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Applied and Environmental Microbiology, January 2008, p. 294-299, Vol. 74, No. 1
0099-2240/08/$08.00+0 doi:10.1128/AEM.01806-07
Copyright © 2008, American Society for Microbiology. All Rights Reserved.
In Situ Activity of Suspended and Immobilized Microbial Communities as Measured by Fluorescence Lifetime Imaging
Petr Walczysko,1,
Ute Kuhlicke,1
Sabine Knappe,2,
Christiana Cordes,2,
and
Thomas R. Neu1*
Department of River Ecology, Helmholtz Centre for Environmental Research-UFZ, Magdeburg, Germany,1
Hochschule Magdeburg-Stendal (FH), Magdeburg, Germany2
Received 3 August 2007/
Accepted 24 October 2007

ABSTRACT
In this study, the feasibility of fluorescence lifetime imaging
(FLIM) for measurement of RNA:DNA ratios in microorganisms was
assessed. The fluorescence lifetime of a nucleic acid-specific
probe (SYTO 13) was used to directly measure the RNA:DNA ratio
inside living bacterial cells. In vitro, SYTO 13 showed shorter
fluorescence lifetimes in DNA solutions than in RNA solutions.
Growth experiments with bacterial monocultures were performed
in liquid media. The results demonstrated the suitability of
SYTO 13 for measuring the growth-phase-dependent RNA:DNA ratio
in
Escherichia coli cells. The fluorescence lifetime of SYTO
13 reflected the known changes of the RNA:DNA ratio in microbial
cells during different growth phases. As a result, the growth
rate of
E. coli cells strongly correlated with the fluorescence
lifetime. Finally, the fluorescence lifetimes of SYTO 13 in
slow- and fast-growing biofilms were compared. For this purpose,
biofilms developed from activated sludge were grown as autotrophic
and heterotrophic communities. The FLIM data clearly showed
a longer fluorescence lifetime for the fast-growing heterotrophic
biofilms and a shorter fluorescence lifetime for the slow-growing
autotrophic biofilms. Furthermore, starved biofilms showed shorter
lifetimes than biofilms supplied with glucose, indicating a
lower RNA:DNA ratio in starved biofilms. It is suggested that
FLIM in combination with SYTO 13 represents a useful tool for
the in situ differentiation of active and inactive bacteria.
The technique does not require radioactive chemicals and may
be applied to a broad range of sample types, including suspended
and immobilized microorganisms.

INTRODUCTION
In situ activity measurement represents an ongoing issue in
various areas of applied and environmental microbiology. As
early as 1985, Staley and Konopka reflected on different techniques
employed to study microbial activity of single bacterial cells
versus that of the bacterial community(
36). In the meantime,
several studies compared the results of different techniques
for measuring microbial activity (
3,
21,
33,
35,
36,
40). The
major techniques comprise metabolism of radiolabeled substances,
tetrazolium reduction (
5,
9,
35,
39), and bromodeoxyuridine
incorporation in DNA (
1,
2,
12,
37). The most frequently used
techniques are the ones using radioactive compounds either as
a labeled nucleotide ([H
3]thymidine) (
34) or as a labeled carbon
substrate (e.g., [H
3]acetate). An elegant technique of activity
measurement with simultaneous phylogenetic identification is
fluorescent in situ hybridization combined with microautoradiography,
which is becoming a widely used technique in different areas
of microbiological research (
6,
11,
14,
20,
28-
32,
43). Fluorescent
in situ hybridization-microautoradiography samples are analyzed
by confocal laser scanning microscopy (CLSM) running the instrument
in both the fluorescent mode ("fluorochrome" emission of gene
probe) and the reflection mode ("radioactive" signal of silver
grains). CLSM is also well established as an in situ technique
for studying microbial communities, especially bioaggregates
and biofilms, without any fixation and embedding (
18,
24). A
relatively new technique for characterization of microbial communities
is laser scanning microscopy with two-photon excitation (2P-LSM).
