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Applied and Environmental Microbiology, December 2001, p. 5614-5620, Vol. 67, No. 12
0099-2240/01/$04.00+0 DOI: 10.1128/AEM.67.12.5614-5620.2001
Copyright © 2001, American Society for Microbiology. All rights reserved.
Green Fluorescent Protein as a Novel Indicator of
Antimicrobial Susceptibility in Aureobasidium
pullulans
Jeremy S.
Webb,1
Sarah R.
Barratt,1
Hristo
Sabev,1
Marianne
Nixon,2
Ian M.
Eastwood,2
Malcolm
Greenhalgh,2
Pauline S.
Handley,1 and
Geoffrey D.
Robson1,*
School of Biological Sciences, University of
Manchester,1 and Avecia
Ltd.,2 Manchester, United Kingdom
Received 22 May 2001/Accepted 10 September 2001
 |
ABSTRACT |
Presently there is no method available that allows noninvasive and
real-time monitoring of fungal susceptibility to antimicrobial compounds. The green fluorescent protein (GFP) of the jellyfish Aequoria victoria was tested as a potential reporter
molecule for this purpose. Aureobasidium pullulans was
transformed to express cytosolic GFP using the vector pTEFEGFP (A. J. Vanden Wymelenberg, D. Cullen, R. N. Spear, B. Schoenike, and
J. H. Andrews, BioTechniques 23:686-690, 1997). The transformed
strain Ap1 gfp showed bright fluorescence that was
amenable to quantification using fluorescence spectrophotometry.
Fluorescence levels in Ap1 gfp blastospore suspensions
were directly proportional to the number of viable cells determined by
CFU plate counts (r2 > 0.99). The
relationship between cell viability and GFP fluorescence was
investigated by adding a range of concentrations of each of the
biocides sodium hypochlorite and
2-n-octylisothiozolin-3-one (OIT) to suspensions of Ap1
gfp blastospores (pH 5 buffer). These biocides each
caused a rapid (<25-min) loss of fluorescence of greater than 90%
when used at concentrations of 150 µg of available chlorine
ml
1 and 500 µg ml
1, respectively.
Further, loss of GFP fluorescence from A. pullulans cells was highly correlated with a decrease in the number of viable cells (r2 > 0.92). Losses of GFP
fluorescence and cell viability were highly dependent on external pH;
maximum losses of fluorescence and viability occurred at pH 4, while
reduction of GFP fluorescence was absent at pH 8.0 and was associated
with a lower reduction in viability. When A. pullulans
was attached to the surface of plasticized poly(vinylchloride) containing 500 ppm of OIT, fluorescence decreased more slowly than in
cell suspensions, with >95% loss of fluorescence after 27 h.
This technique should have broad applications in testing the
susceptibility of A. pullulans and other fungal species
to antimicrobial compounds.
 |
INTRODUCTION |
Since the cloning of wild-type green
fluorescent protein (GFP) from the jellyfish Aequoria
victoria (25), expression of GFP has been
demonstrated in numerous organisms, including plants (31),
animals (5), bacteria (3), yeasts
(7), and filamentous fungi (13, 37). Most
applications of GFP have been as a passive label of gene expression and
protein localization (for a review, see reference 36).
However, GFP and selected mutants are now increasingly used as active
sensors of physiological events within cells. In this role, GFP
fluorescence is influenced posttranslationally by its chemical
environment. For example, the pH sensitivity of GFP has recently been
exploited to measure intracellular (16, 18, 27) and
organellar (20) pH, and GFP-based systems have been
developed to monitor intracellular calcium (21),
microviscosity (34), and protease activity
(15).
One application of GFP that has not been explored with fungi is its use
as an indicator of antimicrobial susceptibility. GFP has several
properties that are desirable for this purpose, including simplicity
and versatility for in vitro use (9). GFP is intrinsically fluorescent, requiring no cofactors or exogenous substrates. Problems related to cell permeabilization and uptake or retention of product are
thus avoided (4, 9). GFP fluorescence also has the
advantage that it can be quantitated in situ using a variety of
techniques, including fluorescence microscopy, (37), flow
cytometry (10), and fluorimetry (3).
