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Appl Environ Microbiol, February 1998, p. 721-732, Vol. 64, No. 2
0099-2240/98/$04.00+0
Copyright © 1998, American Society for Microbiology. All rights reserved.
In Situ Gene Expression in Mixed-Culture Biofilms:
Evidence of Metabolic Interactions between Community Members
Søren
Møller,1
Claus
Sternberg,1
Jens Bo
Andersen,1
Bjarke Bak
Christensen,1
Juan Luis
Ramos,2
Michael
Givskov,1 and
Søren
Molin1,*
Department of Microbiology, The Technical
University of Denmark, DK-2800 Lyngby, Denmark,1
and
Department of Biochemistry and Molecular and Cellular
Biology of Plants, Estación Experimental del
Zaidín, Consejo Superior de Investagaciones
Científicas, Granada, Spain2
Received 21 April 1997/Accepted 3 November 1997
 |
ABSTRACT |
Microbial communities growing in laboratory-based flow chambers
were investigated in order to study compartmentalization of specific
gene expression. Among the community members studied, the focus was in
particular on Pseudomonas putida and a strain of an
Acinetobacter sp., and the genes studied are involved in the biodegradation of toluene and related aromatic compounds. The
upper-pathway promoter (Pu) and the
meta-pathway promoter (Pm) from the TOL plasmid
were fused independently to the gene coding for the green fluorescent
protein (GFP), and expression from these promoters was studied in
P. putida, which was a dominant community member. Biofilms
were cultured in flow chambers, which in combination with scanning
confocal laser microscopy allowed direct monitoring of promoter
activity with single-cell spatial resolution. Expression from the
Pu promoter was homogeneously induced by benzyl alcohol in
both community and pure-culture biofilms, while the Pm
promoter was induced in the mixed community but not in a pure-culture
biofilm. By sequentially adding community members, induction of
Pm was shown to be a consequence of direct metabolic interactions between an Acinetobacter species and P. putida. Furthermore, in fixed biofilm samples organism identity
was determined and gene expression was visualized at the same time by
combining GFP expression with in situ hybridization with
fluorescence-labeled 16S rRNA targeting probes. This combination of
techniques is a powerful approach for investigating structure-function
relationships in microbial communities.
 |
INTRODUCTION |
In nature most bacteria do not exist
as pure cultures, and significant proportions of all microorganisms are
associated with surfaces in complex multispecies communities called
biofilms (14). There are many examples of important
microbial processes that cannot be performed by a pure culture. For
example, anaerobic digestion of organic matter is believed to require
juxtaposition of syntrophic H2-producing acetogens and
H2-consuming methanogens (12, 33). Also, in the
process of nitrification the combined action of ammonia- and
nitrite-oxidizing bacteria (e.g., members of the genera
Nitrosomonas and Nitrobacter) is needed to
complete the oxidation of ammonia to nitrate (6, 28). The
two-member consortium "Chlorochromatium aggregatum" is an elegant
example of the sulfur cycle, in which sulfide-oxidizing phototrophic
bacteria are directly attached to the surface of a single central
sulfate- or sulfur-reducing bacterium. This association allows anoxic
photosynthesis by the phototroph to occur (42). Furthermore,
during degradation of many xenobiotic compounds, such as chlorinated
herbicides (31, 60), nitrate esters (45),
naphthalene derivatives (50), and alkylbenzene sulfonates
(27), the combined action of several species present in
bacterial communities enhances or is required for complete
mineralization of the compounds. Processes which cannot be performed
efficiently or which cannot be performed at all by a pure culture but
depend on the joint action of two or more bacterial species are termed
community level processes (7).
An important factor in understanding community level processes is the
relationship between structure and function in microbial communities.
Recent developments in bacterial rRNA-based phylogeny (57)
have allowed workers to design phylogenetic stains (16) based on fluorescence-labeled rRNA targeting probes. rRNA probes can be
used to identify and quantify phylogenetically defined groups of
organisms in complex mixtures; thus, the key players can be identified
and their population dynamics in a microbial community can be monitored
(4, 49, 52, 56). In addition, by using hybridization with
fluorescent probes, the cellular rRNA content can be quantified and the
growth rate (16, 38, 44, 56) or even the metabolic activity
(39) of a specific population in a community can be
estimated. By using scanning confocal laser microscopy (SCLM) the
three-dimensional structure or architecture (32) of a
community can be described, and by using fluorescent molecular probes
the extracellular polysaccharide composition and the heterogeneity with
respect to oxygen or pH within the microenvironments of a community can
be analyzed (8, 37). Furthermore, by using in situ
hybridization in combination with SCLM the spatial distribution of
organisms in bacterial communities has been visualized (39,
55). By using rRNA probes and SCLM in an investigation of the
architecture of granular sludge, workers have visualized the close
juxtaposition of syntrophic propionate-oxidizing bacteria and
H2-consuming methanogens (21), and the results suggested that there is a structure-function relationship during the
process of interspecies hydrogen transfer.
The next step in inferring structure-function relationships is to
determine the function of the bacteria in situ. One approach has been
to use microelectrodes to measure rates of microbial processes in
combination with a description of community structure. In the study of
Ramsing et al. (48), the presence of sulfate-reducing bacteria was found to be restricted to the anoxic layers. The use of
microsensors for nitrate in combination with rRNA probes for ammonia-
and nitrite-oxidizing bacteria showed that nitrification was restricted
to the top layers of a trickling filter biofilm. In these layers
ammonia and nitrite oxidizers were found in proximity to each other
(51).
A more direct approach for determining the function of an organism in
situ is to investigate its gene expression. This has been done by
identifying specific mRNAs in the pool of extracted mRNA
(43), and recently a method for detecting mRNAs in
single bacterial cells by an in situ PCR has been developed
(24). An alternative to mRNA detection is the use of genetic
reporters (lux, luc, gus, or
lacZ). In the field of environmental microbiology, such
systems have been used to study bacterial infection of root hairs
(25, 40) and surface regulation of alginate synthesis (15) and to monitor nitrogen or phosphate starvation
(29). However, these reporters are not easily compatible
with fluorescent in situ hybridization and SCLM. With the cloning and
heterologous expression of the gene for green fluorescent protein (GFP)
from Aequorea victoria (10) and subsequent
improvements (13, 22), a nearly ideal reporter for
fluorescence detection became available. GFP has been shown to be a
useful tool for monitoring bacterial gene expression (18,
54), as well as plasmid transfer (11, 20). It is
important to note that GFP is a very stable protein in the organisms
studied so far (10), and GFP expression thus reflects the
history of gene expression in the cell rather than expression at the
time of observation.
We have studied induction of the genes for the well-characterized TOL
pathway for toluene degradation (for a review see reference 35). In this pathway toluene degradation starts by
oxidation of the C-1 methyl group to yield benzoic acid (the upper
pathway), which is then further oxidized to catechol. The catechol then undergoes meta fission to produce a semialdehyde, which is
further transformed to Krebs cycle intermediates (the meta
pathway [61]). The genes for toluene degradation are
organized into two separate operons, and transcription is driven from
the Pu (upper) and Pm (meta)
promoters. The upper-pathway operon is induced by toluene and xylenes
and their alcohol derivatives (1), and this induction is
mediated by the effector-activated XylR protein (26)
together with the sigma factor RpoN (19). In Luria-Bertani
medium "exponential silencing" (catabolite repression) of
Pu has been observed, and RpoN is believed to function as
the sensor of the cellular physiological state (9). The
meta pathway is induced by benzoates (47), and
induction is mediated by the substrate-activated XylS protein (46). In addition, expression from the Pm
promoter can be switched on by upper-pathway substrates through a
cascade regulatory system (46).
