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Applied and Environmental Microbiology, June 2001, p. 2823-2828, Vol. 67, No. 6
0099-2240/01/$04.00+0 DOI: 10.1128/AEM.67.6.2823-2828.2001
Copyright © 2001, American Society for Microbiology. All rights reserved.
Fiber-Optic Fluorometer for Microscale Mapping of
Photosynthetic Pigments in Microbial Communities
Roland
Thar,1
Michael
Kühl,1,* and
Gerhard
Holst2
Marine Biological Laboratory, University of
Copenhagen, DK-3000 Helsingør, Denmark,1 and
Max Planck Institute for Marine Microbiology, D-28359 Bremen,
Germany2
Received 28 November 2000/Accepted 12 March 2001
 |
ABSTRACT |
Microscale fluorescence measurements were performed in
photosynthetic biofilms at a spatial resolution of 100 to 200 µm with a new fiber-optic fluorometer which allowed four different excitation and emission wavelengths and was configured for measuring
phycobiliproteins, chlorophylls, and bacteriochlorophylls. We present
details of the measuring system and describe examples of applications
in different microbial communities.
 |
TEXT |
Microbial phototrophic communities
in sediments and biofilms are often used as small-scale model systems
in studies of microbial interaction (15). In the absence
of bioturbation and grazing, such systems exhibit characteristic
stratification of both microbial processes and different photosynthetic
populations over micrometer to submillimeter distances. Microsensor
techniques (8, 14) allow repetitive and nondestructive
high-resolution measurement of physical parameters (light and
temperature), chemical parameters (e.g., pH and O2,
CO2, and H2S contents), and metabolic rates (photosynthesis and respiration) in photosynthetic sediments and biofilms (5, 16). For the most part, analysis of the
microdistribution of phototrophic microorganisms has relied on
determining characteristic depth-dependent photopigment signatures by
destructive techniques, such as horizontal slicing of a sample and
subsequent pigment extraction and analysis (1, 10, 13), or
by spectral absorbance and fluorescence microscopy of vertical thin
sections obtained by freeze sectioning (4).
Nondestructive techniques have involved laser scanning confocal
microscopy and reflectance spectroscopy of translucent biofilms, but
the generally high optical densities of most sediments or microbial
mats limit this approach to the upper 100 to 200 µm of samples
(9, 17). Another approach is based on spectral measurement
of the internal light fields of biofilms and sediments with fiber-optic
microprobes, in which photopigment distributions are inferred from
depth-dependent changes in spectral signatures for characteristic
pigments (7, 11, 13). Besides reflectance and transmission
spectroscopy, fiber-optic microprobes can also be used for microscale
fluorescence analysis of biofilms and sediments (4). Here
we describe a new fiber-optic fluorometer which can detect
photopigments by their characteristic fluorescence as sampled via a
fiber-optic microprobe.
Fiber-optic fluorometer.
The technical concept of the new
fluorometer is shown in Fig. 1.
Ultrabright light-emitting diodes (LEDs) equipped with short-pass filters are used as excitation light sources. The excitation light is
coupled into a single-strand step index silica glass fiber (core/cladding diameter, 100/140 µm) via a standard ST connector. The
fiber is connected to a multimode 2×2 fused fiber coupler (Gould Inc.)
(i.e., a fiber-optic beam splitter). One of the coupler branches is
connected to the fiber-optic microprobe (see below). The excitation
light illuminates the sample around the microprobe tip and excites the
fluorophores present. A fraction of the induced diffuse fluorescent
light reenters the glass fiber through the microprobe tip and is guided
via the fiber coupler to a photomultiplier tube (PMT) (H5702-50;
Hamamatsu). Removable light filters are positioned between the fiber
end face and the PMT detector. The PMT provides a voltage signal
proportional to the measured light intensity.
The light intensity of the LEDs is modulated at a frequency of 750 Hz.
Subsequently, the fluorescence signal detected by the
PMT is also
modulated at 750 Hz. A lock-in amplifier selectively
amplifies only
signals at this frequency in order to minimize
the influence of ambient
light or electronic noise. The electronics
is controlled by a built-in
microcontroller (V25; GME GmbH) that
reads the fluorescence signal
measured by the lock-in amplifier
via an analogue-to-digital converter.
A reference zero value obtained
with the microprobe immersed in pure
water is subtracted from
each measurement. The results of the
measurements are shown in
digits on a small text display.
Alternatively, a personal computer
can be connected via a serial (RS
232) interface in order to control
the measuring procedure by
custom-made
programs.
Fiber-optic microprobe.
Fiber-optic microprobes were prepared
as described by Kühl and Jørgensen (6) from a
100/140 µm (core/cladding ratio) step index fused silica fiber cable
(numerical aperture, 0.22) with a standard ST plug at one end. The
polyvinyl chloride tubing and protective plastic coating of the glass
fiber were stripped for a length of approximately 40 mm, and the bare
fiber was tapered in a small acetylene-oxygen flame to obtain a tip
diameter of 5 to 10 µm. The taper was cut to obtain a fiber tip
diameter of 50 µm. The tip was heated in a hot flame, which resulted
in a rounded tip without sharp edges. For better handling the
fiber-optic microprobe was fixed with epoxy resin in a hypodermic
needle mounted on a syringe, which then was attached to a
micromanipulator (Märtzhäuser GmbH).
Light sources and filter combinations.
The fluorometer was
configured with four ultrabright LEDs with the following peak
wavelengths and half band widths, respectively: 470 and 20 nm
(BP280CWPB1K; DCL Components), 515 and 35 nm (NSPE 510S; Nichia, Inc.),
590 nm (TLHE 5800; VISHAY), and 610 and 20 nm (L-513TUEC; DCL
Components). The LEDs were combined with short-pass filters KP 480 and
KP 540 (OIB GmbH), SP 600 (CVI), and KP 620 (OIB) with cutoff
wavelengths of 480, 540, 600, and 620 nm, respectively. Below these
filtered excitation light sources are referred to as blue, green,
yellow, and orange, respectively.
The fluorescence light was detected in three different wavelength
regions: orange, red plus near-infrared (NIR), and NIR.
The orange
region was cut out by a filter combination consisting
of a 600-nm
long-pass filter and a 650-nm short-pass filter (LP
600 and SP 650;
CVI). For the red plus NIR region and the NIR
region 645- and 780-nm
long-pass glass filters (RG 645 and RG
780; Schott GmbH), respectively,
were used. As the glass filters
themselves exhibited weak fluorescence
if they were excited with
blue light, an additional 570-nm long-pass
filter (Deep Golden
Amber; LEE Filters Ltd.) was placed in front of
them. Detection
of red plus NIR light and NIR light was limited at
longer wavelengths
by the spectral sensitivity of the PMT; at 800 nm
the sensitivity
of the PMT was only 50% of the maximal sensitivity,
and then it
decreased significantly at longer wavelengths up to 900 nm.
However,
new PMT detectors with higher NIR sensitivity have recently
become
available (Hamamatsu). A more detailed description of the
measuring
techniques involved has been given by Holst et al.
(
2).
Chlorophyll in liquid media.
A pure liquid culture of the
marine green alga Nannochloris sp. was diluted in seven
steps by a factor two. At each dilution step the chlorophyll
a fluorescence was measured with the blue
red+NIR
(excitation
emission) combination. The chlorophyll a
content of the undiluted culture was measured by a standard ethanol
extraction method (12). A strong linear correlation (r2 > 0.998) was found between the
fluorescence signal and the chlorophyll concentration (Fig.
2). Even though the system was optimized
for obtaining measurements in optically dense biofilms and sediments, it can also be used for direct quantitative measurement of chlorophyll in liquid media with reasonable sensitivity. Greater sensitivity in
liquid media can be obtained, but this would involve modification of
the sampling geometry at the fiber tip.

