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Applied and Environmental Microbiology, September 2000, p. 3823-3827, Vol. 66, No. 9
0099-2240/00/$04.00+0
Copyright © 2000, American Society for Microbiology. All rights reserved.
Ferrous Iron-Dependent Volatilization of Mercury by
the Plasma Membrane of Thiobacillus ferrooxidans
Kenji
Iwahori,1
Fumiaki
Takeuchi,2
Kazuo
Kamimura,3 and
Tsuyoshi
Sugio1,*
Science and Technology for Energy
Conversion,1 Administration Center for
Environmental Science and Technology,2 and
Department of Biological Function, Faculty of
Agriculture,3 Okayama University, Tsushima
Naka, Okayama 700-8530, Japan
Received 9 December 1999/Accepted 21 June 2000
 |
ABSTRACT |
Of 100 strains of iron-oxidizing bacteria isolated,
Thiobacillus ferrooxidans SUG 2-2 was the most resistant to
mercury toxicity and could grow in an Fe2+ medium (pH 2.5)
supplemented with 6 µM Hg2+. In contrast, T. ferrooxidans AP19-3, a mercury-sensitive T. ferrooxidans strain, could not grow with 0.7 µM
Hg2+. When incubated for 3 h in a salt solution (pH
2.5) with 0.7 µM Hg2+, resting cells of resistant and
sensitive strains volatilized approximately 20 and 1.7%, respectively,
of the total mercury added. The amount of mercury volatilized by
resistant cells, but not by sensitive cells, increased to 62% when
Fe2+ was added. The optimum pH and temperature for mercury
volatilization activity were 2.3 and 30°C, respectively. Sodium
cyanide, sodium molybdate, sodium tungstate, and silver nitrate
strongly inhibited the Fe2+-dependent mercury
volatilization activity of T. ferrooxidans. When incubated
in a salt solution (pH 3.8) with 0.7 µM Hg2+ and 1 mM
Fe2+, plasma membranes prepared from resistant cells
volatilized 48% of the total mercury added after 5 days of incubation.
However, the membrane did not have mercury reductase activity with
NADPH as an electron donor. Fe2+-dependent mercury
volatilization activity was not observed with plasma membranes
pretreated with 2 mM sodium cyanide. Rusticyanin from resistant cells
activated iron oxidation activity of the plasma membrane and activated
the Fe2+-dependent mercury volatilization activity of the
plasma membrane.
 |
INTRODUCTION |
Thiobacillus ferrooxidans
is an acidophilic, chemolithotrophic, iron-oxidizing bacterium that
uses energy produced by oxidation of reduced sulfur compounds and
ferrous iron. This bacterium is one of the most important bacteria for
bacterial leaching of sulfide ores. To solubilize metal ions from
sulfide ores much more efficiently, isolation of T. ferrooxidans strains which are resistant to heavy metal ions seems
to be important. It has been reported that T. ferrooxidans
is sensitive to Hg2+, Ag+, and
MoO42
(5). The properties of
mercuric reductase, a flavoenzyme that reduces Hg2+ to less
toxic Hg0 with NADPH as an electron donor, have been
studied actively with a wide range of gram-negative and gram-positive
bacteria (1, 13-15). Mercuric reductase activity has also
been found in T. ferrooxidans cells (3, 11, 12).
The genes involved in volatilization of mercury have been cloned and
characterized in detail (4, 6, 8, 11).
Recently, we partially characterized the difference between
mercury-resistant and mercury-sensitive strains of T. ferrooxidans. The levels of NADPH-dependent mercuric reductase
were not significantly different in these strains. Instead, purified
cytochrome c oxidase from resistant strain Funis 2-1 was
more resistant to Hg2+ than purified cytochrome
c oxidase from a sensitive strain was (20). To
explain the remarkable mercury resistance observed, we proposed that
both a mercury-resistant cytochrome c oxidase and a
cytosolic NADPH-dependent mercuric reductase, not the latter alone,
function in resistant cells (20).