The strategy used in the present investigation of specific gene
expression in a toluene-degrading mixed community biofilm was to create
genetic fusions between the relevant promoters (for expression of
catabolic genes) and the gfp gene, which allowed easy
microscopic monitoring at the level of single cells, followed by
introduction of the engineered strains into the microbial community.
 |
MATERIALS AND METHODS |
Strains, media, and cultivation of biofilms.
The biofilm
community used consisted of seven bacterial strains (Table
1), all isolated from a biofilter
treating toluene-containing waste gas (39). Biofilms were
cultivated as mixtures of the seven isolates in rectangular
four-channel flow cells (60) with individual channel
dimensions of 1 by 4 by 40 mm and were maintained on FAB medium [1 mM
MgCl2, 0.1 mM CaCl2, 0.01 mM Fe-EDTA (catalog no. E6760; Sigma, St. Louis, Mo.), 0.15 mM
(NH4)SO4, 0.33 mM
Na2HPO4, 0.2 mM KH2PO4,
0.5 mM NaCl]; 0.26 mM benzyl alcohol (Merck, Darmstadt, Germany) was
used as the sole carbon source. Before each experiment the tubing was
autoclaved, and after the flow system was assembled, the system was
sterilized by pumping a 0.5% (wt/vol) hypochlorite solution into the
system and leaving it there overnight. The next day the system was
flushed with 2 liters of sterile water before the medium was pumped
into the system. During growth of biofilms the medium was pumped
through the flow cells at a constant rate of 0.2 mm/s (approximately 2 ml/h) by using a peristaltic pump (model 205S; Watson Marlow, Calmouth,
Cornwall, England). Flow cells were inoculated with mixtures of
overnight cultures of the seven isolates grown in Luria-Bertani medium
in the following ratios: Pseudomonas putida R1, 0.2 ml;
Acinetobacter sp. strain C6, 2 ml; and D8, smo111, smo113,
smo115, and smo127, 1 ml each. The mixtures were sonicated (Branson
Ultrasonics Corp. [Danbury, Conn.] sonifier) for 1 min at an output
control setting of 3 and a duty cycle setting of 40%. A 0.2-ml portion
of the culture was injected into each channel, and the flow cell was
turned upside down. After 1 h the flow was resumed.
Plasmids.
The gene encoding the GFP was obtained as an
enhanced version, gfp-mut3b (13). The
gfp-mut3b gene was PCR amplified as a 0.7-kb
SphI-HindIII fragment and inserted into a
pUC18-NotI-based cloning vector, resulting in pJBA25. The
sequence was changed during the PCR so that the gfp-mut3b
contained an arginine residue instead of a serine residue at position
2. This was done to introduce a SphI site in the start codon
of gfp-mut3b. The gfp-mut3b gene was inserted the
optimal distance downstream from the ribosome binding site of phage T5
(RBSII), which ensured that efficient translation occurred.
Translational stop codons in all three reading frames were inserted
downstream of the HindIII site in pJBA25, and two strong
transcriptional terminators, T0 (from phage lambda) and
T1 (from the rrnB operon of Escherichia
coli), were inserted downstream of the translational stop codons.
The NotI fragment from pJBA25 containing RBSII,
gfp-mut3b, the translational stop codons, and the
transcriptional terminators were inserted into the NotI
sites of pCNB1 and pCNB3 (17), creating the fusions Pm::gfp-mut3a and
Pu::gfp-mut3a, respectively. pCNB1 and pCNB3 are
based on universal mini-Tn5 delivery plasmid pUT described by Herrero et al. (23), and pCNB1 contains in addition to
the Pm promoter the xylS activator gene, whereas
pCNB3 contains in addition to the Pu promoter the
xylR activator gene. In summary, the transposon carried on
pJBA30 contained the regulator gene xylR, which is required
for activation of Pu, and a npt gene which confers kanamycin resistance, while the transposon carried on pJBA26
contained the regulator gene xylS, which is required for activation of Pm, and the Sm/Sp gene, which confers
streptomycin resistance. When this system was used, the transposons
carried on pJBA30 (Pu::gfp) and pJBA26
(Pm::gfp) were capable of transposing into the
chromosome of the recipient strain while not cotransposing the
transposase gene, which stably integrated the reporter construct into
the chromosome of the recipient. The Pu::gfp and
Pm::gfp reporters were inserted into the
chromosome of P. putida R1 by using triparental mating as
described previously (11). The resulting insertants were
screened on 5 mM benzyl alcohol-FAB medium plates containing 25 µg
of streptomycin per ml (pJBA30) or on 2% sodium citrate-5 mM
3-methylbenzoate (3MB)-FAB plates containing 25 µg of kanamycin per
ml (pJBA25). GFP-positive colonies were detected by using an Axioplan
epifluorescence microscope (Carl Zeiss, Oberkochen, Germany) equipped
with a 100-W HBO bulb for excitation, and GFP-specific light was
observed by using the filter for fluorescein (filter set 10; Carl
Zeiss). GFP-positive clones grew on FAB medium supplemented with
toluene vapor or 5 mM benzyl alcohol or on 5 mM sodium benzoate.
Sequencing of 16S rRNA.
Sequencing was performed with a
model 373A automatic DNA sequencer (Applied Biosystems, Foster City,
Calif.) directly by using PCR products generated from chromosomal
DNA extracts and the manufacturer's recommendations. The following
primers were used: 11F (5'-GTTTGATC[A/C]TGGCTCAGATTG-3'), 344R (5'-CCCCACTGCTGCCTCCCGT-3'), 515R
(5'-GTATTACCGCGGC[G/T]GCTGGCAC-3'), 922R
(5'-GCTTGTGCGGGCCCCCGTC-3'), 1101R
(5'-GACAAGGGTTGCGCTCGTT-3'),1389R (5'-GTGACGGGCGGTGTGTACAAG-3'), and 1465R
(5'-CCCCAGTCATGAATCATAAAGTGGT-3') (the
suffix F indicates the forward direction, and the suffix R indicates
the reverse direction). The initial phylogenetic analysis of the
sequenced strains was performed by using the online services of the
Ribosomal Database Project (SIMILARITY_RANK [34]). In addition, sequences were investigated for the phylogenetic signature sequences described by Woese (57) which allow
differentiation of the major groups of the Proteobacteria.
Oligonucleotide probes.
For hybridizations probe EUB338,
specific for the domain Bacteria (3), and probe
PP986, specific for P. putida subgroup A 16S rRNA
(39), were used. Probes for the toluene-degrading isolates
Acinetobacter sp. strain C6 and strain D8 were designed on
the basis of sequence information (Table
2). The specificities of ACN449 and
D8_647 were tested by using previously published sequences and the
CHECK_PROBE program from The Ribosomal Database Project
(34). The probes were tested with the organisms in the community and were specific for their target organisms (data not shown). Oligonucleotide probes labeled with fluorescein isothiocyanate, CY3, or CY5 were purchased from Hobolth DNA Syntese (Hillerød, Denmark).
Hybridization of hydrated biofilm samples with cells expressing
GFP.
Biofilms were fixed in a freshly made 3% paraformaldehyde
solution by pumping this solution through the flow cells with attached biofilms at a rate of 0.8 mm/s for about 5 min. The flow cells were
then kept at 4°C for 1 h. The flow cells were then washed with
phosphate-buffered saline for 10 min (flow rate, 0.5 mm/s) before each
channel was embedded in 20% acrylamide (200:1
acrylamide-bisacrylamide; Sequagel; National Diagnostics, Atlanta,
Ga.). The embedding was done in the following way. One milliliter of
20% (wt/vol) acrylamide was mixed with 8 µl of
N,N,N',N'-tetramethylethylendiamine
and 20 µl of 1% ammonium persulfate (International Biotechnologies Inc., New Haven, Conn.). This allowed about 2 min before the acrylamide solidified, and approximately 0.5 ml was pumped into the channel at a
flow rate of 0.8 mm/s. During this procedure the biofilm structure
could be monitored microscopically, and when the procedure was
performed carefully, we found that the method was nondestructive and
preserved the biofilm in its native hydrated state.
