not be mutually exclusive.
 |
ACKNOWLEDGMENTS |
We thank Manju Amin for technical assistance.
This work was supported in part by State and Hatch funds appropriated
to the University of Georgia, College of Agriculture & Environmental
Sciences Experiment Stations.
 |
FOOTNOTES |
*
Corresponding author. Mailing address: Biological and
Agricultural Engineering Department, Driftmier Engineering Center,
University of Georgia, Athens, GA 30602. Phone: (706) 542-0835. Fax:
(706) 542-8806. E-mail: williamk{at}bae.uga.edu.
 |
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Appl Environ Microbiol, April 1998, p. 1472-1476, Vol. 64, No. 4
0099-2240/98/$04.00+0
Copyright © 1998, American Society for Microbiology. All rights reserved.
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