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Applied and Environmental Microbiology, October 2001, p. 4896-4900, Vol. 67, No. 10
0099-2240/01/$04.00+0 DOI: 10.1128/AEM.67.10.4896-4900.2001
Copyright © 2001, American Society for Microbiology. All rights reserved.
Assessing the Diversity of Marine Bacterial
-Glucosidases by Capillary Electrophoresis
Zymography
Jesús M.
Arrieta and
Gerhard J.
Herndl*
Department of Biological Oceanography,
Netherlands Institute for Sea Research, 1790 AB Den Burg, Texel,
The Netherlands
Received 7 May 2001/Accepted 31 July 2001
 |
ABSTRACT |
We propose a new method for the fast separation and detection of
-glucosidases in environmental samples. With this approach,
-glucosidases extracted from bacteria are evidenced by
substrate-incorporated capillary electrophoresis (CE zymography) and
their kinetic parameters can be determined by repeated injections using
different substrate concentrations. Preliminary results obtained with
natural bacterial communities from the coastal North Sea suggest that
the diversity of
-glucosidases in the marine environment might be
much higher than previously observed.
 |
TEXT |
Bacterioplankton are the principal
consumers of the dissolved organic carbon (DOC) pool in the sea,
which besides soil humus represents the largest reactive organic carbon
reservoir on earth (24). The chemically characterizable
macromolecular compounds of the DOC pool are carbohydrates, proteins,
and lipids, comprising all together about 20 to 40% of the total DOC,
commonly with higher percentages of macromolecular compounds present in
the euphotic layers of the ocean than in the deep waters
(5). The turnover of this DOC pool is highly variable,
ranging between 40 to 100 days in the euphotic layers and averaging
6,000 years in the deep sea (14, 25).
As shown by ultrafiltration techniques, only about 20 to 30% of the
DOC present in the ocean is of >1,000 Da (2). Yet this high-molecular-size fraction, which is contemporarily produced (20), is turned over more rapidly than the <1,000-Da
DOC fraction (1, 2). Gram-negative
bacterioplankton, which usually constitute more than 90% of the total
bacterioplankton in seawater (9), can only transport
molecules of <600 Da through their cell walls (17). This
hydrolysis of the large bioavailable molecules is mediated by
surface-bound ectoenzymes located at the cell wall or in the
periplasmic space (8, 18). Usually bacterial
surface-associated ectoenzymatic activity dominates over freely
dissolved extracellular enzymes (sensu Chróst [8])
in the marine environment (6).
Over the past two decades, a number of studies have focused on the
determination of bacterial ectoenzymatic activity using substrate
analogs linked to fluorophores which fluoresce upon cleavage from the
substrate by the activity of the appropriate ectoenzymes (12,
13). The high fluorescence yield upon cleavage allows
determination of the ectoenzymatic activity of bacterioplankton using
incubation periods of only minutes to hours and in situ temperature
conditions. This approach has been widely applied to determine the
ectoenzymatic activity of bacterioplankton.
Biphasic or even multiphasic kinetics have been obtained not only for
ectoenzymatic activity but also for uptake of organic substrates
(4, 21, 23). The obvious question which arises from these
studies is as follows: why should natural bacteria exhibit
Km values in the millimolar range if the
substrate is present only in the nanomolar to micromolar range in the
environment? Another question is whether a single bacterial species or
even an individual cell can exhibit biphasic uptake and ectoenzymatic activity. To the best of our knowledge, there are no reports of bi- or
multiphasic hydrolytic ectoenzyme kinetics available for single
bacterial strains. The potential ecological implications of these