After fixation and embedding the acrylamide block with biofilm was
placed on a six-well hybridization slide (Novakemi ab,
Enskede, Sweden)
and equilibrated for 15 min with hybridization
buffer containing 20 or
30% formamide (Table
2). Then 30 µl of
the hybridization mixture (20 or 30% formamide [Table
2], 0.9
M NaCl, 100 mM Tris [pH 7.2],
0.1% [wt/v] sodium dodecyl sulfate)
containing approximately 75 ng
of probe was added to each hybridization
well. The cells were incubated
with hybridization solution for
3 h at 37°C in a moisture
chamber. For washing, 50-µl portions
of washing solutions were added
to each well. First, the acrylamide
blocks were washed with washing
solution (20 or 30% formamide
[Table
2], 0.9 M NaCl, 100 mM Tris
[pH 7.2], 0.1% sodium dodecyl
sulfate) for 40 min at 37°C, and
then they were washed for another
40 min with washing solution II (0.1 M Tris [pH 7.2], 0.9 M NaCl)
at 37°C, before they were finally
rinsed twice with 50 µl of distilled
water. The acrylamide blocks
were mounted in 2× SlowFade phosphate-buffered
saline-based antifade
solution (Molecular Probes, Eugene, Oreg.).
Fixation, embedding,
hybridization, and the microscopic investigation
were performed on the
same day since we observed that the GFP
signal degenerated rapidly.
Microscopy and image analysis.
All microscopic observations
and image acquisition were performed with a model TCS4D confocal
microscope (Leica Lasertechnik GmbH, Heidelberg, Germany) equipped with
an argon-krypton laser and three detectors for simultaneous monitoring
of fluorescein isothiocyanate, CY3, and CY5. In addition, a reflection
detector for acquiring bright-field images was installed.
Multichannel simulated fluorescence projection (SFP) images were
generated by using IMARIS software (Bitplane AG, Zürich,
Switzerland) running on a Indigo 2 workstation (Silicon Graphics
Inc.,
Mountain View, Calif.). Images were processed for display
by using
Photoshop (Adobe, Mountain View, Calif.).
Spatial profiles of organisms and gene expression were estimated by
measuring the area covered by either hybridization or
the GFP signal
(represented by different colors) in a series of
three-channel optical
sections by using simple thresholding. Before
thresholding, images were
preprocessed in IMARIS; the background
was removed by using lowpass
filtering and background subtraction,
and a final correction for loss
of intensity from deeper layers
was performed by using the emission
attenuation or gamma correction
algorithms of IMARIS. Thresholding was
performed on the processed
images by using the HIPS (
30)
image analysis package. Line profiles
were generated by using NIH Image
(software available at ftp site
zippy.nimh.nih.gov).
Nucleotide sequence accession numbers.
The sequences
determined in this study have been deposited in the EMBL, GenBank, and
DDBJ nucleotide sequence databases under accession no. Y11464
(Acinetobacter sp. strain C6) and Y11465 (isolate D8).
 |
RESULTS |
Model community.
Previous studies of the kinetics of a
laboratory scale waste gas biofilter indicated that P. putida, which constituted only 4% of the biofilm population, as
judged by activity, was a dominant member of the biofilm community and
was responsible for 65% of the toluene removed by the biofilter
(39). Therefore, P. putida was chosen as the main
organism to investigate gene expression in a more controlled model
system. The toluene-degrading community used as a model system in the
present study consisted of seven strains (Table 1), three
toluene-degrading strains and four nondegrading strains. All of the
organisms were isolated from the natural toluene-degrading biofilter
community (39), and all of the strains were characterized by
examining them repeatedly after plating. Moreover, we thought that it
was important to include even strains unable to degrade toluene in the
model system since they were present in the original bioreactor
community. We chose benzyl alcohol as the substrate for ease of
operation of the flow system. The P. putida strain used in
the mixed community, P. putida R1, has been shown to degrade toluene through a pathway which is similar to that encoded by the TOL
plasmid but which has restricted substrate specificity, so that
m-xylene and p-xylene are not growth substrates
due to blockage of the catabolic pathway at the level of the first
enzyme of the meta-cleavage pathway (unpublished data). To
study the expression of genes involved in toluene degradation in our
artificial seven-strain community, we investigated the expression of
two TOL plasmid-derived promoters, Pu (upper pathway) and
Pm (meta pathway). We constructed two
mini-Tn5-based transposons (see Materials and Methods) and
inserted the fusions Pu::gfp and
Pm::gfp together with the genes encoding their
regulators (xylR and xylS, respectively) into the
chromosome of P. putida R1. The resulting strains grew at
rates identical to the rate of growth of the parent strain in minimal
medium liquid cultures supplied with either citrate or benzyl alcohol
as the carbon and energy source (data not shown). In
citrate-supplemented medium there was no induced expression of
fluorescence, whereas addition of benzyl alcohol resulted in induction
of fluorescence in the Pu::gfp strain and addition
of 3MB (a well-known inducer of the Pm promoter
[1]) resulted in induction of fluorescence in the
Pm::gfp strain; these observations showed that the
two promoters behaved as expected with respect to their modes of gene
expression control (the Pu promoter is inducible with
toluene or benzyl alcohol but not with benzoate, and the Pm
promoter in our construct is inducible only with benzoate [see
below]).
Expression of Pu and Pm in pure-culture
biofilms.
In order to analyze the gene expression patterns of the
two P. putida R1 variants harboring the TOL promoters fused
to the gfp gene, flow chambers with each of the variants in
monoculture were established with a substrate based on benzyl alcohol
as the only carbon source. Biofilms were grown on benzyl alcohol for 1 day, and monitoring of GFP expression showed that the Pu
promoter was homogeneously induced in a pure-culture biofilm containing the relevant strain (Fig. 1A and B). In
contrast, the GFP expression in a pure-culture biofilm containing
P. putida R1 (Pm::gfp) grown on benzyl
alcohol for 1 day showed that the Pm promoter was not induced in P. putida R1 except for strong induction in a
few, very bright cells (Fig. 1C and D). Such bright cells were always present, but at a low frequency (<0.01%). The degrees of expression from the Pu::gfp and Pm::gfp
fusions in the biofilm populations were quantified by performing an
image analysis with series of optical sections that covered the
thicknesses of the biofilms. The Pu promoter was induced in
all cells, while the Pm promoter was not.

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FIG. 1.
Online monitoring of Pu and Pm
expression in pure-culture biofilms after 1 day of biofilm formation.
(A and B) Biofilms formed by P. putida R1
(Pu::gfp). All cells are shown in the reflection
image in panel A, and the GFP fluorescence in panel B shows that
Pu expression was homogeneous. (C and D) Biofilms formed by
P. putida R1 (Pm::gfp). All cells are
shown in the reflection image in panel C, and the GFP fluorescence in
panel D shows that there was no GFP expression except for that of a few
bright cells, showing that Pm was not induced in the
pure-culture biofilm. (E and F) Induction of Pm by 3MB.
