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Applied and Environmental Microbiology, January 2001, p. 118-124, Vol. 67, No. 1
0099-2240/01/$04.00+0 DOI: 10.1128/AEM.67.1.118-124.2001
Copyright © 2001, American Society for Microbiology. All rights reserved.
Polyclonal Antibodies Recognizing the AmoB Protein of Ammonia
Oxidizers of the
-Subclass of the Class
Proteobacteria
Claudia
Pinck,1,*
Caroline
Coeur,2
Patrick
Potier,2 and
Eberhard
Bock1
Institut für Allgemeine Botanik,
Universität Hamburg, D-22609 Hamburg,
Germany,1 and Laboratoire d'Ecologie
Microbienne, UMR CNRS 5557, Université Claude Bernard Lyon 1, 69622 Villeurbanne cedex, France2
Received 5 June 2000/Accepted 22 September 2000
 |
ABSTRACT |
A 41-kDa protein of Nitrosomonas eutropha was purified,
and the N-terminal amino acid sequence was found to be nearly identical with the sequence of AmoB, a subunit of ammonia monooxygenase. This
protein was used to develop polyclonal antibodies, which were highly
specific for the detection of the four genera of ammonia oxidizers of
the
-subclass of Proteobacteria
(Nitrosomonas, including Nitrosococcus mobilis,
which belongs phylogenetically to Nitrosomonas; Nitrosospira; Nitrosolobus; and
Nitrosovibrio). In contrast, the antibodies did not react
with ammonia oxidizers affiliated with the
-subclass of
Proteobacteria (Nitrosococcus oceani and
Nitrosococcus halophilus). Moreover, methane oxidizers
(Methylococcus capsulatus, Methylocystis
parvus, and Methylomonas methanica) containing the related particulate methane monooxygenase were not detected.
Quantitative immunoblot analysis revealed that total cell protein of
N. eutropha consisted of approximately 6% AmoB, when cells
were grown using standard conditions (mineral medium containing 10 mM
ammonium). This AmoB amount was shown to depend on the ammonium
concentration in the medium. About 14% AmoB of total protein was found
when N. eutropha was grown with 1 mM ammonium, whereas 4%
AmoB was detected when 100 mM ammonium were used. In addition, the
cellular amount of AmoB was influenced by the absence of the substrate. Cells starved for more than 2 months contained nearly twice as much
AmoB as actively growing cells, although these cells possessed low
ammonia-oxidizing activity. AmoB was always present and could even be
detected in cells of Nitrosomonas after 1 year of ammonia starvation.
 |
INTRODUCTION |
Nitrification, the microbial
oxidation of ammonia to nitrate, is an essential part of the microbial
nitrogen cycle in marine, freshwater, and soil environments. Two
physiologically different groups of chemolithoautotrophic bacteria, the
ammonia and nitrite oxidizers, are involved in this oxidation. The
ammonia oxidizers derive their energy from the oxidation of
ammonia to nitrite. The first step, the oxidation of ammonia to
hydroxylamine is catalyzed by ammonia monooxygenase (AMO) (18,
60). Hydroxylamine is further oxidized to nitrite by
hydroxylamine oxidoreductase (HAO) (5, 53). Since the AMO
is an important key enzyme of nitrification, many efforts have been
initiated to isolate the enzyme. However, it has not been purified thus
far since the enzyme is not stable once isolated from the cells
(16, 51, 52). Therefore, little is known about its
structure and enzymatic mechanism. Information on the molecular
properties of AMO has been deduced from studies with intact cells. It
was demonstrated that the AMO has a broad substrate specificity
(4, 22, 28, 54) and is irreversibly inhibited by
C2H2 (25, 26). A similar substrate
range and inhibitor profiles including C2H2
effects were found for the biochemically related particulate methane
monooxygenase (pMMO) of methane oxidizing bacteria (7, 14,
20, 42). Moreover, the AMO and the pMMO may be evolutionary
related, since their encoding genes share high sequence similarities
(3, 19).