In this study, a more mercury-resistant strain (SUG 2-2) was obtained
from 100 new strains of iron-oxidizing bacteria, and we show that the
mercury volatilized by resting cells of T. ferrooxidans SUG
2-2 was activated in the presence of Fe2+. Although the
plasma membrane of T. ferrooxidans SUG 2-2 did not have
NADPH-dependent mercury reductase activity, the membrane had the
ability to volatilize Hg0 from a salt solution containing
Fe2+. Fe2+-dependent mercury volatilization
activity with plasma membranes was inhibited by sodium cyanide and
activated by the blue copper protein rusticyanin.
 |
MATERIALS AND METHODS |
Microorganisms, medium, and growth conditions.
Ninety-four
strains of iron-oxidizing bacteria isolated from streams and soils in
Japan and the United States and T. ferrooxidans ATCC 13661, ATCC 14119, ATCC 19859, ATCC 21834, ATCC 23270, and ATCC 33020 from the
American Type Culture Collection were used in this study. To isolate
iron-oxidizing bacteria, stream water or soil samples were incubated at
30°C under aerobic conditions in Fe2+ medium (pH 2.5)
containing (per liter) 30 g of FeSO4 · 7H2O, 3 g of
(NH4)2SO4, 0.5 g of
K2HPO4, 0.5 g of MgSO4
· 7H2O, 0.1 g of KCl, and 0.01 g of
Ca(NO3)2 (16). When the
Fe2+ in the culture medium was oxidized, samples were
plated on 1.0% gellan gum plates containing (per liter) 30 g of
FeSO4 · 7H2O, 3 g of
(NH4)2SO4, 0.5 g of
K2HPO4, 0.5 g of MgSO4
· 7H2O, 0.1 g of KCl, 0.01 g of
Ca(NO3)2, and 0.3 g of yeast extract.
Rusty colonies appearing on the plate were picked. This process was repeated more than three times, and the final isolates were preserved on Fe2+ medium (pH 2.5) and used throughout this study. The
method used for large-scale production of cells has been described
previously (18).
Growth rate.
After cultivation in Fe2+ medium
(pH 2.5) at 30°C, cells were separated from the particles of ferric
hydroxide by filtering with a no. 5B Toyo paper filter. The numbers of
cells in the filtrates were counted with a microscope and hemacytometer
(Kayagaki Irika Kogyo Co., Ltd., Tokyo, Japan) after dilution with 0.1 N sulfuric acid when necessary.
Analysis of mercury volatilized from T. ferrooxidans
culture medium.
A 50-ml culture flask with a screw cap contained
19 ml of Fe2+ medium (pH 2.5) supplemented with 0.7 M
Hg2+ and 1 ml of an active seed culture of T. ferrooxidans. A small test tube containing 2 ml of a
KMnO4 solution was inserted in the 50-ml culture flask to
trap the Hg2+ volatilized from the culture medium. The
KMnO4 solution used (100 ml) was composed of a 10-ml
solution containing 0.6 g of KMnO4, 5 ml of
concentrated H2SO4, and 85 ml of deionized
water. After the culture medium was aerated by shaking at 30°C and
100 rpm, the concentration of Hg0 trapped in the
KMnO4 solution was measured by cold-vapor atomic absorption spectroscopy.
Analysis of mercury volatilized by resting cells and the plasma
membranes of T. ferrooxidans.
Each of several 50-ml flasks
with screw caps contained a reaction mixture plus 2 ml of a
KMnO4 solution as described above. The gas phase was air,
and the reaction mixture was rotated at 100 rpm at 30°C. The reaction
mixture used for the measurement of mercury volatilization with resting
cells was composed of a salt solution (pH 2.5) (20 ml), resting cells
of T. ferrooxidans (1 mg of protein), 0.7 µM
HgCl2, and 25 mM ferrous sulfate. The reaction mixture used
for the measurement of mercury volatilization with plasma membranes was
composed of a salt solution (pH 3.8) (10 ml), plasma membranes of
T. ferrooxidans SUG 2-2 (50 µg of protein), 0.7 µM
HgCl2, and 1 mM ferrous sulfate. The salt solution used
contained (per liter) 3 g of
(NH4)2SO4, 0.5 g of
K2HPO4, 0.5 g of MgSO4
· 7H2O, 0.1 g of KCl, and 0.01 g of
Ca(NO3)2. The concentration of Hg0
trapped in the KMnO4 solution was measured by cold-vapor
atomic absorption spectroscopy.