P. putida R1 (Pm::gfp) was grown for 1 day on benzyl alcohol, and then 5 mM 3MB was added to the medium. The
reflection image (E) recorded on day 2 shows all cells, and the GFP
signal from the same cells (F) reveals induction of Pm. The
arrows indicate the direction of flow.
|
|
To further confirm these observations, a
Pm::lacZ
fusion was introduced into
P. putida R1, and the

-galactosidase activity
was monitored in cells growing with toluene,
benzyl alcohol, or
benzoate as the carbon source. High-level enzyme
activity (8,000
Miller units) was expressed in cells cultivated with
benzoate;
however, in cells growing on toluene or benzyl alcohol the
enzyme
activity was about 30 times lower. These results suggest that
in
P. putida growing on toluene or benzyl alcohol, no
significant
accumulation of benzoate takes place. When biofilms of
P. putida R1 (
Pm::gfp) were grown on
benzyl alcohol and 5 mM 3MB was added
to the medium after 1 day of
growth, induction of
Pm::gfp was
observed in all
cells on day 2 (Fig.
1E and F). This showed that
the
Pm
promoter was indeed inducible in
P. putida R1 pure-culture
biofilms.
Expression of Pu and Pm in mixed-culture
biofilms.
Expression from the Pu and Pm
promoters was studied in the mixed community described above by
monitoring the GFP levels in living biofilms. Flow cells were
inoculated with the seven-member community or with communities in which
wild-type P. putida R1 was replaced by either P. putida R1 (Pu::gfp) or P. putida
R1 (Pm::gfp). GFP expression from Pu
and GFP expression from Pm were monitored by using SCLM.
Figures 2A and B illustrate GFP
expression in a biofilm formed by the community containing P. putida R1 (Pu::gfp) after 1 day of growth and
show that, as was observed with the single-strain biofilm described
above, the Pu promoter was induced in the majority of the
cells. The asterisk in Fig. 2A indicates a colony of cells that did not
express GFP. The spherical microcolony morphology was typical of
colonies formed by Acinetobacter sp. strain C6 (data not
shown) and showed that both strain R1 and strain C6 were present in the
biofilm.

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FIG. 2.
Online monitoring of GFP expression from Pu
and Pm in communities after 1 day of biofilm formation. (A
and B) Pu expression in the biofilm formed by the community
containing P. putida R1 (Pu::gfp). Note
the spherical Acinetobacter sp. strain C6 colony (indicated
by an asterisk) in the reflection image (A). The GFP fluorescence (B),
visualized as an SFP, shows that Pu was constitutively
expressed in the majority of the cells. (C through E) Expression of
Pm in the biofilm formed by the community containing
P. putida R1 (Pm::gfp). All cells
(including the Acinetobacter sp. strain C6 colony indicated
with an asterisk) are shown in the reflection image (C), and GFP
fluorescence (D) shows the lack of homogeneous Pm expression
on day 1. Panel E shows GFP expression quantified along the line shown
in panel D and shows that GFP fluorescence increased as cells got
closer to the Acinetobacter sp. strain C6 microcolony. The
pixel intensities were measured from the maximum projection image (data
not shown). (F and G) Biofilm formation by the wild-type community. The
reflection image (F) and the SFP (G) show that no cells expressed GFP
in the negative control. The asterisk indicates the spherical
microcolonies of Acinetobacter sp. strain C6, and the arrows
show the direction of flow.
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|
P. putida R1 (
Pm::gfp) was also grown
with the six other strains in a mixed community, and expression from
the
Pm promoter
was monitored (Fig.
2C to E). However,
Pm expression was not homogeneous
(as also observed in the
monoculture biofilm), but very heterogeneous
activity was observed
after 1 day of biofilm formation. The reflection
image in Fig.
2C shows
a spherical
Acinetobacter sp. strain C6
microcolony, and the
SCLM image of the GFP signal (Fig.
2D) shows
that the
Acinetobacter sp. strain C6 colony was surrounded by
P. putida R1 (
Pm::gfp) cells expressing
GFP. The GFP expression
patterns indicated that cells close to the
Acinetobacter sp. strain
C6 microcolony were highly induced.
In contrast, cells farther
away from the
Acinetobacter sp.
strain C6 microcolony were only
weakly induced or expressed background
levels, results similar
to the results observed in the single-strain
biofilm (Fig.
1C
and D). The gradient in gene expression could be
further illustrated
by quantifying the GFP signal along the line on the
image in Fig.
2D. The plot in Fig.
2E shows that higher GFP expression
levels
(i.e., higher pixel intensities) occurred in cells located near
the
Acinetobacter sp. strain C6 microcolony. The background
signal
was recorded by using the biofilm formed by the wild-type
community.
A large
Acinetobacter sp. strain C6 microcolony
was observed in
the reflection image (Fig.
2F), and only weak
autofluorescence
was detected in the SCLM image (Fig.
2G), showing that
there was
no green fluorescence from the negative control. Thus, the
GFP
signals observed in situ indicated that there was expression from
the
Pu and
Pm promoters.
The pattern of induction for the
Pm promoter in the presence
of the other strains in the community was analyzed further. When
P. putida R1 (
Pm::gfp) pure-culture
biofilms were grown for 1
day and then
Acinetobacter sp.
strain C6 was introduced, strong
induction of the
Pm
promoter in
P. putida R1 was observed on day
2 (Fig.
3). The other five community members
became established
in the
P. putida R1 biofilms in very low
numbers and were not
able to cause induction of
Pm (Table
3). This indicated that
in the community
studied, only
Acinetobacter sp. strain C6 caused
induction
of the
Pm promoter in
P. putida R1. Our data also
indicate
(Table
3) that the interaction between
P. putida R1
and
Acinetobacter sp. strain C6 was not restricted to
biofilm growth, but also occurred
in liquid culture.

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|
FIG. 3.
Addition of Acinetobacter sp. strain C6 to a
P. putida R1 (Pm::gfp) biofilm. All
cells are shown in the reflection image (A), and the GFP expression (B)
shows that Pm was induced by the presence of
Acinetobacter sp. strain C6. The asterisk indicates a
spherical colony of Acinetobacter sp. strain C6, and the
arrow indicates the direction of flow.
|
|
Time course of Pm induction.
To illustrate the
development of induction of the Pm promoter over time, a
series of low-magnification images are shown in Fig.
4. At day 1 induction was very
heterogeneous, and Pm was most strongly induced in P. putida R1 cells located close to Acinetobacter sp.
strain C6 microcolonies (Fig. 4A and B), as shown above. The heterogeneous induction patterns observed on day 2 (Fig. 4C and D),
with induced regions occurring as bands of induction parallel to the
direction of flow, suggested that the inducing agent was able to
diffuse in the biofilm. On day 3 the induction patterns for
Pm in the biofilm had become more uniform (Fig. 4E and F), further suggesting that the inducing agent accumulated in the biofilm
over time, which resulted in more complete induction of Pm
in older biofilms.

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FIG. 4.
Time course of GFP expression by P. putida R1
(Pm::gfp) in the community. (A and B) Lack of
homogeneous expression of Pm::gfp on day 1. All
cells are shown in the reflection image (A), and an optical section
obtained 5 µm from the substratum shows the GFP expression (B). The
asterisks indicate spherical microcolonies of Acinetobacter
sp. strain C6. (C and D) Pm expression patterns on day 2. The reflection image (C) and an optical section of GFP expression
obtained 5 µm from the substratum (D) show that induction occurred in
bands parallel to the direction of flow. (E and F) Pm
expression on day 3. The reflection image (E) shows all of the cells,
and an optical section of the GFP fluorescence obtained 5 µm from the
substratum (F) shows more homogeneous induction of Pm on day
3, indicating that the inducing agent accumulated in the biofilm. The
arrows indicate the direction of flow.
|
|
Spatial distribution of organisms and gene expression.