The ability to rapidly assess viability is important in the evaluation
of susceptibility to antimicrobial compounds. Plate count methods are
often used for this purpose but are labor-intensive and require long
incubation times. Fluorescence-based assays of cellular viability, such
as those based on fluorescein (43) or tetrazolium salt
derivatives (28), offer greater sensitivity and ease of
use. However, most of these assays rely on the ability of cells to take
up or metabolize extracellular fluorogenic compounds and therefore may
be limited by permeability of the cell membrane. In bacteria,
bioluminescence using luciferase reporter genes provides a sensitive,
noninvasive marker of cell viability (33). Bioluminescence can be measured in situ, allowing measurement of cell viability for
both planktonic (11) and surface-attached
(17) bacteria.
For fungi there are no reports of the use of real-time, noninvasive
reporters of cellular viability in the presence of antimicrobial compounds. Such a technique would have broad applications in
environmental, industrial, and medical mycology. We are interested in
monitoring cell viability in Aureobasidium pullulans because
it is the predominant organism causing defacement and biodeterioration
of plasticized polyvinylchloride (pPVC) (14, 40). The
ability to rapidly assess viability of A. pullulans on pPVC
is important in the evaluation of biocides that provide protection
against biodeterioration of pPVC. The data presented here demonstrate a
strong correlation between GFP fluorescence and cell viability in
A. pullulans and suggest that this technique has
considerable potential for the rapid and real-time evaluation of fungal
susceptibility to antimicrobial compounds.
 |
MATERIALS AND METHODS |
A. pullulans (de Bary) Arnaud.
A.
pullulans strain PRAFS8 was provided by Avecia Biocides,
Manchester, United Kingdom, and was maintained on malt extract agar. To
produce blastospores, cultures were grown to mid-log phase in 80 ml of
malt extract broth by incubation at 25°C for 18 h with shaking
at 200 rpm. A. pullulans blastospore suspensions were
prepared in citric acid buffer (pH 5). This buffer was prepared by
mixing separate solutions of citric acid (5.3 g liter of deionized water
1) and
Na2HPO4 (7.1 g liter of
deionized water
1) to the appropriate pH.
Blastospores were washed three times by centrifugation at 36,000 × g for 5 min and resuspended in buffer to an optical
density at 540 nm of 1.0. For long-term storage, blastospores were
frozen at
80°C in a 20% (vol/vol) glycerol solution.
Transformation.
Expression vector pTEFEGFP
(37), containing a red-shifted mutant GFP cDNA (pEGFP-1;
Clontech) downstream of an A. pullulans translation
elongation factor promoter, was introduced into A. pullulans
by cotransformation with pAN7-1, a vector conferring hygromycin
resistance (26). Protoplasts were prepared and transformed as previously described (39) with 10 µg of both pTEFEGFP
and pAN7-1, and transformants were selected on potato dextrose agar (Oxoid) containing 1 M sorbitol and 100 µg of hygromycin B
ml
1. Transformants were screened for GFP
fluorescence using an Olympus BH-2 epifluorescence microscope equipped
with an HBO 100-W mercury arc lamp and a fluorescein isothiocyanate
filter set. All transformants exhibiting fluorescence were subcultured
onto malt extract agar containing 100 µg of hygromycin B
ml
1. Integration of plasmid DNA in
transformants was confirmed by Southern analysis (32). To
determine if integration of the vector affected the specific growth
rate, the transformants and the parental strain were grown in batch
culture in 80 ml of malt extract broth at 25°C with shaking at 200 rpm, and the optical density at 600 nm was determined periodically. The
specific growth rates were determined during the log phase from the
slope of a plot of the natural log of optical density versus time.
Measurement of GFP fluorescence of suspended blastospores.
Suspensions of transformed A. pullulans blastospores were
prepared as described above. Aliquots (1 ml) of blastospores were transferred to cuvettes, and GFP fluorescence was quantified using a
Hitachi F2000 fluorescence spectrophotometer with excitation at 485 nm
and emission at 510 nm. Standard curves of optical density and viable
cell number versus fluorescence were prepared by making serial
dilutions of transformed blastospores in citrate-phosphate buffer (pH
5). Untransformed A. pullulans blastospores were used as a
control. Viable cells were enumerated by plating serial dilutions onto
malt extract agar and incubating at 25°C for 3 days. To investigate the reproducibility (interbatch variation) of GFP fluorescence levels,
fluorescence measurements were made from blastospore suspensions prepared from five separate cultures and data were subjected to analysis of variance.
Influence of biocides on GFP fluorescence and cell viability of
suspended blastospores.