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FIG. 2.
Chlorophyll a fluorescence in a liquid
culture of Nannochloris sp. The error bars indicate standard
deviations (n = 4). a. u., arbitrary units.
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|
Fluorescence fingerprints.
Fluorescence fingerprints of
phototrophic microorganisms were obtained by placing the sensor tip in
samples of five different species that were representative of different
types of phototrophs (Fig. 3). Pure
cultures of Euglena gracilis, Chromatium gracile (recently
reclassified as Marichromatium gracile comb. nov.
[3]), and Synechococcus sp. were centrifuged
in a test tube (150 × g, 4 min). Subsequently, the
fluorescence fingerprints inside the pellets obtained were determined.
A sample of green sulfur bacteria was obtained from an enrichment
culture in a Winogradsky column incubated for several months at 20°C
in dim daylight. An in vivo absorption spectrum of the enrichment
culture revealed that bacteriochlorophyll c was the dominant
pigment. Pelagic diatoms were obtained from Øresund (Denmark) with a
plankton net (mesh size, 10 µm). In order to avoid any influence of
spatial heterogeneity, all excitation
emission values were
determined in each sample without moving the sensor tip. The
fluorescence signals were expressed as percentages of the blue
red+NIR fluorescence, which detected fluorescence from both
chlorophylls and bacteriochlorophylls.
The microalgal phototrophs
E. gracilis and diatoms exhibited
for the green