2P-LSM takes advantage of infrared excitation with a pico- or
femtosecond pulsed laser source. So far, two-photon instruments
have been used in only a few microbiological studies, e.g.,
studies of dense oral biofilms (
42), marine stromatolites (
15),
assessment of fluorochromes for biofilm examination (
22), differentiation
of cyanobacteria and eukaryotic algae in phototrophic biofilms
(
27), and spatial distribution of zinc in microbial biofilms
(
13). A comparison of one-photon versus two-photon laser scanning
techniques and their application in biofilm research has been
discussed recently (
25). Both CLSM and 2P-LSM are techniques
recording the emission intensities of fluorochromes. However,
the intensity is affected by several parameters, such as laser
intensity, fluorochrome concentration, absorption, quenching,
scattering, etc. Nevertheless, excited fluorochromes can deliver
two pieces of information, first an intensity signal and second
a lifetime signal. Fluorescence lifetime imaging microscopy
(FLIM) is an emerging technique, and its potential applications
have been discussed in several review articles (
4,
7,
8). In
a first microbiological application, FLIM was employed to measure
pH gradients in densely grown artificial biofilms (
42). The
applicability of two-photon excitation using two-photon intensity
and two-photon lifetime imaging in microbial ecology has been
reported as well (
26).
One commercially available FLIM technique measures the fluorescence lifetime by means of time-correlated single photon counting. The technique is based on a pulsed laser light source, e.g., a two-photon infrared laser, the detection time of photons, and the buildup of photon distribution versus time across the whole measurement period. This information is recorded at every single pixel of the image. From the photon distribution over time, the fluorescence decay curve can be recorded. The decay curve is then fitted to an exponential decay in order to determine the lifetime. Using this information, a color-coded fluorescence lifetime image can be calculated (10).
In this study, we employed FLIM as a tool for measuring microbial activity. The different levels of activity were determined by employing a nucleic acid-specific fluorochrome and its lifetime signal in dependency on binding to different types of nucleic acids. The basic idea is to take advantage of the fact that in actively growing bacteria, there is a higher concentration of RNA than in inactive bacteria. Consequently, the ratio of the two lifetimes, RNA:DNA, can be used as a measure in order to identify active and inactive bacterial cells. For this purpose, experimental systems at various levels of complexity were employed. Initial measurements were done with purified nucleic acids in solution, and then pure liquid bacterial cultures were analyzed at the single-cell level; finally, multispecies heterotrophic and chemoautotrophic biofilms were examined.

MATERIALS AND METHODS
Nucleic acid solutions.
tRNA from
Escherichia coli strain W (Sigma-Aldrich, St. Louis,
MO) was solved in TE buffer (100 mM TRIS, 10 mM EDTA, pH 8)
at a final concentration of 3,770 µg/ml. DNA from
E. coli strain B (Sigma-Aldrich) was solved in TE buffer (100 mM TRIS,
10 mM EDTA, pH 8) at a final concentration of 31 µg/ml.
The size of
E. coli DNA was studied by using agarose gel electrophoresis
and turned out to be >3,000 bp. In addition, DNA from the
slow-growing BNC1 strain (
17) was isolated using the DNeasy
tissue kit (QIAGEN, Hilden, Germany). DNA purified by this procedure
was typically up to 50 kb in size, with fragments of 30 kb predominating
(DNeasy Tissue Handbook).
Pure culture studies.
Escherichia coli strain K-12 (JM 83, no. 3947; German Collection of Microorganisms and Cell Cultures [DSMZ], Braunschweig, Germany) was grown in liquid LB medium at 37°C. For subculturing, 1 ml of an overnight culture was inoculated in 200 ml of medium in 500-ml Erlenmeyer flasks and shaken at 130 rpm until the culture was in the stationary phase. The cell number and concentration were established microscopically using a Thoma chamber (Hecht, Sondheim, Germany). During the growth curve of the bacteria, 1 ml of the culture was sampled every 30 or 45 min for subsequent FLIM measurements.
µ computation.
For each time point in the growth curves of bacterial monocultures, the growth rate (µ) was computed from the increase/decrease of the cell density to the next-nearest-neighbor points. The growth rate at time point t2 (µ) was obtained as follows. First, from the cell density at time t2 (cd2) and the cell density at the previous time point, t1 (cd1), the growth rate (µ1/2) was calculated according to the following equation: µ1/2 = [ln(cd2) – ln(cd1)]/(t2 – t1). Then, from the cell density at time t2 (cd2) and the cell density of the following time point t3 (cd3), the growth rate (µ2/3) was calculated. The final growth rate at time point t2 was obtained as the average of the two growth rates of µ1/2 and µ2/3.