The following biocides were obtained from
Avecia Biocides: 2-n-octyl-4-isothiazolin-3-one (OIT),
2,3,5,6-tetrachloro-4-(methylsulfonyl)pyridine (TCMP),
10,10'-oxybisphenoxyarsine (OBPA),
N-(trichloromethylthio)phthalimide (NCMP), and
n-butyl-1,2-benzisothiazolin-3-one (BBIT). Stock solutions of these biocides were prepared in dimethyl sulfoxide (DMSO) so that
the final concentration of DMSO added to blastospore suspensions was
2% (vol/vol). Sodium hypochlorite was obtained from BDH (Darmstadt, Germany) and was added directly to Ap1 gfp cells. Various
concentrations of the biocides OIT and sodium hypochlorite were added
to 30-ml aliquots of blastospores in 50-ml centrifuge tubes (Falcon).
Fluorescence measurements from three replicate tubes were made at
various intervals for each biocide concentration, and tubes were shaken
throughout using a rotating mixer set at 30 rpm (model SB1; Stuart
Scientific, Redhill, United Kingdom). To monitor viable cell numbers
during biocide treatment, 10-ml aliquots of blastospore suspensions
were treated with either 100 µg of OIT ml
1 or
75 µg of sodium hypocholorite ml
1 for
different time periods. At specific time points, fluorescence measurements were made from each tube and cells were immediately washed
three times in citrate-phosphate buffer (pH 5) by centrifugation at
3,600 × g prior to plating on malt extract agar for
enumeration. With sodium hypochlorite, sodium thiosulfite neutralizer
solution was added to suspensions to a final concentration of 1%
(wt/vol) before washing. These experiments were replicated on at least two separate occasions. The influence of an additional range of industrial biocides on GFP fluorescence and cell viability was determined at the working concentration at which they are normally incorporated within pPVC. These concentrations were as follows (in
micrograms milliliter
1): TCMP, 50; OIT, 500;
BBIT, 750; OBPA, 50; and NCMP, 500. For each biocide, GFP fluorescence
was monitored over a period of 4 h, after which time cells were
washed three times as described above and plated on malt extract agar
for enumeration.
Influence of external pH on GFP fluorescence and cell viability
of suspended blastospores.
The biocide OIT was used to investigate
the influence of external pH on loss of GFP fluorescence and viable
cell numbers. Blastospore suspensions were prepared in
citrate-phosphate buffer adjusted to pH values in the range of 4 to 8. Aliquots (10 ml) of cells were treated with 100 µg of OIT
ml
1 (100 ppm) for 1 h. After this time,
fluorescence measurements were made from each of three aliquots and
cells were immediately washed three times in buffer at the appropriate
pH by centrifugation at 3,600 × g for 5 min. Numbers
of viable cells remaining at each pH value were then determined by
plating on malt extract agar. GFP fluorescence and CFU counts were
compared relative to those of controls without added OIT at each pH value.
Influence of OIT incorporated into pPVC on GFP fluorescence.
The pPVC was formulated as previously described (40)
except that OIT was incorporated with the other components to give a
final concentration of 500 ppm. Disks 4.5 mm in diameter were punched
from the pPVC sheet, washed in 2% (vol/vol) Lipsol detergent, rinsed
thoroughly in deionized water, and placed in the bottoms of wells of a
96-well flexible assay plate (Becton Dickinson). For determining loss
of fluorescence of A. pullulans attached to pPVC containing
OIT, blastospores were prepared as described above and resuspended in
citrate-phosphate buffer (pH 5) to a concentration of 1.8 × 106 blastospores ml
1, and
200 µl was placed on the surfaces of the disks. Disks were removed at
various time intervals up to 27 h and examined with an Olympus
BH-2 epifluorescence microscope equipped with an HBO 100-W mercury arc
lamp and a fluorescein isothiocyanate filter set, and images were
recorded with a Matrox Rainbow Runner pixel grabber. Images were
thresholded to remove cells with a fluorescence intensity of less than
10% of the background, and the number of fluorescent cells was
estimated as the percentage of the total area. Two separate fields of
view were recorded per disk, and four disks per time point were chosen
at random.
 |
RESULTS |
Transformation and colony screening.