Preparation of plasma membranes and rusticyanin.
Cells of
T. ferrooxidans SUG 2-2 grown in Fe2+ medium (pH
2.5) at 30°C for 1 week were washed three times with 0.1 M potassium phosphate buffer (pH 7.5), disrupted by sonication for 15 min with a
sonicator (model INSONATOR 201M; Kubota Co., Tokyo, Japan), and
centrifuged at 12,000 × g for 10 min to remove cell
debris. The cell extract obtained was centrifuged at 105,000 × g for 60 min to obtain the plasma membrane fraction.
Rusticyanin was prepared by the method described previously
(2).
Protein content.
Protein content was determined by the
method of Lowry et al. (9) with crystalline bovine serum
albumin as the standard.
 |
RESULTS |
Volatilization of mercury from Fe2+ medium by
mercury-resistant or -sensitive T. ferrooxidans
strains.
Screening 100 iron-oxidizing bacterial strains, including
six T. ferrooxidans strains from the American Type Culture
Collection, for resistance to Hg2+ was done. T. ferrooxidans SUG 2-2, isolated from hot spring water from Aomori
Prefecture, Japan, was the strain most resistant to Hg2+
toxicity among the strains tested and could grow in Fe2+
medium supplemented with 6 µM Hg2+. This strain gave a
cell yield of 6.0 × 107 cells/ml after 6 days of
cultivation in Fe2+ medium (pH 2.5) supplemented with 0.7 µM Hg2+ (Fig. 1A). SUG 2-2 volatilized 86% of the total mercury (14 nmol) added to the culture
medium after 4 days of cultivation (Fig. 1B). T. ferrooxidans Funis 2-1 (10, 20) volatilized 78% of the
total mercury after 8 days of cultivation. In contrast, T. ferrooxidans AP19-3 (7, 17) could not grow in
Fe2+ medium supplemented with 0.7 µM Hg2+ and
volatilized only 10% of the total mercury added to the medium after 10 days of cultivation (Fig. 1). Neither Funis 2-1 nor AP19-3 could grow
in Fe2+ medium supplemented with 6 µM HgCl2.

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FIG. 1.
Volatilization of metal mercury from Fe2+
medium containing 0.7 M Hg2+ by T. ferrooxidans
strains. (A) Cell growth and amount of Fe2+ remaining in
Fe2+ medium (pH 2.5) containing 0.7 µM Hg2+.
Symbols: , , and , cell growth of T. ferrooxidans
SUG 2-2, Funis 2-1, and AP19-3, respectively; , , and , amount
of Fe2+ remaining with T. ferrooxidans SUG 2-2, Funis 2-1, and AP19-3, respectively. (B) Mercury volatilized in
Fe2+ medium (pH 2.5) containing Hg2+ (0.7 µM). Cultures of T. ferrooxidans SUG 2-2 ( ), Funis 2-1 ( ), and AP19-3 ( ) were examined.
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Effects of ferrous iron on the amount of mercury volatilized from
resting cells.