Biofilm studies.
Biofilms were grown in rotating annular reactors on polycarbonate or glass slides (19, 23). Sewage sludge taken from a municipal wastewater treatment plant (Hildesheim, Germany) was used as an inoculum. Chemoautotrophic biofilms were cultivated in SI-N1 trace element solution (0.5 g Na2EDTA, 3 g FeSO4·7H2O, 0.3 g Na2MoO4·2H2O, 0.2 g CuSO4·5H2O in 1,000 ml) with 1 g liter–1 MgSO4 and 0.4 g liter–1 CaCl2. A substrate load based on a biofilm surface area of 1.5 or 3 g m–2 day–1 ammonium (NH4+) and 1.5 g m–2 day–1 hydrogen carbonate (HCO3–) was used. For cultivation of heterotrophic biofilms, SL 6 trace element solution (0.3 g H3BO3, 0.13 g CoCl2, 0.014 g CuCl2·2H2O, 0.015 g MnSO4, 0.031 g Na2MoO4·2H2O, 0.01 g NiCl2·6H2O, 0.056 g ZnSO4·7H2O in 1,000 ml) with 1 g liter–1 MgSO4, 0.4 g liter–1 CaCl2, 1 g liter–1 NaNO3, and a substrate load of 1.5 g m–2 day–1 glucose was employed. The biofilm samples for FLIM were taken at days 11, 30, and 68 for both heterotrophic and autotrophic biofilms. Autotrophic biofilms were additionally sampled at day 106.
Fluorescence staining.
The nucleic acid-specific fluorochrome SYTO 13 (Molecular Probes, Eugene, OR) was used in all experiments. The samples were stained with SYTO 13 for 5 min in the dark at room temperature and at a final concentration of 10 µM in TE buffer.
Microscopy and FLIM device.
Laser scanning microscopy was done with a TCS SP1 in combination with an upright microscope (Leica, Mannheim, Germany). The system was controlled by the Leica Confocal Software, version 2.5, build 1104. Images of samples were recorded using 63x 1.2-numerical-aperture and 63x 0.9-numerical-aperture water immersion/immersible lenses, respectively. For two-photon excitation, the setup was equipped with a triple-laser system consisting of two laser diode bars, a Millennia Vs continuous-wave pump laser, and a tunable mode-locked Ti/Sapphire Tsunami laser with the midwave mirror set (Spectra Physics, Mountain View, CA). A wavelength of 800 nm was used for two-photon excitation of SYTO 13. The fluorescence emission of SYTO 13 was detected in the range of 400 to 800 nm. The SPC-730 module working on a time-correlated single-photon counting principle and the SPC-730 software, version 8.5, were available for detection of time-resolved fluorescence (Becker & Hickl, Berlin, Germany). FLIM signals were detected using a PMH-100 detector for photon counting (Hamamatsu, Hamamatsu City, Japan) mounted to the RLD port (nondescanned detector) of the laser scanning microscope. Standard recording time for lifetime imaging was 60 s.
Image analysis.
In a first step, the computation of fluorescence lifetimes and digital image analysis of FLIM images was performed using the SPC Image software, version 2.84 (Becker & Hickl). Then, the images were exported into the ImageJ software program (NIH; [http://rsb.info.nih.gov/ij/]). ImageJ was used with a self-written plugin for further analysis of the FLIM images. No background correction was performed, since the background fluorescence from the cultured strains and the autotrophic biofilms was found to be negligible (data not shown). In the bacterial pure culture experiments, each bacterium was manually selected with the region-of-interest (ROI) tool and the average fluorescence lifetime in nonzero pixels of this region was taken. For measurements in nucleic acid solutions, the average fluorescence lifetime from the whole image was evaluated in the case of tRNA and DNA from the BNC1 strain. In the case of DNA from E. coli, the precipitated DNA fibrils were chosen as the ROI and evaluated. In the biofilm experiments, ROIs were drawn around the characteristic spherical colonies of the autotrophic biofilms. In parallel, the average fluorescence lifetime from the whole image was evaluated.