red+NIR combination values of 10 and 20%,
respectively.
This combination targeted the carotenoids. The higher
value for
the diatom sample could be anticipated by its brownish color
compared
to the bright green of the
E. gracilis sample. The
other fluorescence
combinations did not produce significant
values.
The fluorescence fingerprint of the cyanobacteria
(
Synechococcus) resembled that of the microalgae with one
exception for
the orange

red+NIR combination. For this combination
a signal
of about 20% was detected, whereas no other sample produced
significant
signals. The strong fluorescence was due to
phycobiliproteins,
which are characteristic of cyanobacteria.
Unicellular red algae
like
Cyanidium sp. also contain
phycobiliproteins, but these organisms
are found mainly in acidic
springs and soils. Thus, the orange

red+NIR combination can be used
as a sensitive indicator for
cyanobacteria in most benthic
systems.
The green sulfur bacteria exhibited a fluorescence fingerprint similar
to that of oxygenic phototrophs except for the blue

NIR
combination; for this combination bacteriochlorophyll
c produced a peak of almost 50%. The same peak, but less pronounced,
was
obtained with the
Chromatium sample, which contained mainly
bacteriochlorophyll
a. The weaker signal in the
Chromatium sample
can be explained by the longer wavelength
for maximum fluorescence
of bacteriochlorophyll
a (~870
nm) compared to that of bacteriochlorophyll
c (~750 nm).
The sensitivity of the PMT at 870 nm is about 10
times less than that
at 750 nm. In addition, the
Chromatium sample
exhibited a
peak for the green

orange combination, which may
have been due to
characteristic
carotenoids.
In summary, the data above show that fluorescence fingerprints allow
discrimination of the dominant photopigments characteristic
of benthic
microalgae, cyanobacteria, and anoxygenic
phototrophs.
Measurements in artificial biofilms.
In order to investigate
the spatial resolution of the fiber-optic microprobe, we obtained
measurements in defined biofilms of known composition and thickness.
Three stratified layers consisting of 2% agar were prepared in a test
tube. A homogenized suspension of Nannochloris sp. was added
to the semisolid (~45°C) agar used for the middle layer.
Fluorescence was measured in 200-µm vertical resolution steps with
the blue
red+NIR combination (Fig.
4A). As the fiber tip approached the
upper surface of the Nannochloris layer, the fluorescence
signal increased exponentially from a distance 1 mm above that surface.
About 100 µm above the interface the signal exhibited a maximum
value, which was about two times higher than the average signal value
inside the Nannochloris layer. When the fiber tip approached
the lower limit of the Nannochloris layer at a depth of 5 mm, the signal decreased to one-half of the initial value within ~200
µm. The spatial resolution of a microscale fluorescence measurement
is very dependent on the optical density of the sample in front of the
fiber tip. At a low optical density (e.g., when measurements are
obtained in agar), a large volume in front of the fiber tip is excited,
which results in low spatial resolution, as shown by the increase in
fluorescence 1 mm above the Nannochloris layer (Fig. 4B). At
a higher optical density, a smaller volume is excited, which results in
greater spatial resolution, as shown by the rapid decrease in the
fluorescence signal at the lowermost boundary of the
Nannochloris layer. It is important to keep these
limitations of the technique in mind when fluorescence profiles are
determined for natural samples like stratified microbial communities in
sediments or microbial mats. However, in many cases the optical density
is much greater than that of the Nannochloris layer
described here and the spatial resolution is <100 to 200 µm
(4). It is important to consider spatial resolution in
samples with gelatinous layers of exopolymers with a low optical
density comparable to that of agar.