The mercury reductase activity of SUG 2-2 cells was
determined with NADPH as an electron donor and cytosol prepared from
the strain as an enzyme source. The NADPH-dependent mercury
volatilization activity of the cytosol of strain SUG 2-2 was nearly the
same as that of Funis 2-1 (data not shown). From our results, it seems that strain SUG 2-2 has another enzyme system to detoxify mercury. The
role of the iron-oxidizing system of SUG 2-2 in mercury detoxification by the strain was studied. The amount of mercury volatilized from a
10-ml salt solution (pH 2.5) containing resting cells of SUG 2-2 and
0.7 µM Hg2+ was 20% of the total amount of mercury (14 nmol) added to the reaction mixture after 3 h of incubation. The
amount of mercury volatilized by the resting cells increased
approximately threefold when 25 mM Fe2+ was added, and
approximately 62% of the total mercury added was volatilized. The
amount of mercury volatilized by SUG 2-2 cells increased in proportion
to the concentration of Fe2+ added to the reaction mixture
and also in proportion to the cell concentration (data not shown). To
clarify whether T. ferrooxidans strains other than SUG 2-2 also have Fe2+-dependent mercury volatilization activity,
the same experiments were done with resting cells of nine additional
iron-oxidizing bacterial strains with or without 25 mM Fe2+
(Fig. 2). After 60 min of incubation,
resting cells of Funis 2-1 volatilized 34 and 14% of the total amount
of mercury (14 nmol) added to the reaction mixture in the presence and
in the absence of 25 mM Fe2+, respectively, indicating that
Funis 2-1 as well as SUG 2-2 has Fe2+-dependent mercury
volatilization activity. T. ferrooxidans ATCC 33020 from the
American Type Culture Collection volatilized mercury in the presence of
Fe2+. In comparison, the amounts of metal mercury
volatilized by T. ferrooxidans AP19-3 and ATCC 13661 were
less or the same with or without Fe2+. As shown in Fig. 2,
the day after each of the strains exhibited the maximum cell number in
Fe2+ medium containing 0.7 µM Hg2+, testing
was carried out. The results indicate that the strains which had higher
Fe2+-dependent mercury volatilization activities were
more resistant to Hg2+ toxicity than the strains which had
lower activities. The Fe2+-dependent mercury volatilization
activities were completely inhibited by pretreating strain SUG 2-2 and
Funis 2-1 cells with 5 mM NaCN for 15 min, suggesting that cytochrome
c oxidase of T. ferrooxidans is involved in the
Fe2+-dependent mercury volatilization reaction.

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FIG. 2.
Fe2+-dependent mercury volatilization
activities of resting cells of 10 T. ferrooxidans strains.
The mercury volatilization activities of T. ferrooxidans
strains were measured in 20 ml of salt solution (pH 2.5) containing
resting cells (1 mg of protein), 0.7 µM Hg2+, and 25 mM
Fe2+ (striped bars). The activities were also measured in
20 ml of salt solution (pH 2.5) containing resting cells and
Hg2+ but no Fe2+ (open bars). The days on which
maximum cell growth was observed in Fe2+ medium containing
0.7 µM Hg2+ are shown for the 10 strains of T. ferrooxidans.
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Characteristics of Fe2+-dependent mercury
volatilization activity.
The optimum pH and temperature for
Fe2+-dependent mercury volatilization activity of strain
SUG 2-2 cells were pH 2.3 and 30°C, respectively. These values are
the same as the optimum pH and temperature values for the iron oxidase
of T. ferrooxidans SUG 2-2 cells (data not shown).
The effects of heavy metal ions on Fe2+-dependent mercury
volatilization activity were studied with resting cells of SUG 2-2 (Table 1). Na2MO4
and Na2WO4 inhibited the activity more than
80%. Silver ions also markedly inhibited the activity at 5 mM. These
compounds strongly inhibited both iron oxidase and cytochrome
c oxidase activities of T. ferrooxidans (5, 10, 19).
Volatilization of mercury by the plasma membrane of T. ferrooxidans SUG 2-2.
Fe2+-dependent mercury
volatilization activity was measured with plasma membranes from strain
SUG 2-2 cells. The plasma membranes did not have mercuric reductase
activity when NADPH was used as an electron donor. To decrease the
amount of reduced compounds in the plasma membrane, KMnO4
was added to the membrane until reduced type c and
a cytochromes in the membrane were nearly completely oxidized. In the presence and absence of 1 mM Fe2+, 50 µg
of plasma membranes prepared from SUG 2-2 cells volatilized 48 and
12%, respectively, of the total mercury (7 nmol) added to a 10-ml
reaction mixture after 5 days of incubation at 30°C (Fig.
3). Mercury was not volatilized in a
reaction mixture containing Hg2+, Fe2+, and
plasma membranes boiled for 10 min. Since the plasma membranes prepared
from T. ferrooxidans SUG 2-2 cells had low iron-oxidizing activity, we added the blue copper protein rusticyanin to the reaction
mixture. Rusticyanin isolated from SUG 2-2 cells activated the
iron-oxidizing activity of plasma membranes 4.5-fold (data not shown).
Fe2+-dependent mercury volatilization activity markedly
increased in the presence of 0.1 mg of rusticyanin (Fig.