The
spatial distribution of community members and simultaneous
visualization of gene expression were studied by combining GFP
expression and hybridization with 16S rRNA targeting probes. Figure
5A shows a three-dimensional
representation of the organism distribution in a 3-day-old biofilm
formed by the community containing P. putida R1
(Pu::gfp). Two probes were used, and P. putida R1 was hybridized with PP986 (blue) and
Acinetobacter sp. strain C6 was hybridized with ACN449
(red). Figure 5B shows an overlay of the GFP signal that was
simultaneously recorded in the green channel during scanning. The image
is interpreted in the following way. P. putida R1
(Pu::gfp) expressing GFP is both blue and green and appears cyan. Acinetobacter sp. strain C6 not expressing
GFP is unchanged and appears red. Expression of
Pu::gfp was quantified by using image analysis,
and Fig. 6A shows the spatial
distribution of Pu expression in the community and shows
that most P. putida R1 cells expressed GFP from the
Pu promoter throughout the biofilm (between 80 and 100% of
the area covered by the hybridization signal was also covered by GFP
fluorescence [Fig. 6A]). The spatial distribution of the dominant
organisms in the biofilm was also quantified. Figure 6A shows that
Acinetobacter sp. strain C6 was the dominant organism at the
substratum level (~55% areal coverage), whereas P. putida
R1 dominated the outermost layers of the biofilm (~100% areal
coverage).

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FIG. 5.
Spatial distribution of organisms and gene expression in
the community. The dominant organisms in the community were targeted by
hybridization. (A) Dual hybridization of Acinetobacter sp.
strain C6 (red) and P. putida R1 (blue) in the community
containing P. putida R1 (Pu::gfp) on
day 3. (B) Overlay of the GFP fluorescence (green) expressed from the
Pu promoter. Cells that stained both blue (hybridization)
and green (GFP expression) appear cyan. (C and D) Expression from
Pm in the community containing P. putida R1
(Pm::gfp) grown for 3 days. Panel C shows a colony
of Acinetobacter sp. strain C6 (red) surrounded by P. putida R1 (Pm::gfp) cells expressing GFP
(cyan), and panel D shows surface coverage by Acinetobacter
sp. strain C6 (red), with P. putida R1 distributed over the
surface. These colonies expressed GFP (cyan). P. putida R1
was hybridized with PP986 labeled with CY5, Acinetobacter
sp. strain C6 was hybridized with ACN449 labeled with CY3, and GFP was
sampled in the green channel. The images shown are SFPs with
x and z projections shown on the sides of the
images; these projections provide extended focus images for the regions
between the marks. The arrows indicate the direction of flow.
|
|

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|
FIG. 6.
Profiles of organisms and gene expression in the
biofilm. (A) Expression from the Pu promoter. Symbols: ,
percentage of the P. putida R1 population in the biofilm
expressing Pu::gfp; , percentage of cells in
the biofilm that were P. putida R1 cells; , percentage of
cells that were Acinetobacter sp. strain C6 cells. (B)
Expression from the Pm promoter. Symbols: , percentage of
the P. putida R1 population in the biofilm expressing
Pm::gfp; , percentage of cells in the biofilm
that were P. putida R1 cells; , percentage of cells that
were Acinetobacter sp. strain C6 cells. Percentages were
calculated by determining the ratio between areas covered by the
respective fluorescent signals in a series of multicolor optical
sections. All bacteria were hybridized by using EUB338 labeled with
CY5, P. putida R1 was hybridized with PP986 labeled with CY3
or CY5, Acinetobacter sp. strain C6 was hybridized with
ACN449 labeled with CY3, and GFP was sampled in the green channel.
Error bars indicate ±1 standard deviation. The profiles are the
results obtained after we averaged the data for five independent
positions in the biofilm.
|
|
The spatial distribution of
Pm expression in the context of
the community was also determined. Figure
5C shows a spherical
microcolony of
Acinetobacter sp. strain C6 entirely
surrounded
by
P. putida R1 cells, all of which showed
expression from the
Pm promoter. Figure
5D shows a portion
of the biofilm where the
surface was entirely covered by
Acinetobacter sp. strain C6 and
colonies of
P. putida R1 expressing
Pm::gfp were distributed
over
the surface without any apparent spatial interaction with
Acinetobacter sp. strain C6. This may indicate that direct
contact between the
two organisms (as suggested by Fig.
5B and C) is
not necessary
for induction of
Pm. The distribution of
Pm expression in the
biofilm was quantified, and Fig.
6B
shows
Pm expression relative
to the position of the dominant
members of the community. On day
3 all of the
P. putida R1
cells were expressing GFP from the
Pm promoter throughout
the biofilm (~100% areal coverage) (Fig.
6B),
and no spatial
gradients in expression from
Pm were observed.
The presence of D8 and the presence of the four non-toluene-degrading
strains in the community could be confirmed by probing
(by using D8_647
and EUB338, respectively). However, these organisms
were present in
only low numbers (data not shown). This confirms
that
P. putida R1 and
Acinetobacter sp. strain C6 were the
dominant
organisms in the biofilm community.
 |
DISCUSSION |
Two of the seven organisms present in the community studied here,
P. putida R1 and Acinetobacter sp. strain C6,
were the focus of our study because they are present in fairly high
numbers and because they interact. Both of these strains are able to
degrade benzyl alcohol, and we have evidence (data not shown) that they both have degradative pathways similar to the degradative pathway located on the TOL plasmid. The two pathways are, however, not identical to the TOL plasmid pathway, and they are probably not identical in the two strains either. The differences occur at the level
of substrate specificities and have been observed in hybridization
experiments performed with probes derived from the TOL plasmid
(unpublished data). The gene expression analysis described here took
advantage of the existence of cloned promoters and regulatory genes
derived from the TOL plasmid.
In biofilms expression from the Pu promoter was continuously
induced in the mixed-strain community, as well as in pure culture. Benzyl alcohol is an inducer of the Pu promoter
(1), and the homogeneous expression from Pu
probably reflects the presence of the substrate in all
microenvironments of the community during the spatial development of
the biofilm, as well as during the temporal development of the biofilm.
In contrast, expression from the Pm promoter in the biofilms
was more complex. In a pure-culture biofilm the Pm promoter
was not induced by the benzyl alcohol added, probably because the cascade induction system could not operate since the xylS
gene used in the designed fusions between the Pm promoter
and gfp lacked the promoter that normally responds to benzyl
alcohol coupled with XylR (17, 46) and because the benzoate
formed in the cells from benzyl alcohol metabolism was quickly removed
and did not accumulate in sufficient amounts to induce detectable
levels of GFP production. In the early stages of biofilm development, induction of the Pm promoter was heterogeneous, and addition
of the other community members to a P. putida R1 monoculture
biofilm showed that Pm was induced only by the presence of
Acinetobacter sp. strain C6. A simple explanation is that
the Pm inducer, benzoate, leaked from
Acinetobacter sp. strain C6 into the surrounding medium. Although both organisms carry the genes for a TOL-like degradation pathway for benzyl alcohol, the differences between them could easily
result in different rates of conversion of the different metabolites,
resulting in accumulation of benzoate in only one of them. Leakage of
metabolites out of growing cells is known to occur; for example, during
degradation of simple substrates, such as glucose, catabolites (i.e.,
acetate) can leak in significant amounts from E. coli
(5). The excreted benzoate can then diffuse into the medium
and be available as a substrate and/or inducer for other cells. This
hypothesis is supported by the induction patterns observed. The
Pm promoter was initially induced only in P. putida R1 cells located close to Acinetobacter
colonies, whereas in later stages of biofilm development the
Pm promoter was induced in all P. putida R1
(Pm::gfp) cells, which probably reflected
accumulation of benzoate throughout the biofilm. Since Pu
promoter expression was continuously induced, P. putida R1 cells in the community could be expected to grow on a mixture of benzyl
alcohol and benzoate. Alternatively, the proximity of Acinetobacter cells could change the physiology of the
P. putida R1 cells in such a way that intracellular benzoate
would accumulate in adequate amounts to cause sufficient induction of
the Pm promoter. In any case, the data present genetic
evidence that metabolic interactions occur between community members in
an aerobic degradative biofilm community.