Inactivation of AMO by 14C2H2
labels a membrane bound 27-kDa polypeptide, which is called AmoA
(21). This protein seems to be the active-site-containing
subunit of the enzyme (21, 24). A corresponding gene
amoA has been identified and, within the same operon,
another gene called amoB was sequenced (39).
The amoB codes for a 41-kDa polypeptide (AmoB), which could
be copurified with the 27-kDa AmoA (10, 39). Upstream of
the amoA-amoB tandem, a third gene was identified,
amoC (3, 30). The numbers of copies of the
amo operon seem to be genus specific. Two nearly identical
copies are present in strains of Nitrosomonas and
Nitrosovibrio, and three copies were found in strains of
Nitrosospira and Nitrosolobus (29, 31, 39,
41, 45), whereas only a single copy could be detected in marine
Nitrosococcus strains of the
-subclass of
Proteobacteria (3). However, neither the
expressed polypeptides of amoA and amoB nor the
purified proteins from Nitrosomonas cell homogenates showed
ammonia-oxidizing activity (21, 23).
In previous studies antibodies were developed using whole cells of
ammonia oxidizers, which recognize epitopes of the cell wall (8,
43, 47, 55, 56). These antibodies were applied in ecological
studies to detect and count ammonia oxidizers in bacterial communities
by using fluorescence microscopy. Their application was supposed to
overcome the disadvantages of traditional counting methods such as the
most-probable-number technique (38), which often
underestimates the number of ammonia oxidizers in the natural
environment (9). However, the application of these antibodies was limited since ammonia oxidizers show high serological diversity even within one genus. Therefore, ecologically relevant strains had to be isolated prior to antibody development. In the case
of nitrite-oxidizing bacteria, it was shown that antibodies recognizing
the conserved key enzyme can be used for the detection of all known
genera of these organisms (6). They can be applied for
studies of the key enzyme, as well as for the detection of as-yet-nonisolated strains in the environment.
In this study, the AmoB subunit of the AMO of N. eutropha N904 was used for the development of polyclonal
antibodies. Evidence is given that these antibodies are highly specific
for all genera of ammonia oxidizers affiliated with the
-subclass of
Proteobacteria. Quantitative immunoblot analysis was used to
measure the cellular amount of AmoB of Nitrosomonas eutropha
N904 under different growth and starvation conditions.
(This study is based in part on the doctoral study of C. Pinck at the
University of Hamburg.)
 |
MATERIALS AND METHODS |
Bacterial strains and culture conditions.
The strains of
ammonia oxidizers isolated from soil and used in this study were
Nitrosomonas communis Nm 2 (34),
Nitrosomonas oligotropha Nm 45 (34),
Nitrosomonas ureae Nm 10 (34),
Nitrosospira sp. strain Nsp 1, and Nitrosolobus
multiformis Nl 13 (ATCC 25196). Nitrosomonas europaea
Freitag and Nitrosomonas nitrosa Nm 90 (34) were obtained from sewage. The strains Nitrosomonas sp.
strain Dave and N. eutropha N904 originated from a
biowaste fermenter and from cattle manure, respectively.
Nitrosomonas sp. strain Nm R1.24, Nitrosospira
sp. strain Nsp G1.6, Nitrosospira sp. strain Nsp M1.3,
Nitrosospira sp. strain Nsp R6.2, Nitrosovibrio
sp. strain Nv G1.3, and Nitrosovibrio sp. strain Nv K7.1
(49) were isolated from the sandstone of historical
buildings. The marine ammonia oxidizers of the
-subclass of the
Proteobacteria isolates Nitrosomonas aestuarii Nm
36 (34), Nitrosomonas cryotolerans Nm 55, Nitrosomonas halophila Nm 1 (34),
Nitrosomonas marina Nm 22 (34),
Nitrosococcus mobilis Nc 2 (32), and the two
marine ammonia oxidizers belonging to the
-subclass of
Proteobacteria isolates Nitrosococcus halophilus
Nc 4 (33) and Nitrosococcus oceani Nc 1 (ATCC
19707) were obtained from seawater.