4). In the presence of 0.1 mg of
rusticyanin, plasma membranes of SUG 2-2 cells volatilized 1.7 and 0.2 nmol of mercury in 10-ml reaction mixtures containing 7 nmol of
Hg2+ in the presence and in the absence of 1 mM
Fe2+, respectively, after 2 days of incubation. However,
since only 2.2 nmol of mercury was volatilized after 5 days of
incubation, 7 nmol of HgCl2 and 10 µmol of
Fe2+ were added to the reaction mixture every 3 days (Fig.
5). Further additions of
HgCl2 and Fe2+ to the reaction mixture resulted
in further volatilization of the mercury, suggesting that the membranes
still had Fe2+-dependent mercury volatilization activity
after 6 days of incubation. After 8 days of incubation and two more
additions of mercury, the plasma membranes of SUG 2-2 cells volatilized
5 nmol of mercury in the reaction mixture. In contrast, only 1.5 nmol
of mercury was volatilized when the membranes were incubated without a
further addition of mercury. Mercury was not volatilized in the
reaction mixture containing plasma membranes boiled for 10 min.

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FIG. 3.
Effects of Fe2+ concentration on the mercury
volatilization activity of plasma membranes of T. ferrooxidans SUG 2-2. The Fe2+-dependent mercury
volatilization activity was measured in 10 ml of salt solution (pH 3.8)
containing 50 µg of plasma membranes, 0.7 µM Hg2+ and
Fe2+ ( , 0.01 mM; , 0.2 mM; , 1 mM; , 3 mM; and
, 5 mM). The activities were also measured in 10 ml of salt solution
containing 50 µg of plasma membranes and 0.7 µM Hg2+
but no Fe2+ ( ) and in 10 ml of salt solution containing
50 µg of plasma membranes boiled for 10 min, 0.7 µM
Hg2+, and 1 mM Fe2+ (×).
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FIG. 4.
Effects of rusticyanin on the Fe2+-dependent
mercury volatilization activity of T. ferrooxidans SUG 2-2 cells. The Fe2+-dependent mercury volatilization activity
was measured in 10 ml of salt solution (pH 3.8) containing 50 µg of
plasma membranes, 1 mM Fe2+, 0.7 µM Hg2+, and
rusticyanin ( , 0.01 mg; , 0.02 mg; , 0.05 mg; and , 0.1 mg). The activities were also measured in 10 ml of salt solution
containing 50 µg of plasma membranes, 1 mM Fe2+, and 0.7 µM Hg2+ ( ), in a salt solution containing 50 µg of
plasma membranes and 0.7 µM Hg2+ ( ), in a salt
solution containing 1 mM Fe2+, 0.7 µM Hg2+,
rusticyanin (0.1 mg of protein), and boiled plasma membranes (×), and
in a salt solution containing 1 mM Fe2+, 0.7 µM
Hg2+, and rusticyanin (0.1 mg of protein) but no plasma
membranes ( ).
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FIG. 5.
Effects of further addition of HgCl2 to the
reaction mixture on Fe2+-dependent mercury volatilization
activity. The Fe2+-dependent mercury volatilization
activity was measured in 10 ml of salt solution (pH 3.8) containing 50 µg of plasma membranes, 1 mM Fe2+, 0.7 µM
Hg2+, and rusticyanin (0.1 mg of protein). Hg2+
(7 nmol) and Fe2+ (10 nmol) were added to the reaction
mixture every 3 days ( ). The Hg2+ volatilized was also
measured in a 10-ml reaction mixture to which HgCl2 was not
added ( ). The arrows indicate the times at which HgCl2
(7 nmol) was added to the reaction mixture. The
Fe2+-dependent mercury volatilization activity was also
measured in 10 ml of salt solution (pH 3.8) containing 50 µg of
plasma membranes boiled for 10 min, 1 mM Fe2+, 0.7 µM
Hg2+, and rusticyanin (0.1 mg of protein) (×).