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FIG. 4.
Fluorescence microprofiles in artificial biofilms. (A)
Nannochloris sp. embedded in an agar layer. (B) Multilayer
system containing diatoms (depth, 0 to 2.3 mm) and green sulfur
bacteria (depth, 2.3 to 5.5 mm). a.u., arbitrary units.
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A defined two-layer system was prepared by sequentially centrifuging a
different cell suspension in a test tube (150 ×
g,
4 min). The lower 30 mm of the test tube was filled with 1% agar.
A 3- to 3.5-mm-thick layer of green sulfur bacteria was added,
which was
covered by a 2- to 2.5-mm-thick layer of diatoms. The
thicknesses of
the various layers were determined after the experiment
by freezing the
sample at

80°C and subsequent vertical sectioning.
Fluorescence
profiles for the blue

red+NIR and blue

NIR combinations
were
determined at 200-µm depth intervals, as shown in Fig.
4B.
As the
same excitation light was used for both fluorescence measurements,
the
difference between the two profiles represented the red fluorescence
in
the visible spectrum. Two layers could be distinguished: (i)
an upper
layer showing only fluorescence for the blue

red+NIR
combination
and (ii) a lower layer in which a signal for the blue

NIR
combination was also detected. Thus, the fluorescence measurements
showed that bacteriochlorophyll was abundant only in the lower
layer.
The thicknesses of the layers in the fluorescence profile
correlated
well with the actual layer thicknesses in the sample.
The results show
that the fiber-optic fluorometer can resolve
the zonation of different
phototrophs in
biofilms.
Application in a photosynthetic sediment.
The system was used
to study cyanobacterial distribution in a marine sulfidic sediment
sample obtained with a core tube (diameter, 45 mm) in Øresund
(Denmark) at a water depth of 6 m. The overlaying water in the
core had a salinity of 22 ppt and was constantly aerated. The core was
kept at 20°C in dim daylight before the experiment. Most of the
sediment surface was covered with Beggiatoa sp. In the
center of the surface layer, a circular area (diameter, ~15 mm) was
covered by a dense 2-mm-thick layer of motile, large, filamentous
cyanobacteria (Oscillatoria sp.). At the beginning of the
experiment, additional illumination was applied with a halogen bulb
(Philips 6423; 15 V; 150 W; distance, 20 cm), which resulted in an
increase in the surface area covered by the cyanobacteria (Fig.
5D). The chlorophyll fluorescence was
monitored over a transect in the upper 3 mm of the sediment. The
transect data included five fluorescence profiles for the blue
red+NIR combination (200-µm depth intervals) for points that were 2 mm from each other. The transect data, which were acquired just before
the illumination was switched on, are shown as a contour plot in Fig.
5A. The chlorophyll distribution showed that only the leftmost 4 mm of
the sediment transect was covered by cyanobacteria. The transect values
for the next 2 days (Fig. 5B and C) show the increase in the area covered by cyanobacteria. The measurements obtained show the potential of the new system for monitoring dynamic changes in the distribution of
benthic phototrophic microorganisms due to migration.