observations have been discussed previously (3, 23). Without going into detail here, the problem of the apparently existing
ectoenzymatic diversity in the natural environment has not been
addressed yet. There is only one study which determined the diversity
of a bacterioplankton ectoenzyme,
-glucosidase, in the natural
environment (19). These authors found only two different
-glucosidases in the pycnocline layer of the Adriatic Sea,
indicating a rather limited diversity of
-glucosidase, especially if
the large number of potential substrates is considered
(19).
With the present methods available for assessing ectoenzymatic activity
under near-natural conditions, the required resolution to determine
ectoenzyme diversity in natural bacterioplankton communities cannot be
achieved. We therefore modified a capillary electrophoresis (CE)-based
method, originally described by Xue and Yeung (26) for
detecting lactate dehydrogenase in mammalian cells, to separate and
detect the different bacterial
-glucosidases present in seawater.
This modified method not only allows the determination of the
ectoenzyme diversity present in a given sample but also allows the
simultaneous determination of the kinetics of all the different
ectoenzymes present in the sample. In this paper we present the outline
of the method with the example of
-glucosidase. (This work was
performed in partial fulfillment of the requirements for a Ph.D. from
the University of Groningen, Groningen, The Netherlands, by
J.M.A.)
Bacterial ectoenzyme extraction.
For developing this method,
four
-glucosidase-producing bacterial strains (two gram-positive
strains, Planococcus citreus and Salinicoccus
roseus, and two gram-negative strains, Vibrio sp. and
Paracoccus alkenifer, belonging to the
- and
-proteobacteria, respectively) isolated from the northern Adriatic
Sea (11) were used. The strains were cultured in ZoBell
2216 broth (5 g of peptone, 1 g of yeast extract, 1 liter of
0.2-µm-pore-size-filtered seawater). One-milliliter aliquots of
exponentially growing cultures were harvested by centrifugation
(3,200 × g, 4°C, 15 min) and washed three times with
0.2-µm-pore-size-filtered artificial seawater (16)
before resuspension of the pellet in the buffer solution for ectoenzyme
extraction (described below).
Natural bacterioplankton communities were collected from the coastal
North Sea using acid-rinsed carboys. Fifty liters of seawater was
filtered through 0.8-µm-pore-size polycarbonate filters (142-mm
diameter; Millipore, Bedford, Mass.) in order to exclude most
eukaryotic organisms. To minimize the loss of bacterial biomass due to
clogging, the filter was replaced every 10 liters. Bacteria in the
filtrate were concentrated to a final volume of 0.5 liters using a
Pellicon (Millipore) tangential-flow filtration system equipped with a
0.1-µm-pore-size filtration cartridge (hydrophilic polyvinylidene
difluoride membrane [Durapore]; Millipore). The bacteria in the
retentate were further concentrated by centrifugation (20,000 × g, 4°C, 30 min) and the resulting pellet was washed three
times with artificial seawater.
About 10
8 to 10
9 bacterial
cells obtained from bacterial cultures or from natural bacterial
communities were resuspended in
1 ml of extraction buffer consisting of
40% glycerol (Sigma, St.
Louis, Mo.), 100 mM taurine (Fluka Chemie AG,
Buchs, Switzerland),
20 mM cholic acid (Fluka), and 1 mM
MgSO
4 (pH 7.50), sonicated
on ice at 50 W for
30 s, and centrifuged again for 60 min (20,000
×
g, 4°C). Thereafter, the supernatant containing the enzyme
extract
was carefully siphoned off and stored at 4°C for subsequent
analysis.
The bulk of the intracellular components such as DNA and RNA
remained
in the pellet, as verified by phenol-chloroform nucleic acid
extraction
and agarose gel electrophoresis (data not shown). Therefore,
we
assume that the enzymes in the supernatant are
ectoenzymes.
The