Sequential metabolism of degradation products is well-known in many
anaerobic community microbial processes. For example, the layered
structure of granular sludge (21, 33) suggests that the
spatial distribution of organisms reflects the positions of the
organisms in the food chain. Thermodynamic considerations suggest that
close juxtaposition of H2 producers and consumers occurs,
and this suggestion has been supported by gas metabolism evidence
(12, 53), as well as by direct microscopic observations (21, 53), which further support the significance of specific spatial arrangements during anaerobic degradation of organic matter. In
addition, similar structures have been observed in granular sludge from
different reactors (21, 33, 53), and this similarity is
probably a consequence of tight coupling and strong interdependence in
the anaerobic degradation process.
There are also many examples of aerobic processes in which different
bacterial species are interdependent. As mentioned above, degradation
of many xenobiotic compounds requires the action of a bacterial
consortium and does not occur in a pure culture. Microbial associations
in such degradative communities are less well-studied. Wolfaardt et al.
(60) observed the development of structured consortia in a
biofilm community growing on a chlorinated hydrocarbon (diclofob-methyl). The structure of the consortia rapidly degenerated when the biofilm was irrigated with labile carbon sources, indicating that there was a high degree of substrate-dependent coupling in the
system (60). Furthermore, diclofob-methyl was shown to
accumulate in the extracellular polysaccharide of certain community
members (58) and to bind to sites of preferred chemistry
(59), suggesting that there were regions where specific
activities occurred in the community. In a separate investigation
performed with a different community and a different hydrocarbon,
Møller et al. (37) observed a similar substrate-dependent
biofilm architecture. Taken together, these data suggest that the
degradative biofilms studied are examples of tightly coupled and highly
organized bacterial communities (36).
In contrast, the structural interactions in the benzyl
alcohol-degrading biofilm investigated here seemed to be rather loose, although the architecture of the biofilm had characteristic features. The two dominant organisms appeared to have different niches in the
biofilm, with Acinetobacter sp. strain C6 primarily
attaching to the substratum and P. putida R1 being the
dominant organism in the outermost layers of the biofilm (Fig. 6). SCLM
images of the three-dimensional structure of the community revealed the heterogeneous architecture of the biofilm; in some regions
Acinetobacter sp. strain C6 seemed to colonize P. putida R1 colonies (Fig. 5A), in other regions P. putida R1 seemed to colonize Acinetobacter sp. strain
C6 colonies (Fig. 5C), and in yet other regions the two organisms
seemed to grow independently (Fig. 5D). This suggests that close
physical association between the two organisms was not essential for
biofilm proliferation.
The loose architectural features described above probably reflect the
fact that both P. putida R1 and Acinetobacter sp.
strain C6 are able to degrade benzyl alcohol in pure culture (Table 3), which is not the case with the highly organized communities mentioned above. In spite of the loose organization, metabolic interaction between the two community members was observed and seemed to occur in
all regions in the mature biofilm independent of the local architecture. In addition, the interaction was observed in liquid culture (Table 3). The importance of the metabolic interaction remains
to be determined, but measurements of biofilm thickness indicated that
there was synergy between community members; the seven-strain community
formed biofilm thicker than the biofilms consisting only of P. putida R1 and Acinetobacter sp. strain C6, which were
thicker than the pure-culture biofilms (39a). Our observations indicate that bacteria living in an apparently loosely organized microbial community may cooperatively interact with each
other and consequently that community level processes (7) are not restricted to highly organized microbial communities.
 |
ACKNOWLEDGMENTS |
This work was supported by the Danish Biotechnology Program.
Palle Hobolth, Hobolth DNA Syntese (Hillerød, Denmark), is
acknowledged for sequencing the 16S rRNA. Brendan Cormack, Rafael Valdivia, and Stanley Falkow are acknowledged for the gift of the
gfp-mut3 allele used in this study.
 |
FOOTNOTES |
*
Corresponding author. Mailing address: Department of
Microbiology, Building 301, The Technical University of Denmark,
DK-2800 Lyngby, Denmark. Phone: 45 45 25 25 13. Fax: 45 45 88 73 28. E-mail: sm{at}im.dtu.dk.
 |
REFERENCES |
| 1.
|
Abril, M.,
C. Michan,
K. N. Timmis, and J. L. Ramos.
1989.
Regulator and enzyme specificities of the TOL plasmid-encoded upper pathway for degradation of aromatic hydrocarbons and expansion of the substrate range of the pathway.
J. Bacteriol.
171:6782-6790[Abstract/Free Full Text].
|
| 2.
|
Alm, E. W.,
D. B. Oerther,
N. Larsen,
D. A. Stahl, and L. Raskin.
1996.
The oligonucleotide probe database.
Appl. Environ. Microbiol.
62:3557-3559[Medline].
|
| 3.
|
Amann, R. I.,
L. Krumholz, and D. A. Stahl.
1990.
Fluorescent-oligonucleotide probing of whole cells for determinative, phylogenetic, and environmental studies in microbiology.
J. Bacteriol.
172:762-770[Abstract/Free Full Text].
|
| 4.
|
Amann, R. I.,
W. Ludwig, and K. H. Schleifer.
1995.
Phylogenetic identification and in situ detection of individual microbial cells without cultivation.
Microbiol. Rev.
59:143-169[Abstract/Free Full Text].
|
| 5.
|
Andersen, K. B., and K. von Myenburg.
1980.
Are growth rates of Escherichia coli in batch cultures limited by respiration?
J. Bacteriol.
144:114-123[Abstract/Free Full Text].
|
| 6.
|
Bock, E., and H.-P. Koops.
1992.
The genus Nitrobacter and related genera, p. 2302-2309. In
A. Balows, H. G. Trüper, M. Dworkin, W. Harder, and K.-H. Schleifer (ed.), The procaryotes, 2nd ed.
Springer-Verlag, New York, N.Y.
|
| 7.
|
Caldwell, D. E., and J. W. Costerton.
1996.
Are bacterial biofilms constrained to Darwin's concept of evolution through natural selection?
Microbiol. SEM
12:347-358.
|
| 8.
|
Caldwell, D. E.,
D. R. Korber, and J. R. Lawrence.
1992.
Confocal laser microscopy and digital image analysis in microbial ecology.
Adv. Microb. Ecol.
12:1-67.
|
| 9.
|
Cases, I.,
V. de Lorenzo, and J. Pérez-Martin.
1996.
Involvement of sigma-54 in exponential silencing of the Pseudomonas putida TOL plasmid Pu promoter.
Mol. Microbiol.
19:7-17[Medline].
|
| 10.
|
Chalfie, M.,
Y. Tu,
G. Euskirchen,
W. W. Ward, and D. C. Prasher.
1994.
Green fluorescent protein as a marker for gene expression.
Science
263:802-805[Abstract/Free Full Text].
|
| 11.
|
Christensen, B. B.,
C. Sternberg, and S. Molin.
1996.
Bacterial plasmid conjugation on semi-solid surfaces monitored with the green fluorescent protein (Gfp) from Aequorea victoria as a marker.
Gene
173:59-65[Medline].
|
| 12.
|
Conrad, R.,
T. L. Phelps, and J. G. Zeikus.
1985.
Gas metabolism evidence in support of the juxtaposition of hydrogen-producing and methanogenic bacteria in sewage sludge and lake sediments.
Appl. Environ. Microbiol.
50:595-601[Abstract/Free Full Text].
|
| 13.
|
Cormack, B. P.,
R. H. Valdivia, and S. Falkow.
1996.
FACS-optimized mutants of the green fluorescent protein (GFP).