Statistical analysis.
The correlation between groups was proven by using the Spearman rank order correlation test. Differences between the groups was proven by using the unpaired t test (to compare two groups) or one-way analysis of variance followed by Dunn's method (to compare >2 groups). If the data were not normally distributed, the Mann-Whitney rank sum test (to compare 2 groups) or the Kruskal-Wallis analysis of variance on ranks (to compare >2 groups) was applied. The significance level in all tests was a P value of <0.05. Results are given as means ± standard deviations unless stated otherwise.

RESULTS
Experiments with DNA/tRNA solutions.
Fluorescence lifetimes of SYTO 13 in
E. coli DNA and tRNA solutions
and their mixtures were measured. This should simulate the situation
in the living cell, where both nucleic acids are present. Thus,
after staining with SYTO 13, the average fluorescence lifetime
of SYTO 13-DNA complexes and SYTO 13-RNA complexes was obtained.
The average fluorescence lifetime from 256-by-256 pixel images
were computed for tRNA as well and the tRNA/DNA mixture. In
the case of pure DNA, the average fluorescence lifetime in the
precipitates seen in the images was assessed, since the bulk
phase did not show sufficient fluorescence intensity for evaluation
of lifetimes. The results (Fig.
1) showed shorter fluorescence
lifetimes for the pure DNA solution (2,715 ± 121 ps;
n = 22 images) than for the pure tRNA solution (3,590 ±
42 ps;
n = 10 images). The fluorescence lifetime of SYTO 13
in the tRNA:DNA mixture (concentration ratio [weight:weight]
of tRNA:DNA = 3.39:1) is situated in between the values for
pure DNA and tRNA (3,212 ± 63 ps;
n = 10 images). The
average in vivo fluorescence lifetimes of SYTO 13-stained
E. coli cells (2,739 ± 247 ps;
n = 1,553 cells) lies close
to that of the pure DNA solution.
In a first experiment with autotrophic biofilms, a very short
lifetime of SYTO 13 was measured. The fluorescence lifetime
of SYTO 13 in slow-growing, autotrophic biofilms was 1,853 ±
203 ps (
n = 82 images) and thus was short compared to results
of the in-solution experiments with
E. coli-derived DNA and
tRNA (see Fig.
1). Therefore, we have performed additional experiments
with SYTO 13- stained DNA solutions purified from the slow-growing
bacterial strain BNC1 in order to check the possibility that
the fluorescence lifetimes of SYTO 13 bound to DNA isolated
from slow-growing bacterial strains is significantly shorter
than those for
E. coli-derived DNA. The measurements of SYTO
13-stained DNA purified from the slow-growing EDTA-degrading
BNC1 strain showed an even shorter fluorescence lifetime (1,523
± 293 ps;
n = 13 images) if compared with DNA from
E. coli.
Bacterial monocultures.
The experiments with bacterial monocultures were the next step on the way to establishing the fluorescence lifetime measurements of bacterial growth and activity in complex microbial communities. During the growth curve of E. coli in liquid medium, cell counts were determined. The fluorescence lifetime of SYTO 13 was monitored every 45 min. The bacteria were inoculated in fresh medium and observed until the population reached the stationary growth phase.
SYTO 13 fluorescence lifetimes were assessed from fluorescence lifetime images using the freehand ROI tool. The average lifetime of each bacterium in the image was computed for images with <10 bacteria, and the average fluorescence lifetimes of 10 randomly selected bacteria were assessed for images with more than 10 bacteria. In E. coli liquid culture (Fig. 2), the lifetime was longer in the exponential growth phase than in the lag and stationary growth phases. Standard errors of means, which show the diversity of the lifetimes in the bacterial population, were smaller in the late exponential phase than in the lag and stationary phases. This correlates with the lower diversity of growth rates for the exponentially growing population than for populations in lag or stationary growth phases. The correlation between growth rates µ (Fig. 3) and the fluorescence lifetimes was significant in all experiments (4 experiments, 9 to 12 time points per experiment, and typically 20 to 50 bacteria per time point).