-glucosidase activity of both the strains and the natural
bacterial communities was measured in triplicate subsamples
by means of
the fluorogenic substrate analog
methylumbelliferyl-

-
D-glucoside
(
13) in the
cells resuspended in artificial seawater before
extraction, in the
enzyme extract, and in the remaining pellet
in order to determine the
extraction efficiency for

-glucosidase.
The fluorescence was
measured at an excitation wavelength of 360
nm and an emission
wavelength of 445 nm on a Hitachi F-2000 spectrofluorometer
(Hitachi,
Tokyo, Japan). The extraction efficiencies ranged from
0.3% for the
gram-positive
P. citreus to 92.8% for the
Vibrio sp. (Table
1). For the freshly collected
natural bacterial communities
the average extraction efficiency was
73.4%. Extracting the

-glucosidases
in the presence of Triton X-100
as previously described (
19)
did not improve the
extraction efficiency. Moreover, the presence
of Triton X-100 in the
sample interfered with the separation (data
not shown). No effort was
made to inactivate proteases in the
sample since the electrophoretic
patterns remained unchanged in
shape and relative intensity during
storage in the dark at 4°C
for 4 days.
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TABLE 1.
Mean extraction efficiency and range of -glucosidase
activity measured in triplicate for the single bacterial strains and in
five different bacterial communities from the coastal North Sea
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|
CE separation and online detection of
-glucosidase
activity.
Analyses were performed using a Biofocus 3000 CE system
equipped with a Biofocus LIF2 laser-induced fluorescence detector (Bio-Rad, Hercules, Calif.). The enzyme separation and detection were
performed in 50-µm-inside-diameter fused silica capillaries. To avoid
electro-osmotic flow and to minimize protein interaction with the wall
of the capillary, the inner surface of the capillary was coated with
polyacrylamide by means of a siloxane bond (15). The total
length of the capillary was 75 cm and the distance from the inlet to
the detection window was 70.4 cm. Detection of
-glucosidase activity
in the capillary was based on the hydrolysis of the fluorogenic substrate analog resorufin-
-D-glucopyranoside (Rglu)
(Sigma). The fluorophore released upon hydrolysis is resorufin and was measured using the 594-nm line of the helium-neon laser as the excitation source, with the emission measured at 630 nm in the LIF2
system (600DRLP02 beam splitter, 630DF30 discrimination filter; Bio-Rad).
The electrophoresis buffer contained 100 mM taurine, 20 mM cholic acid,
and 1 mM MgSO
4 dissolved in distilled water, and
the
pH was adjusted with NaOH to 7.50. Different concentrations of
the
substrate (Rglu) were added to the electrophoresis buffer,
ranging from
0.1 to 350 µM final concentrations; however, at concentrations
higher
than 200 µM, a small amount of precipitate was observed
after a few
hours of storage at 4°C, and those results were excluded
from the
calculations of enzyme kinetics. The samples containing
the solubilized
ectoenzymes and buffer solutions were transferred
to the refrigerated
carousel of the Biofocus system and kept at
4°C. The capillary
temperature was set at 15°C to protect the
enzymes from Joule heating
during the electrophoretic separation
using FC-77 (3M, St. Paul, Minn.)
as a cooling
fluid.
The activity of the different

-glucosidases was measured using a
four-step procedure (Fig.
1) similar to
that described by
Xue and Yeung (
26) to measure
lactate dehydrogenase activities
in erythrocytes. The solubilized
enzymes were hydrodynamically
injected into the capillary at a constant
pressure × time value
of 15 lb/in
2 × s to
provide a fixed injection volume of 147 nl as calculated
by repeated
injection and pressure mobilization of a resorufin
standard.
Thereafter, 20 kV was applied for 20 min to separate
the different

-glucosidases based on their different electrophoretic
mobility and
to allow them to migrate into the region containing
the substrate (Fig.
1). Due to the presence of glycerol in the
sample buffer, the ionic
strength in the sample zone is lower
than in the electrophoresis
buffer, producing a transient decrease
in the present level during the
first 3 min of the separation
as observed for all the runs. This
phenomenon is known as field
amplification and might be responsible for
an additional sample
concentration and narrowing of the observed peaks
(
7). The
voltage was then turned off to allow the enzymes
to hydrolyze
the fluorogenic substrate added to the electrophoresis
buffer.
Hydrolysis of this fluorogenic substrate leads to a local
accumulation
of the fluorescent hydrolysis product (resorufin) in those
regions
of the capillary where

-glucosidases are present. After
allowing
the different

-glucosidases to react with the Rglu
substrate
for 10 to 20 min (see below), 20 kV was applied again to
elute
the fluorescent products passing the detection window where
quantification
takes place.