The nitrite oxidizers Nitrobacter hamburgensis
X14 (11) and Nitrobacter
winogradskyi Engel (12) originated from soil. Nitrospira moscoviensis M-1 (15) was obtained
from a heating system. Nitrobacter vulgaris K48
(12) originated from the sandstone of historical
buildings; Nitrospina gracilis 3(211) (57),
Nitrospina sp. strain 347, and Nitrococcus
mobilis 231 (57) were isolated from seawater.
All ammonia oxidizers, nitrite oxidizers, the methane oxidizers
Methylococcus capsulatus Bath (NCIMB 11132),
Methylocystis parvus 4a,
Methylomonas methanica
Oo52006, and
Bacillus subtilis 019,
Escherichia
coli K-12/067 (ATCC 23716),
Methylobacterium radiotolerans,
Paracoccus denitrificans 001 (ATCC
19367), and
Pseudomonas sp. strain AM1 are stored in the
culture collection
of the Institut für Allgemeine Botanik,
Abteilung Mikrobiologie,
Universität Hamburg. The strains
Achromobacter cycloclastes,
Agrobacterium
tumefaciens GM 19023,
Alcaligenes faecalis (ATCC
8750),
Azorhizobium sp. strain 24,
Azospirillum
lipoferum (ATCC
29707),
Bacillus azotoformans (ATCC
29788),
Bradyrhizobium denitrificans,
Chromobacterium
violaceum, and
Pseudomonas sp. strain AK 15 were
obtained from C. Coeur (University of Lyon I, Villeurbanne,
France).
Terrestrial and freshwater ammonia oxidizers were grown at 28°C in
mineral salt medium (
34) in the presence of 10 mM
ammonium.
N. cryotolerans Nm 55,
N. aestuarii Nm 36,
N. halophila Nm 1,
and
Nitrosococcus mobilis Nc 2 were grown in the same medium
containing
10 g of NaCl liter
1.
N. marina Nm 22,
Nitrosococcus oceani Nc 1, and
Nitrosococcus halophilus Nc 4 were cultivated in seawater
medium, with the following
composition: 10 mM NH
4Cl, 0.4 mM
KH
2PO
4, 3 g of HEPES, and 1 ml
of 0.05%
(wt/vol) cresol red solution per liter of 40%
seawater.
For quantitative immunoblots,
N. eutropha N904 was
grown lithoautotrophically in mineral salt medium containing different
concentrations of NH
4Cl (1, 10, or 100 mM). After cells of
N. eutropha N904 were grown for 10 days with different
substrate
concentrations, the AmoB amount was determined. For
mixotrophic
growth the mineral salt medium was supplemented with 5 mM
pyruvate,
1.5 g of yeast extract (Difco) liter
1, and
1.5 g of peptone (Difco) liter
1, and either 9.1 mM
pyruvate or 9.1 mM
alanine.
Batch cultures of
N. eutropha N904,
Nitrosomonas sp. strain Dave and
N. europaea
Freitag were starved of ammonia at 16°C in
the dark. To test the AmoB
amount by immunoblotting, samples were
obtained after 1, 29, 58, 129, and 360 days of ammonia
starvation.
Nitrobacter hamburgensis X
14,
Nitrobacter
winogradskyi Engel, and
Nitrobacter vulgaris
K
48 were grown mixotrophically in the
presence of 2 g
of NaNO
2 liter
1 (
12).
Nitrospira moscoviensis M-1 was cultivated in mineral
medium
with 0.2 g of NaNO
2 liter
1
(
15).
Nitrospina gracilis 3(211),
Nitrospina sp. strain 347,
and
Nitrococcus
mobilis 231 were cultivated in seawater media
according to the
method of Watson and Waterbury (
57). The cultures
were
incubated at 28°C, expect for
Nitrospira moscoviensis M-1,
which was incubated at 37°C.
The methane oxidizers were cultivated in nitrate mineral salt medium
(
58) including 0.25 µM CuSO
4 at 3% methane
synthetic
air atmosphere. The methylotrophs were grown in mineral
medium
containing 0.15% (wt/vol) methanol (
17). All other
bacterial
strains were cultivated according to the American Type
Culture
Collection and National Collection of Industrial and Marine
Bacteria
instructions.