Gene
173:33-38[Medline].
|
| 14.
|
Costerton, J. W.,
K. J. Cheng,
G. G. Geesey,
T. I. Ladd,
J. C. Nickel,
M. Dasgupta, and J. T. Marrie.
1987.
Bacterial biofilms in nature and disease.
Annu. Rev. Microbiol.
42:435-464.
|
| 15.
|
Davies, D. G.,
A. M. Chakrabarty, and G. G. Geesey.
1993.
Exopolysaccharide production in biofilms: substratum activation of alginate gene expression by Pseudomonas aeruginosa.
Appl. Microbiol. Biotechnol.
59:1181-1186.
|
| 16.
|
DeLong, E. F.,
G. S. Wickham, and N. R. Pace.
1989.
Phylogenetic stains: ribosomal RNA-based probes for identification of single cells.
Science
243:1360-1362[Abstract/Free Full Text].
|
| 17.
|
de Lorenzo, V.,
S. Fernández,
M. Herrero,
U. Jakubzik, and K. N. Timmis.
1993.
Engineering of alkyl- and haloaromatic-responsive gene expression with mini-transposons containing regulated promoters of biodegradative pathways of Pseudomonas.
Gene
130:41-46[Medline].
|
| 18.
|
Dhandayuthapani, S.,
L. E. Via,
C. A. Thomas,
P. M. Horowitz,
D. Deretic, and V. Deretic.
1995.
Green fluorescent protein as a marker for gene expression and cell biology of mycobacterial interactions with macrophages.
Mol. Microbiol.
17:901-912[Medline].
|
| 19.
|
Dixon, R.
1986.
The xylABC promoter from Pseudomonas putida TOL plasmid is activated by nitrogen regulatory gene in Escherichia coli.
Mol. Gen. Genet.
203:129-136[Medline].
|
| 19a.
| Eberl, L. Personal communication.
|
| 20.
|
Eberl, L.,
R. Schulze,
A. Ammendola,
O. Geisenberger,
R. Erhart,
C. Sternberg,
S. Molin, and R. I. Amann.
1997.
Use of green fluorescent protein as a marker for ecological studies of activated sludge communities.
FEMS Microbiol. Lett.
149:77-83.
|
| 21.
|
Harmsen, H. J. M.,
H. M. P. Kengen,
A. D. L. Akkermans,
A. J. M. Stams, and W. M. De Vos.
1996.
Detection and localization of syntrophic propionate-oxidizing bacteria in granular sludge by in situ hybridization using 16S rRNA-based oligonucleotide probes.
Appl. Environ. Microbiol.
62:1656-1663[Abstract].
|
| 22.
|
Heim, R.,
A. B. Cubitt, and R. Y. Tsien.
1995.
Improved green fluorescence.
Nature
373:663-664[Medline].
|
| 23.
|
Herrero, M.,
V. de Lorenzo, and K. N. Timmis.
1990.
Transposon vectors containing non-antibiotic resistance selection markers for cloning and stable chromosomal insertion of foreign genes in gram-negative bacteria.
J. Bacteriol.
172:6557-6567[Abstract/Free Full Text].
|
| 24.
|
Hodson, R. E.,
W. A. Dustman,
R. P. Garg, and M. A. Moran.
1995.
In situ PCR for visualization of microscale distribution of specific genes and gene products in prokaryotic communities.
Appl. Environ. Microbiol.
61:4074-4082[Abstract].
|
| 25.
|
Hurek, T.,
B. Reinhold-Hurek,
M. van Montagu, and E. Kellenberger.
1994.
Root colonization and systemic spreading of Azoarcus sp. strain BH71 in grasses.
J. Bacteriol.
176:1913-1923[Abstract/Free Full Text].
|
| 26.
|
Inouye, S.,
A. Nakazawa, and T. Nakazawa.
1983.
Molecular cloning of regulatory gene xylR and operator-promoter regions of the xylABC and xylDEFG operons of the TOL plasmid.
J. Bacteriol.
155:1192-1199[Abstract/Free Full Text].
|
| 27.
|
Jiménez, L.,
A. Breen,
N. Thomas,
T. W. Federle, and G. S. Sayler.
1991.
Mineralization of linear alkylbenzene sulfonate by a four-member aerobic bacterial consortium.
Appl. Environ. Microbiol.
57:1566-1569[Abstract/Free Full Text].
|
| 28.
|
Koops, H.-P., and U. C. Möller.
1992.
The lithotrophic ammonia-oxidizing bacteria, p. 2625-2637. In
A. Balows, H. G. Trüper, M. Dworkin, W. Harder, and K.-H. Schleifer (ed.), The procaryotes, 2nd ed.
Springer-Verlag, New York, N.Y.
|
| 29.
|
Kragelund, L.,
B. Christoffersen,
F. J. de Bruijn, and O. Nybroe.
1995.
Isolation of lux reporter gene fusions in Pseudomonas fluorescens DF57 inducible by nitrogen or phosphorus starvation.
FEMS Microbiol. Ecol.
17:95-106.
|
| 30.
|
Landy, M. S.,
Y. Cohen, and G. Sperling.
1984.
HIPS: a Unix-based image processing system.
Comput. Vision Graphics Image Process.
25:331-347.
|
| 31.
|
Lappin, H. M.,
M. P. Greaves, and J. H. Slater.
1985.
Degradation of the herbicide mecoprop [2-(2-methyl-4-chlorophenoxy)propionic acid] by a synergistic microbial community.
Appl. Environ. Microbiol.
49:429-433[Abstract/Free Full Text].
|
| 32.
|
Lawrence, J. R.,
D. R. Korber,
B. D. Hoyle,
J. W. Costerton, and D. E. Caldwell.
1991.
Optical sectioning of microbial biofilms.
J. Bacteriol.
173:6558-6567[Abstract/Free Full Text].
|
| 33.
|
MacLeod, F. A.,
S. R. Guiot, and J. W. Costerton.
1990.
Layered structure of bacterial aggregates produced in an upflow anaerobic sludge bed and filter reactor.
Appl. Microbiol. Biotechnol.
56:1598-1607.
|
| 34.
|
Maidak, B. L.,
G. J. Olsen,
N. Larsen,
R. Overbeek,
M. J. McCaughey, and C. R. Woese.
1997.
The RDP (Ribosomal Database Project).
Nucleic Acids Res.
25:109-110[Abstract/Free Full Text].
|
| 35.
|
Marqués, S., and J. L. Ramos.
1993.
Transcriptional control of the Pseudomonas putida TOL plasmid catabolic pathway.
Mol. Microbiol.
9:923-929[Medline].
|
| 36.
|
Molin, S., and J. Molin.
1997.
CASE: complex adaptive systems ecology.
Adv. Microb. Ecol.
15:27-80.
|
| 37.
|
Møller, S.,
D. R. Korber,
G. M. Wolfaardt,
S. Molin, and D. E. Caldwell.
1997.
Impact of nutrient composition on a degradative biofilm community.
Appl. Environ. Microbiol.
63:2432-2438[Abstract].
|
| 38.
|
Møller, S.,
C. S. Kristensen,
L. K. Poulsen,
J. M. Carstensen, and S. Molin.
1995.
Bacterial growth on surfaces: automated image analysis for quantification of growth rate-related parameters.
Appl. Environ. Microbiol.
61:741-748[Abstract].
|
| 39.
|
Møller, S.,
A. R. Pedersen,
L. K. Poulsen,
E. Arvin, and S. Molin.
1996.
Activity and three-dimensional distribution of toluene-degrading Pseudomonas putida in a multispecies biofilm assessed by quantitative in situ hybridization and scanning confocal laser microscopy.
Appl. Environ. Microbiol.
62:4632-4640[Abstract].
|
| 39a.
| Nielsen, A. T., and S. Møller. Unpublished
data.
|
| 40.
|
O'Kane, D. J.,
W. L. Lingle,
J. E. Wampler,
M. Legocki,
R. P. Legocki, and A. A. Szalay.
1988.