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FIG. 1.
Schematic outline of the method used to separate and
detect different types of -glucosidases. Different symbols represent
different enzymes in the sample (see text for a more detailed
explanation of the four steps).
|
|
Separation of different
-glucosidases.
The separation
conditions were optimized for
-glucosidase suspensions extracted
from two different strains of gram-negative bacteria (Vibrio
sp. and P. alkenifer). Single peaks of
-glucosidase activity were obtained when the extracts from the two bacterial strains
were injected separately (Fig. 2A). The
fluorescent signal increased linearly with increasing incubation times
of 5, 10, 20, 30, and 40 min, without significant peak distortion due
to diffusion of the fluorescent product. However, a tail of elevated fluorescence was found preceding the peaks (Fig. 2A) in all
electropherograms. The intensity of this feature was proportional to
the amount of sample injected but did not increase with increasing
incubation times and did not appear in heat-denatured samples.
Therefore, we believe that it is produced by the enzyme(s) during its
migration in the capillary. A similar behavior was also reported for
lactate dehydrogenase (27). This fluorescent tail,
however, biases the determination of an accurate baseline, especially
if dealing with more complex samples such as natural enzyme extracts.
To accurately determine hydrolysis rates and evidence the enzyme peaks,
repeated injections with increasing incubation periods are required in order to discriminate the fluorescence produced during the incubation period from the signal produced elsewhere. Therefore, incubation times
of 10 and 20 min were chosen for the experiment with the natural
community and the ectoenzymatic activity was calculated by integrating
the peak area. Different pH values ranging between 7.50 and 8.50 were
tested. The peak resolution decreased at pHs of
8.00. Therefore, pH
7.50 was chosen for an optimal separation of the
-glucosidases.

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FIG. 2.
Electropherograms obtained after injecting enzyme
extracts from two different strains (Vibrio sp. and
P. alkenifer) separately (A) and mixed together (B);
note that the peak height is reduced by 50% in the mixture (B) as it
contains only 50% of each of the extracts. RFU, relative fluorescence
units.
|
|
To determine the potential of the CE to separate

-glucosidases,
equal amounts of the extracts from
Vibrio sp. and
P. alkenifer were mixed. As shown in Fig.
2B, the mobility of an
individual

-glucosidase is independent of the presence of other

-glucosidases
in the same sample and the amount of fluorescent
product released
is proportional to the amount of enzyme
injected.
Separation of
-glucosidases from natural bacterial
communities.
Once the method was optimized for the separation of
-glucosidases from strains, the ectoenzymes from a whole bacterial
community were extracted as described above and run in the CE under the same conditions described for the strains. Peaks were considered to
represent
-glucosidases if the integrated area of fluorescence increased systematically in replicate incubations of 10 and 20 min, as
explained above. In contrast to previous observations on the
variability (diversity) of
-glucosidases in marine systems (19), the electrophoretic pattern we obtained (Fig.
3) revealed seven distinct peaks of
-glucosidase activity, while Rath and Herndl (19) found
only one to two different types of
-glucosidase using
chromatographic methods. The differences between the former study and
the CE approach may be partly due to the superior resolution power of
CE in combination with the sensitivity of laser-induced fluorescence
detection. The differences in electrophoretic mobility of native
proteins are caused by differences in the amino acid sequence and/or by
the secondary structure of the protein (10). Therefore,
these different forms of
-glucosidase may have different functional
properties such as reaction kinetics. Differences in the kinetic
properties of ectoenzymes often reflect differences in the substrate
supply and utilization among different members of the bacterioplankton
community (22, 23).

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FIG. 3.
Electrophoretic pattern obtained from enzymes extracted
from a natural bacterial community. The different lines show the
results obtained with different concentrations of Rglu. RFU, relative
fluorescence units.
|
|
Determination of
-glucosidase kinetics using CE.
Standard
solutions of resorufin ranging from 8 nM to 400 µM were injected in
triplicate to establish the calibration curves necessary for converting
the relative fluorescence units into resorufin concentrations.
Therefore, the absolute amount of resorufin injected ranged from 0.90 to 58,800 fmol (1 fmol = 10
15 mol).
Despite the fact that the 594-nm wavelength provided by our laser is
not optimal for the excitation of resorufin (excitation maximum, 571 nm), we successfully detected as few as 3.45 × 1010 molecules (57.33 fmol) of resorufin in the
electrophoresis buffer. Below this threshold it was not possible to
clearly distinguish the signal from background noise. The increase in
fluorescence intensity of resorufin was linear
(r2 = 0.998) over the whole range from
57.33 up to 58,800 fmol of resorufin, making this method suitable for
quantification of enzyme activity over a large range of enzyme
concentrations and specific activities. At the lowest amounts of
resorufin (<1 pM), the measured peak area was slightly lower than
expected from the calculated regression line obtained over the whole
concentration range. However, this had no effect on our measurements
due to the high fluorescent readings obtained for both the strains and
the natural samples.
The kinetic properties of the detected