AmoB isolation, sequencing, and production of antibodies.
Cells of N. eutropha N904 were harvested by
centrifugation, washed twice, and suspended in 0.9% NaCl. Cell
homogenates were prepared by passing the cell suspension
(1010 cells ml
1) through a French pressure
cell at 140 MPa or by sonification on ice for 15 to 30 min by using a
Biorupter apparatus. The protein concentrations of the crude extracts
were determined colorimetrically according to the method of Bradford
(13) as modified by Spector (48). Crude
extracts were adjusted to 3.0 mg of protein ml
1. The
samples were diluted (1:1) with 10 mM Tris-HCl buffer (pH 6.8)
containing 2% sodium dodecyl sulfate (SDS), 20% glycerol, 1%
2-mercaptoethanol, and 0.001% bromophenol blue and then solubilized for 15 min at room temperature. Samples (75 µl) were loaded onto lanes of 0.75-mm-thick SDS-polyacrylamide gels, prepared as described by Laemmli (36). The stacking and separating gels
contained 4 and 12% polyacrylamide, respectively. Electrophoresis was
performed at 80 V and 10°C by using a PROTEAN II Slab Cell (20 by 16 cm; Bio-Rad). After electrophoresis the gels were reversibly stained by
using the Zinc Stain & Destain Kit (Bio-Rad) to determine the position
of the 41-kDa protein. The protein bands were cut out of the gels. The
staining of the slices was removed, and the protein was electroeluted
from the gel at 60 mA for 6 h in an Electro-Eluter Model 422 (Bio-Rad). The protein was concentrated by lyophilization (Freezemobile
12; Virtis). Antiserum against this polypeptide was produced by Valbex
(Villeurbanne, France) in chickens. Injections of 50 µg of protein
were given at prescribed intervals.
For protein sequencing by Edman degradation, the 41-kDa protein was
isolated by a modified SDS-polyacrylamide gel electrophoresis
(PAGE).
In order to avoid N-terminal blockage the gel had been
pre-electrophoresed for 2 h, adding 0.07% sodium thioglycolate
to
the Laemmli running buffer. The separated proteins were electroblotted
(Pegasus; PHASE) onto a 0.2-µm-pore-size polyvinylidene
difluoride
membrane filter (Schleicher & Schuell), using the procedure
described
by Matsudaira (
37). The amino acid sequencing of
the isolated
protein was done by the Institute of Biology and Chemistry
of
Proteins (University of Lyon I, Villeurbanne, France). Protein
sequences were used to search for homologous proteins in the EMBL
and
SwissProt data banks (
http://www.ncbi.nlm.nih.gov/BLAST/)
(
2).
Immunoblotting.
Cells were harvested, and crude extracts
were prepared as described above. SDS-PAGE analyses were performed at
40 mA by using a Mini-PROTEAN II Cell (8 by 7.3 cm; Bio-Rad). The
separated proteins were electroblotted (Pegasus; PHASE) for 2 h at
0.8 mA per cm2 onto a cellulose nitrate membrane (pore
size, 0.2 µm; Schleicher & Schuell) using a discontinuous buffer
system (35). The membrane was then blocked for 1.5 h
in a phosphate-buffered saline (PBS) containing 1% bovine serum
albumin (BSA). The proteins on the nitrocellulose membrane were
incubated with antiserum (diluted 1:32,000 in PBS containing 0.05% BSA
and 0.025% Tween 20) overnight at room temperature. After two washes
with PBS, the proteins were incubated with biotin-conjugated secondary
antibodies (Biotrend, Cologne, Germany) diluted 1:30,000 in PBS
containing 0.05% BSA-0.025% Tween 20 for 1.5 h at room
temperature. The membrane was washed twice with PBS, and the proteins
were incubated with a streptavidin-biotinylated alkaline phosphatase
complex (diluted 1:3,000 in PBS containing 0.05% BSA and 0.025% Tween
20) for another 1.5 h. After two washes with 10 mM Tris-HCl (pH
8.6) containing 0.02% BSA and 0.05% Tween 20, the cellulose nitrate
membrane was incubated with a substrate solution containing 0.005%
5-bromo-4-chloro-3-indolyl-phosphate (BCIP), 0.001% 4-nitroblue
tetrazolium, 0.1 M NaHCO3, 0.05 M
Na2CO3, and 0.004 M MgCl2. The
enzymatic reaction was stopped by adding distilled water. A dense blue
color indicated a positive reaction. Each immunoblotting experiment was
reproduced at least three times. The membrane was scanned (ScanMagic
9636 S; Mustek), a densitogram of the lanes was performed, and the AmoB
was quantified using software program origin 4.0 (Microcal).