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FIG. 5.
Distribution of Oscillatoria sp. in a marine
sulfidic sediment core for three consecutive days. Additional
illumination was applied at zero time. (A to C) Transects of
chlorophyll a fluorescence. (D) Sediment surface area
covered by Oscillatoria sp. (top view). The positions of the
profile sites are indicated by open circles. a.u., arbitrary units; t,
time; d, day.
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Application in intertidal sediment.
Zonation of diatoms and
cyanobacteria was investigated with intertidal sediments from the Rhone
delta (Camargue, France). The sediment was dominated by diatoms
overgrown by a thin layer of filamentous cyanobacteria. Numerous
fluorescence microprofiles were obtained in a 100-mm2 area.
Figure 6 shows profiles obtained for all
excitation
emission combinations. Vertical freeze sectioning and
subsequent epifluorescence microscopy revealed two distinct layers: an
upper layer ~300 µm thick dominated by filamentous cyanobacteria
and a second layer 1.3 to 1.7 mm thick dominated by diatoms. The
combined biomass of phototrophs was much greater in the upper layer
than in the lower layer. Anoxygenic phototrophic bacteria were not
detected by microscopy, and consequently the blue
NIR combination
resulted in no significant fluorescence signal in the sediment. The
yellow
orange and orange
red+NIR combinations revealed a high
level of phycobilins over a depth interval which was similar to the measured thickness of the cyanobacterial top layer. The profiles obtained with the blue
red+NIR and green
red+NIR combinations also showed peaks in the top layer, but high signal values were also
obtained for deeper layers where diatoms dominated.

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FIG. 6.
Fluorescence microprofiles for different excitation emission combinations in an intertidal sediment from the Rhone delta
(Camargue, France). The error bars indicate standard deviations
(n = 5). a.u., arbitrary units.
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Summary.
It is now possible to obtain microscale fluorescence
measurements with fiber-optic microprobes for nondestructive mapping of
photopigments in biofilms, sediments, and other surface-associated microbial communities. Microscale fluorescence measurements
can also be used for quantitative measurement of pigment concentrations in liquid cultures. However, quantitative measurements cannot be
obtained for optically dense samples, like sediments or microbial mats,
without knowledge of the spatially heterogeneous absorption and
scattering properties of the samples.
In the present study we used fiber-optic microprobes with a tip
diameter of 50 µm, but both smaller and larger tip diameters
can be
obtained easily by using different optical fibers and varying
the
tapering process. Smaller tip diameters should increase spatial
resolution. With a fiber tip diameter of 10 µm fast signal changes
were detected due to movement of filamentous cyanobacteria in
a
biofilm. Larger tip diameters allow integration of heterogeneity
in
pigment distribution, but this leads to greater disturbance
of the
sample. Thus, larger fiber diameters are useful mostly
for monitoring
fluorescence patterns at the surfaces of biofilms
or
sediments.
The new device described here is useful for a wide range of biological
applications where fast fluorescence measurement at
a high spatial
resolution is needed. In addition to the distribution
of photopigments,
the distribution of other fluorescent dyes can
also be mapped (e.g., in
studies of mass transfer within biofilms
or sediments). Other possible
applications are to combine microscale
fluorescence measurements with
molecular techniques to map the
distribution of specific fluorescently
labeled microbes and to
monitor expression of specific genes in
genetically modified microbes
(e.g., via green fluorescent
proteins).
 |
ACKNOWLEDGMENTS |
This study was supported by grants from the European Commission
(grants MAS3-CT98-5054 and EVK3-CT-1999-00010) and the Danish Natural
Science Research Council (contract 9700549).
We thank Volker Meyer for his help with the development of the
electronics and Andrea Wieland for constructive comments and for
providing the intertidal sediment sample from Camargue.
 |
FOOTNOTES |
*
Corresponding author. Mailing address: Marine
Biological Laboratory, University of Copenhagen, Strandpromenaden 5, DK-3000 Helsingør, Denmark. Phone: 45 49 21 33 44. Fax: 45 49 26 11 65. E-mail: mkuhl{at}zi.ku.dk.
 |
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Applied and Environmental Microbiology, June 2001, p. 2823-2828, Vol. 67, No. 6
0099-2240/01/$04.00+0 DOI: 10.1128/AEM.67.6.2823-2828.2001
Copyright © 2001, American Society for Microbiology. All rights reserved.