-glucosidases were determined
with triplicate injections of the enzyme solutions in
the
electrophoresis buffer containing concentrations of the fluorogenic
substrate Rglu ranging from 0.05 to 150 µM. An example is given
in
Fig.
3 showing the pattern obtained from repeated injections
of the

-glucosidases extracted from a natural sample at different
substrate
concentrations. The hydrolysis rates corresponding to
each of the
detected peaks were first calculated for each concentration
and then
used to calculate the specific
Vmax
and
Km values of
the different

-glucosidases by nonlinear regression (
8). The
estimated
Km values of

-glucosidases
obtained from coastal North
Sea bacterioplankton ranged from 26.02 to
136.78 µmol liter
1 (Table
2).
Characterizing the diversity of
-glucosidases.
For the
characterization of the
-glucosidase diversity it is necessary to
measure both the number of different
-glucosidases present in the
environmental sample and the relative amount of each ectoenzyme
(Vmax is proportional to the amount of
enzyme present). The relative amount of ectoenzyme is certainly biased due to the different extraction efficiencies observed. However, if we
assume that the extraction efficiency is constant for a specific
ectoenzyme produced by a bacterial species, it is possible to compare
the relative abundance of a specific
-glucosidase between related
samples, i.e., by studying the succession of ectoenzyme activities in
bacterioplankton communities. Different ectoenzymes might have the same
electrophoretic mobility, thus potentially leading to an
underestimation of the number of enzymes present. Therefore, the
determination of the
-glucosidase richness as obtained by CE has to
be considered a conservative estimate. Nevertheless, we detected a
higher number of
-glucosidases in natural bacterioplankton with the
CE approach than that reported hitherto.
It is now possible to estimate phylogenetic microbial diversity in
natural samples using molecular techniques (
9). However,
the link between the phylogenetic and functional diversity of
microbial
communities is still largely missing. Despite the above-mentioned
limitations of the CE approach, we believe that it is a new and
promising tool for determining functional bacterial diversity.
Although
it is not possible to directly link the different types
of

-glucosidase to the bacterial species producing them, it is
possible
to relate the changes in the phylogenetic composition
observed in
bacterioplankton communities to the shifts in the
enzyme composition of
the community. The CE approach is not limited
to the determination of

-glucosidase activity, but by using other
substrates it should also
be possible to detect the variability
of other enzymes occurring in
marine environments. Finally, with
some modifications in the extraction
protocols and buffer system
used, the CE approach should be suitable
for studying ectoenzyme
diversity in other natural environments as
well, such as freshwaters
and
soils.
 |
ACKNOWLEDGMENTS |
Financial support was provided by the Dutch Earth and Life Sciences
Research Council (ALW) and the NIOZ. J.M.A. was supported by a
predoctoral grant from the Basque Government.
 |
FOOTNOTES |
*
Corresponding author. Mailing address: Department of
Biological Oceanography, Netherlands Institute for Sea Research (NIOZ), P.O. Box 59, 1790 AB Den Burg, Texel, The Netherlands. Phone: 31-222-369-507. Fax: 31-222-319-674. E-mail: herndl{at}nioz.nl.
This is NIOZ contribution number 3631.
 |
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Applied and Environmental Microbiology, October 2001, p. 4896-4900, Vol. 67, No. 10
0099-2240/01/$04.00+0 DOI: 10.1128/AEM.67.10.4896-4900.2001
Copyright © 2001, American Society for Microbiology. All rights reserved.