After incubation for 5 days, five putative transformants growing on hygromycin B-supplemented
medium were identified by epifluorescence microscopy. Southern analysis
with genomic DNAs derived from two of the transformants (termed Ap1
gfp and Ap2 gfp) and the parental strain
confirmed integration of pTEFEGFP (data not shown) at separate locations but at a single site. Both of these transformants showed very
bright cytoplasmic fluorescence similar to that described by Vanden
Wymelenberg et al. (37). No significant difference (P > 0.001) between the specific growth rates of the
untransformed parent and those of AP1 gfp and AP2
gfp (results not shown) was found. Fluorescence
spectrophotometry showed that transformant Ap1 gfp had the
highest fluorescence levels, and this transformant was selected for
biocide susceptibility studies).

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FIG. 1.
Influence of the biocides OIT and sodium hypochlorite on
GFP fluorescence in Ap1 gfp blastospores. (a) OIT at
concentrations of 0 ( ), 50 ( ), 100 ( ), 350 ( ), and 500 ( ) µg ml 1. (b) Sodium hypochlorite at concentrations
of 0 ( ), 25 ( ), 50 ( ), 75( ), and 125 ( ) µg of
available chlorine ml 1. Each point represents the mean of
three replicate measurements ± standard error of the mean.
(Errors were within the heights of the symbols.)
|
|
GFP fluorescence of suspended blastospores.
GFP fluorescence
in Ap1 gfp blastospores was linear with respect to both
optical density and viable cell number
(r2 > 0.99) (results not shown).
Untransformed A. pullulans showed a slight background
fluorescence at high cell densities, probably due to scattering of
incident light. Significant interbatch variation (P < 0.001) occurred among mean fluorescence values from five separate
cultures of blastospores. The individual mean and standard deviation
for fluorescence values among the five cultures ranged between 127 ± 1 and 197 ± 5 relative fluorescence units. In order to
eliminate this source of variation, each subsequent experiment was
completed from a single batch of blastospores.
Influence of biocides on GFP fluorescence of suspended
blastospores.
Both of the biocides OIT and sodium hypochlorite
caused rapid losses of GFP fluorescence from Ap1 gfp cells
in a concentration-dependent manner (Fig. 1). In the presence of 500 µg of OIT ml
1, fluorescence levels fell by
82% in 30 s and then decreased more slowly to reach a plateau at
95% loss of fluorescence by 25 min (Fig. 1a). Interestingly, the
influence of 100 µg of OIT ml
1 on
fluorescence appeared to be biphasic. During the first 17 min of
incubation, fluorescence levels fell by 30% at a rate similar to that
observed using 50 µg of OIT ml
1. However,
fluorescence levels then fell by a further 40% at an increased rate
between 17 min and 1 h of incubation. This biphasic reduction in
fluorescence was consistently observed in over five independent
experiments. In comparison with results with OIT, incubation with
sodium hypochlorite caused similar reductions in fluorescence in the
range of 15% (25 µg of available chlorine ml
1) to 90% (150 µg of available chlorine
ml
1) after 35 min (Fig. 1b). Measurements of
the effects of both biocides on GFP fluorescence were repeated on at
least three separate occasions with similar results.
Correlation between GFP fluorescence and cell viability.
To
determine whether loss of GFP fluorescence correlated with a reduction
in the number of viable cells, fluorescence measurements and CFU counts
were made at intervals after the addition of each of the biocides OIT
and sodium hypochlorite at 100 µg of OIT ml
1
and 75 µg of available chlorine ml
1,
respectively (Fig. 2). With OIT,
logarithmic decreases in the number of viable cells paralleled the loss
of GFP fluorescence, and CFU counts fell from 3.5 × 106 to 6.3 × 102 CFU
ml
1 in 1 h (Fig. 2a). Sodium hypochlorite
caused a rapid decrease in viability from 5 × 106 to 1.8 × 104 CFU
ml
1 by 30 s, and this mirrored the large
reduction in GFP fluorescence of 38% that also occurred within 30 s (Fig. 2b). With sodium hypochlorite, decreasing CFU counts reached a
plateau at 9.2 × 102 CFU
ml
1 after 10 min, while GFP fluorescence
continued to decrease slowly after this time and reached a plateau of
11% relative fluorescence after 20 min (Fig. 2b). The data for both
biocides showed a strong linear correlation
(r2 = 0.93) between loss of GFP
fluorescence and logarithmic decreases in CFU viable counts (Fig. 2c).