Determination of ammonia oxidation activity.
Exponentially
grown cells of N. eutropha N904 cultivated in
1-liter Erlenmeyer flasks were harvested by centrifugation, washed, and
resuspended in mineral medium. The ammonia oxidation activity of the
cells was reflected by the decrease in ammonia as well as by the
increase in nitrite concentration in suspensions of 5 × 107 cells per ml. The activities were determined as mean
values of three experiments. Ammonia and nitrite levels were measured
by high-pressure liquid chromatography (50).
 |
RESULTS |
Purification and identification of AmoB protein.
The N
terminus of the 41-kDa protein of N. eutropha N904,
separated by SDS-PAGE, was sequenced by Edman degradation (positions 3 to 24). The derived amino acid sequence was compared with the amino
acid sequences deduced from the amoB genes of N. eutropha Nm 57, since an amoB gene sequence of
N. eutropha N904 is not available yet. The AmoB subunit
of N. eutropha Nm 57 is encoded by two nearly identical
gene copies (amoB1 and amoB2, GenBank accession
numbers U51630 and U72670). The N terminus of the isolated 41-kDa
protein of N. eutropha N904 showed 82% amino acid
sequence identity to the deduced AmoB sequences of N. eutropha Nm 57 from positions 41 to 62 onwards (Fig.
1). The sequences AmoB1 and AmoB2 from
N. eutropha Nm 57 differ in positions 43 and 47, respectively, compared to the N-terminal sequence from N. eutropha N904 (positions 5 and 9). As a consequence, the AmoB sequence of N. eutropha N904 tallied only with one
amino acid of AmoB1 or AmoB2 of N. eutropha Nm 57, respectively. Mismatches were often represented by the amino acid
glycine (positions 14 and 17 of N. eutropha N904).

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FIG. 1.
Comparison of amino acid sequences of the isolated
41-kDa protein of N. eutropha N904 (a) and the deduced
amino acid sequences of AmoB1 (b) and AmoB2 (c) of N. eutropha Nm 57 encoded by the amoB genes. (The
SwissProt accession numbers for N. eutropha Nm 57 amoB1 and amoB2 are U51630 and U72670,
respectively.) The periods represent an identical match to the sequence
of the isolated 41-kDa protein of N. eutropha N904. The
space represents a gap among the sequences. The isolated 41-kDa protein
of N. eutropha N904 showed 82% (18 of 22) amino acid
sequence identity compared to both AmoB proteins of N. eutropha Nm 57.
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Specificity of the antibodies.
Polyclonal antibodies were
produced against the purified AmoB of N. eutropha N904.
The reactivity of the antibodies was tested by immunoblotting of crude
extracts of numerous ammonia oxidizers, including all described species
of the genus Nitrosomonas. All tested strains are listed in
Materials and Methods. The antibodies were highly specific for the
detection of 41-kDa proteins in cell extracts of the four genera of
ammonia oxidizers of the
-subclass of Proteobacteria
(Nitrosomonas, including Nitrosococcus mobilis, which belongs phylogenetically to Nitrosomonas;
Nitrosospira; Nitrosolobus; and
Nitrosovibrio). In six strains of ammonia oxidizers isolated
from building stones, strains which have been characterized as yet only
by their morphology, 41-kDa proteins were recognized as well. The
antibodies did not show any unspecific reactions with other proteins of
these crude extracts (Fig. 2). No
proteins were recognized in crude extracts of Nitrosococcus
oceani Nc 1 (Fig. 2) and Nitrosococcus halophilus Nc 4 (data not shown), which belong to the
-subclass of
Proteobacteria. Hence, the antiserum could be used to detect
AmoB in ammonia oxidizers of the
-subclass of
Proteobacteria including not-yet-described isolates, but not for the detection of AmoB in ammonia oxidizers of the
-subclass of
Proteobacteria.