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 |
DISCUSSION |
Bacteria resistant to mercury usually have a cytosolic
NADPH-dependent mercuric reductase which catalyzes the reduction of soluble Hg2+ to volatile Hg0 with NADPH as an
electron donor. Studies to clarify the characteristics of mercury
reductase and its gene structure have been performed with various
bacteria, including members of the genera Pseudomonas, Staphylococcus, Bacillus, and Serratia
(1, 13, 15). The iron-oxidizing chemolithotrophic bacterium
T. ferrooxidans also has mercuric reductase to detoxify
Hg2+ (8, 11, 12). Recently, it was shown that
both mercuric reductase and cytochrome c oxidase, but not
mercuric reductase alone, function in mercury-resistant strain Funis
2-1 of T. ferrooxidans when the strain grows in
Fe2+ medium containing Hg2+ (20).
In this report, it is shown that a newly isolated strain, T. ferrooxidans SUG 2-2, is much more resistant to mercury than the
previously reported strain Funis 2-1 and that
Fe2+-dependent mercury volatilization activity is present
in six T. ferrooxidans strains, including strain SUG 2-2. Olson et al. (11, 12) reported that the rate of mercury
volatilization by T. ferrooxidans BA-4 which was adapted to
Hg2+ at concentrations up to 5 µM was slightly
accelerated by the addition of 150 mM FeSO4. The level of
Fe2+-dependent mercury volatilization activity found in the
six strains of T. ferrooxidans corresponded well with the
level of mercury resistance of these strains, which was estimated by
the growth rate in Fe2+ medium (pH 2.5) containing 0.7 µM
Hg2+. This strongly suggests the possibility that both
Fe2+-dependent mercury volatilization and cytosolic
NADPH-dependent mercury volatilization play a role in detoxification of
Hg2+ in many strains of T. ferrooxidans.
According to the level of Fe2+-dependent mercury
volatilization activity, the T. ferrooxidans strains
isolated can be categorized into two groups, one containing the strains
possessing a high level of Fe2+-dependent mercury
volatilization activity and the other containing the strains possessing
a low level of activity.
Involvement of an iron oxidation enzyme system in the
Fe2+-dependent mercury volatilization reaction of T. ferrooxidans SUG 2-2 cells is supported by the following findings.
(i) Plasma membranes prepared from strain SUG 2-2 cells did not have
NADPH-dependent mercuric reductase activity but had
Fe2+-dependent mercury volatilization activity. Plasma
membranes boiled for 10 min did not have mercury volatilization
activity. (ii) Rusticyanin purified from strain SUG 2-2 cells enhanced
both iron-oxidizing activity and the Fe2+-dependent mercury
volatilization activity. (iii) NaCN, which strongly inhibits the iron
oxidase activity of cells and the cytochrome c oxidase
activity of plasma membranes, completely inhibited the Fe2+-dependent mercury volatilization activity. The
Fe2+-dependent mercury volatilization activity measured
with plasma membranes was very low compared with that of the resting
cells. This is probably because the components needed for iron
oxidation, for instance, rusticyanin and soluble cytochrome
c oxidase, were lost during preparation of plasma membranes
by disruption of the resting cells with a sonicator. The iron-oxidizing
activities measured at pH 3.8 were 11.4 and 0.14 µl of O2
consumed/mg per min for the resting cells and the plasma membranes, respectively.
This paper shows that there is a novel Fe2+-dependent
mercury volatilization activity in six strains of T. ferrooxidans, including strain SUG 2-2. To clarify the mechanism
of the Fe2+-dependent mercury volatilization reaction more
precisely, it is important to answer the following question precisely:
is cytochrome c oxidase alone or cytochrome c
oxidase plus other components of the iron oxidation enzyme system
involved in the mercury volatilization reaction? Our preliminary
experiments show that cytochrome c oxidase partially
purified from T. ferrooxidans SUG 2-2 volatilizes mercury in
the presence of Fe2+.
 |
FOOTNOTES |
*
Corresponding author. Mailing address: Science and
Technology for Energy Conversion, Okayama University, Tsushima
Naka, Okayama 700-8530, Japan. Phone: 81-86-251-8306. Fax:
81-86-251-8306. E-mail: Sugio{at}cc.okayama-u.ac.jp.
 |
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Applied and Environmental Microbiology, September 2000, p. 3823-3827, Vol. 66, No. 9
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Copyright © 2000, American Society for Microbiology. All rights reserved.
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