Visualization of bioluminescence as a marker of gene expression in rhizobium-infected soybean root nodules.
Plant Mol. Biol.
10:387-399.
|
| 41.
|
Pedersen, A. R.
1996.
.
Biological removal of toluene in waste gas reactors. Ph.D. thesis.
Institute of Environmental Science and Engineering, The Technical University of Denmark, Lyngby.
|
| 42.
|
Pfenning, N.
1980.
Syntrophic mixed cultures and symbiotic consortia with phototrophic bacteria: a review, p. 127-131. In
G. Gottschalk, N. Pfenning, and H. Werner (ed.), Anaerobes and anaerobic infections.
Gustav Fisher Verlag, Stuttgart, Germany.
|
| 43.
|
Pichard, S. L., and J. H. Paul.
1991.
Detection of gene expression in genetically engineered microorganisms and natural phytoplankton populations in the marine environment by mRNA analysis.
Appl. Environ. Microbiol.
57:1721-1727[Abstract/Free Full Text].
|
| 44.
|
Poulsen, L. K.,
G. Ballard, and D. A. Stahl.
1993.
Use of rRNA fluorescence in situ hybridization for measuring the activity of single cells in young and established biofilms.
Appl. Environ. Microbiol.
59:1354-1360[Abstract/Free Full Text].
|
| 45.
|
Ramos, J. L.,
A. Haïdour,
E. Duque,
G. Piñar,
V. Calvo, and J. M. Olivia.
1996.
Metabolism of nitrate esters by a consortium of two bacteria.
Nat. Biotechnol.
14:320-322.
[Medline] |
| 46.
|
Ramos, J. L.,
N. Mermod, and K. T. Timmis.
1987.
Regulatory circuits controlling transcription of the TOL plasmid operon encoding meta-cleavage pathway for degradation of alkylbenzoates by Pseudomonas.
Mol. Microbiol.
1:293-300[Medline].
|
| 47.
|
Ramos, J. L.,
A. Stolz,
W. Reineke, and K. N. Timmis.
1986.
Altered effector specificities in regulators of gene expression: TOL plasmid xylS mutants and their use to engineer expansion of the range of aromatics degraded by bacteria.
Proc. Natl. Acad. Sci. USA
83:8467-8471[Abstract/Free Full Text].
|
| 48.
|
Ramsing, N. B.,
M. Kühl, and B. B. Jørgensen.
1993.
Distribution of sulfate-reducing bacteria, O2, and H2S in photosynthetic biofilms determined by oligonucleotide probes and microelectrodes.
Appl. Environ. Microbiol.
59:3840-3849[Abstract/Free Full Text].
|
| 49.
|
Raskin, L.,
L. K. Poulsen,
D. R. Noguera,
B. E. Rittmann, and D. A. Stahl.
1994.
Quantification of methanogenic groups in anaerobic biological reactors by oligonucleotide probe hybridization.
Appl. Environ. Microbiol.
60:1241-1248[Abstract/Free Full Text].
|
| 50.
|
Rozgaj, R., and M. Glancer- oljan.
1992.
Total degradation of 6-aminonaphthalene-2-sulphonic acid by a mixed culture consisting of different bacterial genera.
FEMS Microbiol. Ecol.
86:229-235.
|
| 51.
|
Schramm, A.,
L. H. Larsen,
N. P. Revsbech,
N. B. Ramsing,
R. I. Amann, and K. H. Schleifer.
1996.
Structure and function of a nitrifying biofilm as determined by in situ hybridization and the use of microelectrodes.
Appl. Environ. Microbiol.
62:4641-4647[Abstract].
|
| 52.
|
Stahl, D. A.,
B. Flesher,
H. R. Mansfield, and L. Montgomery.
1988.
Use of phylogenetically based hybridization probes for studies of ruminal microbial ecology.
Appl. Environ. Microbiol.
54:1079-1084[Abstract/Free Full Text].
|
| 53.
|
Thiele, J. H.,
M. Chartrain, and J. G. Zeikus.
1988.
Control of interspecies electron flow during anaerobic digestion: role of floc formation in syntrophic methanogenesis.
Appl. Environ. Microbiol.
54:10-19[Abstract/Free Full Text].
|
| 54.
|
Valdivia, R. H., and S. Falkow.
1996.
Bacterial genetics by flow cytometry: rapid isolation of Salmonella typhimurium acid-inducible promoters by differential fluorescence induction.
Mol. Microbiol.
22:367-378[Medline].
|
| 55.
|
Wagner, M.,
R. I. Amann,
P. Kämpfer,
B. Assmus,
A. Hartmann,
P. Hutzler,
N. Springer, and K. H. Schleifer.
1995.
Identification and in situ detection of gram-negative filamentous bacteria in activated sludge.
Syst. Appl. Microbiol.
17:405-417.
|
| 56.
|
Wallner, G.,
R. Erhart, and R. I. Amann.
1995.
Flow cytometric analysis of activated sludge with rRNA-targeted probes.
Appl. Environ. Microbiol.
61:1859-1866[Abstract].
|
| 57.
|
Woese, C. R.
1987.
Bacterial evolution.
Microbiol. Rev.
51:221-271[Free Full Text].
|
| 58.
|
Wolfaardt, G. M.,
J. R. Lawrence,
J. V. Headly,
R. D. Robarts, and D. E. Caldwell.
1994.
Microbial exopolymers provide a mechanism for bioaccumulation of contaminants.
Microb. Ecol.
27:279-291.
|
| 59.
| Wolfaardt, G. M., J. R. Lawrence, R. D. Robarts, and D. E. Caldwell. Unpublished data.
|
| 60.
|
Wolfaardt, G. M.,
J. R. Lawrence,
R. D. Robarts,
S. J. Caldwell, and D. E. Caldwell.
1994.
Multicellular organization in a degradative biofilm community.
Appl. Environ. Microbiol.
60:434-446[Abstract/Free Full Text].
|
| 61.
|
Worsey, M. J., and P. A. Williams.
1975.
Metabolism of toluene and xylenes by Pseudomonas putida (arvilla) mt-2: evidence for a new function of the TOL plasmid.
J. Bacteriol.
124:7-13[Abstract/Free Full Text].
|
Appl Environ Microbiol, February 1998, p. 721-732, Vol. 64, No. 2
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-
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-
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-
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-
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[Abstract]
[Full Text]
-
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[Abstract]
[Full Text]
-
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65: 3056-3063
[Abstract]
[Full Text]
-
Kang, Y., Saile, E., Schell, M. A., Denny, T. P.
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65: 2356-2362
[Abstract]
[Full Text]
-
Unge, A., Tombolini, R., Mølbak, L., Jansson, J. K.
(1999). Simultaneous Monitoring of Cell Number and Metabolic Activity of Specific Bacterial Populations with a Dual gfp-luxAB Marker System. Appl. Environ. Microbiol.
65: 813-821
[Abstract]
[Full Text]
-
DuTeau, N. M., Rogers, J. D., Bartholomay, C. T., Reardon, K. F.
(1998). Species-Specific Oligonucleotides for Enumeration of Pseudomonas putida F1, Burkholderia sp. Strain JS150, and Bacillus subtilis ATCC 7003 in Biodegradation Experiments. Appl. Environ. Microbiol.
64: 4994-4999
[Abstract]
[Full Text]
-
Christensen, B. B., Sternberg, C., Andersen, J. B., Eberl, L., Møller, S., Givskov, M., Molin, S.
(1998). Establishment of New Genetic Traits in a Microbial Biofilm Community. Appl. Environ. Microbiol.
64: 2247-2255
[Abstract]
[Full Text]