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FIG. 2.
Immunoblot using antiserum recognizing the AmoB of
different ammonia-oxidizing bacteria. Lane A, N. eutropha N904; lane B, Nitrosovibrio sp. strain K7.1;
lane C, Nitrosospira sp. strain R6.2; lane D,
Nitrosococcus mobilis Nc 2; lane E, Nitrosolobus
multiformis, Nl 13; lane F, Nitrosococcus oceani Nc 4. Standard protein molecular masses are indicated on the right (in
kilodaltons). Crude extracts of cells were added to the gel at protein
amounts of 10 µg per lane.
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In order to prove the specificity of the antiserum, control experiments
were performed with pure cultures of the methane-oxidizing
bacteria
Methylococcus capsulatus Bath,
Methylomonas
methanica Oo52006, and
Methylocystis parvus 4a. The key
enzyme in CH
4 oxidation
of these organisms, the pMMO, was
shown to possess high sequence
similarities to the AMO. Furthermore,
the heterotrophic nitrifier
Paracoccus denitrificans 001 was
analyzed, since this organism
also contains an ammonia-oxidizing
system. In addition, immunoblot
analysis was carried out with several
other bacteria, such as
nitrite oxidizers and methylotrophic and
denitrifying bacteria.
The antiserum did not react with any of these
organisms.
Quantitative immunoblot analysis of the AmoB amount.
The AmoB
amount of total cellular protein of N. eutropha N904
was measured using immunoblot analysis of crude extracts with protein
amounts ranging from 0.25 to 16 µg (Fig. 3a and
b), which corresponded to 2.9 × 106 cells and 1.9 × 108 cells,
respectively. The protein coloration increased with the protein amount,
and a saturation curve was obtained. These data could be used to
determine the specific cellular amount of AmoB (Table
1). Purified AmoB ranging from 0.03 to
0.42 µg served as standards (Fig. 3c and d). By using standard growth
conditions (mineral medium with 10 mM ammonium), a cellular amount of
5.9% ± 1.8% AmoB was found in the total cell protein of
N. eutropha N904. As shown in Fig.
4, this cellular AmoB amount
depended on the ammonium concentration in the mineral medium. The
amount of AmoB increased to 14% ± 1.4% when the substrate
was reduced to 1 mM. When cells were grown with 100 mM ammonium, only a
low AmoB amount of 4% ± 0.8% was found.

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FIG. 3.
Coloration intensities of the AmoB after immunostaining
in correlation to the amount of total protein in N. eutropha N904 grown with 10 mM ammonium (a and b) and in
correlation to the amount of purified AmoB (c and d). The coloration
intensities obtained by immunoblotting (a and c) are plotted against
the amounts of total protein (b) and against the amounts of purified
AmoB (d). The values on the right of the immunoblots are molecular
masses (in kilodaltons).
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TABLE 1.
Specific AmoB amount in cells of N. eutropha N904 grown with 10 mM ammonium as measured by using
immunoblot analysisa
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FIG. 4.
Quantification of AmoB in crude extract of N. eutropha N904 grown with different ammonium concentrations. (a) An
immunoblot was performed using crude extracts containing 4 µg of
total protein. Lane A, cells grown with 1 mM; lane B, cells grown with
10 mM; lane C, cells grown with 100 mM ammonium. The values on the
right of the immunoblot are molecular masses (in kilodaltons). (b)
Decrease of specific AmoB amount of the total protein by increasing
ammonium concentrations in the mineral media. The error bars represent
the standard deviations for the average of three replicate
experiments.
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The AmoB amount increased when
N. eutropha N904 was
starved of ammonia. Cells, which did not receive ammonium for more than
60 days, contained 9.7% ± 0.9% AmoB (Fig.