Measurements of GFP fluorescence loss and cell viability were made on
two separate occasions for each biocide with similar results.

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FIG. 2.
Influence of the biocides OIT and hypochlorite on loss
of GFP fluorescence and cell viability in Ap1 gfp
blastospores. (a) Influence of 100 µg of OIT ml 1. (b)
Influence of 75 µg of hypochlorite ml 1. (c) Correlation
between GFP fluorescence and numbers of viable cells during treatment
with OIT ( ) and sodium hypochlorite ( ). Each point represents the
mean of three replicate measurements ± standard error of the
mean. (Errors not shown were within the heights of the symbols.)
|
|
Influence of external pH on fluorescence and cell viability.
Losses of both fluorescence and cell viability in the presence of OIT
were highly dependent on the pH of the suspension buffer (Fig.
3). Loss of GFP fluorescence was greatest
under acidic conditions. The maximum reduction of 73% occurred at pH
4, while no significant loss of fluorescence (P > 0.001) occurred under alkaline conditions at pH 8. Fluorescence levels
remaining after treatment with OIT for 1 h increased in a linear
manner between pH 4 and 8. Loss of cell viability was also greatest at
acidic pH values, with >99.98% loss of viability at pH 4, while 39%
of cells remained viable at pH 8. There was a linear log-log
relationship between external pH and viable cell numbers remaining
after incubation with OIT for 1 h. In the absence of OIT, neither
the intensity of GFP fluorescence nor cell viability was significantly
affected between pH 4 and 8 (P > 0.001) (results not
shown).

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FIG. 3.
Influence of external pH on percent loss of GFP
fluorescence and viability of Ap1 gfp cells after
treatment with 100 µg of OIT ml 1 for 1 h. Each
point represents the mean of three replicate measurements ± standard error of the mean. (Errors not shown were within the heights
of the symbols.)
|
|
Comparison of a range of biocides at concentrations normally
used.
The kinetics of GFP fluorescence loss in the presence
of five broad-spectrum biocides commonly incorporated within pPVC is shown in Fig. 4. All of the biocides
caused greater than 60% loss of fluorescence after 4 h and caused
100% loss of viability within this period. OIT and BBIT caused a
complete reduction of fluorescence to baseline levels. Fluorescence
levels of cells incubated with DMSO without biocide fell to 90% after
4 h, and 90% of cells (5.4 × 106 CFU
ml
1) remained viable after this period.

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FIG. 4.
Influence of a range of biocides on GFP fluorescence in
Ap1 gfp blastospores. Blastospores were exposed to the
concentrations of biocide normally incorporated within pPVC: NCMP, 500 µg ml 1 ( ); OBPA, 50 µg ml 1 ( );
TCMP, 50 µg ml 1 ( ); BBIT, 750 µg ml 1
( ); OIT, 500 µg ml 1 ( ); no biocide, 2% DMSO
( ). Each point represents the mean of three replicate
measurements ± standard error of the mean. (Errors were within
the heights of the symbols.)
|
|
Influence of OIT incorporated into pPVC on GFP fluorescence.
Loss of fluorescence from blastospores of AP1 gfp attached
to the surface of pPVC containing 500 ppm of OIT was examined over a
period of 27 h. The kinetics of loss of fluorescence by
surface-attached cells was most rapid over the first 5 h, at which
point ca. 70% of cells had lost fluorescence. The percentage of
fluorescent cells continued to decline until >95% of cells had lost
fluorescence after 27 h (Fig. 5).


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FIG. 5.
Effect of incorporation of 500 ppm of OIT into pPVC on
surface-attached AP1 gfp spores. (a) Percentages of
fluorescent cells on pPVC ( ) and pPVC with 500 ppm of OIT
incorporated ( ). Each point represents the mean of five replicate
measurements ± standard error of the mean. (b) Fluorescent images
taken after 0 h (top left), 2 h (top right), 6 h (bottom
left), and 27 h (bottom right).
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|
 |
DISCUSSION |
This study is the first to demonstrate that GFP fluorescence may
be used as a real-time, noninvasive indicator of fungal susceptibility to antimicrobial agents. In bacteria, GFP fluorescence has been shown
to be rapidly reduced in the presence of a number of biocides (3,
19). Casey and Nguyen (3) observed a correlation
between loss of GFP fluorescence and loss of cell viability in
Escherichia coli, and they suggested that the technique was
useful as a rapid screen for antimicrobial compounds. However, no
detailed explanation for the loss of GFP fluorescence was provided.