Biofilm experiments.
The fluorescence lifetimes of SYTO 13-stained chemoautotrophic
and heterotrophic biofilms growing in rotating annular reactors
were compared in order to study whether the lifetimes correlate
with the growth rate of the biofilms (autotrophic biofilms have
a lower growth rate than heterotrophic ones). Fluorescence lifetimes
of SYTO 13 in autotrophic (slower-growing) biofilms were significantly
shorter than those with heterotrophic biofilms (1,853 ±
203 ps [
n = 82 images] for autotrophic biofilms; 2,486 ±
390 ps [
n = 54 images] for heterotrophic biofilms). Furthermore,
in the case of autotrophic biofilms, the effects of different
substrate loads on the fluorescence lifetime were studied. Under
a higher substrate load, which is supposed to result in higher
growth rates of biofilm organisms, the biofilm showed longer
fluorescence lifetimes, indicating higher RNA:DNA ratios in
the cells than was the case with the biofilm under lower substrate
loads. In order to be sure that we compared the similar bacterial
species in these autotrophic biofilms, we evaluated separately
the lifetimes of typical spherical microcolonies of bacteria
growing in our autotrophic biofilms and compared them (see Fig.
4). The fluorescence lifetimes of autotrophic colonies grown
with 3 g m
–2 day
–1 ammonium were significantly longer
than those of colonies grown with 1.5 g m
–2 day
–1 ammonium (2,377 ± 257 ps [
n = 38 colonies] for higher
substrate load; 1,977 ± 253 ps [
n = 69 colonies] for
lower substrate load).
Slides from the reactor experiments with heterotrophic and autotrophic
biofilm media were removed from the reactor and incubated in
petri dishes in buffer without nutrients for 24 h in order to
evaluate the impact of starvation on the lifetime of SYTO 13.
It is known that starvation decreases the RNA:DNA ratio. The
control biofilms were left in the reactor (and supplied with
glucose or ammonium) till 1 to 2 h before the measurements were
taken. The starved heterotrophic biofilms showed significantly
shorter fluorescence lifetimes than the control (2,562 ±
291 ps [
n = 13 images] for starved biofilms; 2,970 ±
161 ps [
n = 14 images] for glucose-supplied biofilms). For autotrophic
biofilms, the difference in lifetimes between the starved and
ammonium-supplied biofilms was not significant. Nevertheless,
the mean values showed the same trend as in the case of heterotrophic
biofilms, being shorter in case of starved autotrophic biofilms
than with the ammonium-supplied autotrophic biofilms (1,814
± 117 ps [
n = 15 images] for starved biofilms; 1,848
± 105 ps [
n = 17 images] for ammonium-supplied biofilms).

DISCUSSION
The idea of using FLIM in combination with SYTO 13 for in situ
bacterial activity measurement originates with a report on DNA
and RNA discrimination in healthy and apoptotic Chinese hamster
ovary cells (
41). This approach was transferred to microbiological
samples in order to employ it for measuring bacterial activity.
The rationale of the experiments was that resting bacterial
cells, e.g., those in the stationary growth phase, have a high
DNA content and a low RNA content. During bacterial activity,
e.g., in the logarithmic growth phase, the bacterial cells produce
RNA and as a result the proportion of RNA/DNA changes. This
change was determined by means of FLIM as a sum parameter or
on the basis of single cells.
A first attempt at using the FLIM approach on biofilm samples showed that it is possible to distinguish bacteria exposed to different nutrient regimes (26). For this purpose, biofilms were developed with river water in a rotating annular reactor on polycarbonate slides. The slides from the reactor were then incubated in petri dishes with either old river water, fresh river water, or fresh river water with glucose added. Measurement of the SYTO 13 lifetime showed significantly different signals. As a result, the lifetimes of SYTO 13 were approximately 1,700 ps (starved bacteria), 2,000 ps (slow-growing bacteria), and 2,200 ps (fast-growing bacteria). These preliminary results (26) encouraged the present study with defined nucleic acids in solution, pure cultures of E. coli, and chemoautotrophic and heterotrophic biofilms.