5). That is nearly twice
the amount
compared to that found in active growing cells or cells
that had been
starved of ammonia for 20 days. The AmoB could even
be detected after 1 year of ammonia starvation. These results
did not correlate with the
ammonia oxidation activity. The highest
activity was found within cells
in the exponential growth phase
using standard cultivation conditions
(575 µmol of NH
4+ g of protein
1
h
1). The specific activity was reduced to 255 µmol of
NH
4+ g of protein
1
h
1 when cells were starved of ammonia for 1 month, a
level which
remained nearly constant during further starvation.
Experiments
with cells of
Nitrosomonas sp. strain Dave and
N. europaea Freitag
showed similar results (data not
shown).

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FIG. 5.
Quantification of AmoB in crude extract of starved cells
of N. eutropha N904. (a) Immunoblot was performed with
crude extracts containing 4 µg of total protein. Lane A, cells
ammonia starved for 1 day; lane B, cells ammonia starved for 29 days;
lane C, cells ammonia starved for 58 days; lane D, cells ammonia
starved for 129 days, and lane E, cells ammonia starved for 360 days.
The values on the right of the immunoblot are molecular masses (in
kilodaltons). (b) After different times of ammonia starvation the
specific AmoB percentage of the total protein amount increased. The
error bars represent the standard deviation for the average of three
replicate experiments.
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Mixotrophic growth of the bacteria with ammonia and organic N compounds
had no influence on the AmoB amount of the cells.
Cells of
N. eutropha N904, which were grown mixotrophically in
the presence of pyruvate, yeast extract, and peptone, as well
as
pyruvate or alanine, showed nearly the same AmoB amount as
lithoautotrophically grown
cells.
 |
DISCUSSION |
The isolated 41-kDa protein of N. eutropha N904
shows high sequence similarity to the sequences AmoB1 and AmoB2 of
N. eutropha Nm 57. The mismatches in positions 14 and
17 of the partially sequenced AmoB protein of N. eutropha N904 (Fig. 1) might be a contamination of glycine used in
the transfer buffer for blotting the protein on the membrane. The
amoB genes of N. eutropha Nm 57 encode
hydrophobic 37-amino-acid leader sequences (39) that was
not present in the isolated AmoB of N. eutropha N904.
Apparently, this part of the N terminus was removed during protein
processing. Nevertheless, the purified 41-kDa protein can be regarded
as the AmoB of N. eutropha N904. Sequence differences
in the AmoB peptides between N. eutropha N904 and
N. eutropha Nm 57 may be due to strain differences.
In this study, an antiserum against the AmoB was developed which
recognized the 41-kDa subunit of the AMO in crude extracts of
N. eutropha N904. It could be demonstrated that this
antiserum has a broad serological specificity for all tested ammonia
oxidizers of the
-subclass of Proteobacteria. Thus far,
only antibodies recognizing specific epitopes of the cell wall of
ammonia oxidizers have been described (43, 47, 55), and
these were limited in the application to specific serological groups
(8, 56). The AMO is a highly conserved enzyme in ammonia
oxidizers affiliated with the
-subclass of
Proteobacteria. Therefore, the broad serological specificity
of the antibodies against AmoB may be due to their 73% AmoB sequence
similarity (3). Thus, it seems likely that the antibodies
can be used for in situ detection of ammonia oxidizers of the
-subclass in natural bacterial communities. First, evidence is given
as the antibodies reacted with the AmoB in new strains of ammonia
oxidizers isolated from building stones. Recent studies also proved in
a similar approach that monoclonal antibodies recognizing the key
enzyme of nitrite oxidizers are a useful tool for microbial ecological
studies (1, 6).
In contrast, the antiserum did not react with the ammonia oxidizers
belonging to the
-subclass of Proteobacteria. This
might be due to the low similarities between the AmoB of these
bacteria to that of ammonia oxidizers belonging to the
-subclass of
Proteobacteria. The phylogenetically related pMMO of
methanotrophic bacteria also did not react with the antibodies. Indeed,
the amino acid sequence of the AmoB of Nitrosococcus oceani
(
-proteobacteria) shows higher similarity (50 to 52%) to the pMMO
sequence of Methylococcus capsulatus (
-proteobacteria)
than to the AmoB sequence (38 to 39%) of the ammonia oxidizers of the
-subclass of Proteobacteria (3).