The nucleic acid-specific fluorochrome SYTO 13 becomes fluorescent after binding RNA and DNA. For both single- and double-stranded nucleic acids, the quantum yields are equal. SYTO 13 has an excitation maximum at 488 nm and an emission peak at 510 nm. In comparison to the fluorescence emission intensity, the lifetime of SYTO 13 is significantly different if it is bound to RNA or DNA (Fig. 1). This result is in agreement with results of a previous study investigating the distribution of DNA and RNA in eukaryotic cell cultures. Van Zandvoort et al. could demonstrate different lifetimes for SYTO 13 bound to DNA (nucleus and mitochondria) and to RNA (cytoplasm) using differential imaging (41). The differences in the lifetime of isolated E. coli DNA in comparison to DNA in E. coli cells may be due to the local microenvironment. For example, the cellular DNA is associated with proteins which may slightly shift the lifetime measured. The lifetime also followed the growth curve measured for suspended E. coli cells (Fig. 2). If the growth rate of E. coli is calculated and compared with the lifetime measured, a significant correlation can be seen (Fig. 3). This strongly suggests the applicability of lifetime imaging as an in situ technique for measuring bacterial cell activity.
The RNA:DNA ratio was already discussed as a potential technique as a measure for estimating the growth rate of bacteria. However, the technique requires the extraction of nucleic acids in order to measure RNA and DNA using a spectrophotometer after staining with ethidium bromide (16). The discrimination of different bacterial populations in seawater was described using flow cytometry (38). Troussellier and colleagues were able to separate different bacterial clusters using the fluorescence intensity of SYTO 13. The emission intensity was taken as a measure of nucleic acid content and cell size. These clusters might represent either the same or different bacterial species. We have shown that in environmental biofilms, it is possible to differentiate bacterial populations based on their fluorescence lifetimes after staining with SYTO 13 (Fig. 4). When FLIM is used, the information about cell size and fluorescence intensity is intrinsically present or can be easily obtained from the fluorescence intensity image, which is always computed automatically prior to the fluorescence lifetime image. Consequently, the fluorescence intensity in combination with the fluorescence lifetime will reveal more information on environmental microbial populations. This combined approach allows the recording of both structural information on cellular and polymeric biofilm constituents and physiological information, e.g., bacterial activity.
Conclusions.
The FLIM approach in combination with the nucleic acid-specific fluorochrome SYTO 13, described for eukaryotic cells elsewhere, can be transferred to microbiological samples.
The fluorescence lifetimes of SYTO 13 in tRNA and DNA solutions were in agreement with previous measurements, which confirmed the assumptions for measurement of RNA/DNA ratios.
The division rate [µ] of E. coli strongly correlates with the fluorescence lifetime of SYTO 13, showing the suitability of the method for measurement of cell activity in liquid bacterial monocultures.
The FLIM approach for RNA:DNA ratio measurements can easily be extended to environmental microbial communities, as suggested by experiments with slow- and fast-growing biofilm communities.
FLIM as a tool for measuring bacterial activity does not require extraction of RNA and DNA, no radioactive chemicals are necessary, and it can be applied as an in situ technique.

ACKNOWLEDGMENTS
P.W. acknowledges financial support from UFZ.
We thank B. Nörtemann for the EDTA-degrading strain BNC1. The supply of reactor biofilms from Christian Staudt is appreciated. The plugin for ImageJ was written by M. Tröger and R. Braungarten.

FOOTNOTES
* Corresponding author. Mailing address: Helmholtz Centre for Environmental Research-UFZ, Department of River Ecology, Brueckstrasse 3a, 39114 Magdeburg, Germany. Phone: 49 391 8109 800. Fax: 49 391 8109 150. E-mail:
thomas.neu{at}ufz.de 
Published ahead of print on 2 November 2007. 
Present address: School of Medical Sciences, University of Aberdeen, Aberdeen, United Kingdom. 
Present address: Hochschule Anhalt (FH), Köthen, Germany. 

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Applied and Environmental Microbiology, January 2008, p. 294-299, Vol. 74, No. 1
0099-2240/08/$08.00+0 doi:10.1128/AEM.01806-07
Copyright © 2008, American Society for Microbiology. All Rights Reserved.