The antibodies could be used to determine for the first time the amount
of AmoB in cells of N. eutropha N904. It was shown that
the total cell protein consisted of approximately 6% AmoB when cells
were grown using standard substrate conditions (mineral medium
containing 10 mM ammonium). During cell growth, the specific cellular
amount of the AmoB was regulated by the ammonium concentration in the
medium. When ammonium was limited, higher amounts of AmoB could be
detected in cells of N. eutropha N904 in comparison to cells grown with standard concentrations. At ammonia concentrations below the Km value of the AMO (1.8 mM)
(46), the low activity of the enzyme seemed to be
compensated for by high amounts of the key enzyme. At high substrate
concentrations the activity of the enzyme is maximal. Therefore, the
cells were able to grow, although the enzyme concentration was reduced.
Organic compounds had no influence on the AmoB amount in cells of
N. eutropha N904 as it was found for the nitrite
oxidizer Nitrobacter. In Nitrobacter spp. a
higher level of the nitrite oxidoreductase was observed in
mixotrophically growing cells compared to cells growing in mineral
medium (1).
Starved cells contained higher amounts of AmoB than actively growing
cells, although they possessed far less ammonia oxidation activity.
Previous studies also found considerable amounts of active AMO in
starved cells of N. europaea (40, 59).
Hence, our studies and these investigations indicate that the amount of
AMO does not correlate with the activity of ammonia oxidation in
Nitrosomonas. Although the AmoB was detected in high
concentrations in cells of N. eutropha N904,
N. europaea Freitag, and Nitrosomonas strain
Dave after 1 year of ammonia starvation and their AMO remained active,
the AMO seems not to be a constitutive enzyme. Sayavedra-Soto et al.
(44) found that the mRNA of the AMO in cells of
N. europaea was totally degraded a few hours after the
depletion of ammonia. Moreover, it was shown that the endogenous
respiration of N. cryotolerans cells decreased to
undetectable levels under starvation conditions (27).
Accordingly, the AMO seems to be strongly protected from degradation so
that the energy supply is ensured as soon as ammonia is available. The
increase of the AmoB amount in the cells during ammonia starvation
might be due to the decline of unprotected proteins.
Similar results were also reported for the second key enzyme of the
ammonia oxidation, the HAO. Using immunoblot analysis, the HAO level
remained constant within 81 days of ammonia starvation in cells of
N. europaea and a high amount of active HAO was
detected (40, 59), while the mRNA was degraded during
ammonia starvation (44).
This study demonstrated that the antibodies recognizing the AmoB could
be applied successfully for physiological studies. Cytological analyses
are in progress that will provide information about the localization of
the enzyme by immunogold and immunofluorescence labeling. If the
antibodies can be employed for isolation of the enzyme, there is even a
good prospect for a detailed biochemical characterization of the AmoB protein.
 |
ACKNOWLEDGMENTS |
This work was supported by a grant from the Deutscher
Akademischer Austauschdienst (DAAD, PROCOPE) and by the European Union (ENV4-CT98-0707).
We thank H.-P. Koops for contributing pure cultures of ammonia
oxidizers, S. Bartosch for technical assistance and comments on the
manuscript, and E. Spieck for the initiation of antibody development
and for scientific discussions.
 |
FOOTNOTES |
*
Corresponding author. Mailing address: Institut
für Allgemeine Botanik, Ohnhorststr. 18, D-22609 Hamburg,
Germany. Phone: 49-40-42816-426. Fax: 49-40-42816-400. E-mail:
pinck{at}mikrobiologie.uni-hamburg.de.
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Applied and Environmental Microbiology, January 2001, p. 118-124, Vol. 67, No. 1
0099-2240/01/$04.00+0 DOI: 10.1128/AEM.67.1.118-124.2001
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