Further, because of the inherent stability of GFP, this approach was
thought by Collins et al. (6) to risk falsely equating GFP
fluorescence and viability, potentially leading to some active
compounds being overlooked.
Recently, GFP has become established as a sensitive and accurate
indicator of intracellular pH (18, 20, 27). Intracellular pH is considered to be one of the most important factors in fungal physiology. Intracellular pH regulates the key enzymes in glycolysis and gluconeogenesis (16, 23) and is thought to regulate
other cell responses, including the induction of heat shock proteins (41). In Neurospora crassa, cytosolic
acidification to pH 6.5 using propionic acid resulted in complete
inhibition of growth (24), and several studies have
correlated intracellular pH with fungal cell viability (16,
38). We propose that the observed correlation between GFP
fluorescence and cell viability in this study results from the
sensitivity of GFP to intracellular pH.
Intracellular pH is regulated by the essential fungal plasma membrane
proton pump H+-ATPase (29, 30) and
has itself been suggested to be a potential target for development of
novel antifungal agents (22). Inhibition of
H+-ATPase causes rapid depolarization of the
plasma membrane, followed by intracellular acidification and cell death
(2, 12). Biocide killing and loss of intracellular pH
control will result from either a direct inhibition of
H+-ATPase, indirect loss of
H+-ATPase activity through inhibition of
respiration or other essential cell processes, or damage to the cell
membrane and modification of cell permeability. Fungistatic compounds
that inhibit growth but do not interfere with intracellular pH
regulation (1) would not be expected to cause fluorescence
loss in this system, and the fungistatic triazole drug itraconazole
caused only low levels of fluorescence loss (<20%) from Ap1
gfp cells (data not shown). Loss of GFP fluorescence due to
leaking of GFP to the external medium resulting from loss of membrane
integrity or cell lysis or due to protease degradation of the GFP
chromophore is unlikely, since microscopic observation of Ap1
gfp cells showed that neither sodium hypochlorite nor OIT
caused cell lysis. Moreover, loss of GFP fluorescence caused by OIT or
sodium hypochlorite was almost completely reversible when cells were
washed and resuspended in pH 7 buffer, although cell viability was not
restored (data not shown), indicating that the chromophore remained
intact in the cytosol. Loss of GFP fluorescence and cell viability was
found to be highly dependent on the pH of the external medium. If
intracellular pH regulation is inhibited, then it follows that lower
external pH values will cause greater intracellular acidification and
thus greater loss of fluorescence and viability. However, the activity of many biocides is also dependent on pH. For example, the active entity of sodium hypochlorite is undissociated hypochlorous acid, which
is more abundant at low pH values (35). Therefore, we chose to use OIT to investigate the effect of external pH on loss of
fluorescence and cell viability, as OIT does not possess ionizable groups that would be influenced by pH.
The measurement of GFP fluorescence described in this study proved to
be a rapid and simple procedure for monitoring viability in Ap1
gfp cells in the presence of biocides. These data suggest that GFP fluorescence at low external pH will prove useful for screening potential fungicidal agents and compounds that inhibit intracellular pH regulation. This technique also has considerable potential as a simple and economic alternative to the use of
fluorescent dyes for estimating cell viability. Another obvious
advantage of using GFP is that it can be used to quantify biocide
susceptibility in real time and with spatial resolution in situ using a
fluorescence microscope. This allows studies of the efficacy of
biocides incorporated within substrata to be studied directly without
the necessity for the removal of attached microorganisms. In this
study, the rate of cell death for 500 ppm of OIT was considerably lower
when the OIT was incorporated into the pPVC than when cells where
exposed in suspension. The time taken for a loss of 50% of
fluorescence was <1 min for suspended cells but ca. 4 h for
attached cells. This may indicate differences between the physiologies
of cells in suspension and cells attached to a surface. Such a
phenomenon has been widely reported for bacteria and is frequently
associated with an increase in resistance to antibacterial agents
(8, 42). Alternatively, the mobility and rate of leaching
of the biocide may mean that a lower concentration of biocide is
presented at the surface than when the biocide is in suspension.
Nonetheless, the reduced rate of kill of the incorporated biocide
emphasizes the importance of testing the efficacies of such biocides in situ.
 |
ACKNOWLEDGMENTS |
This work was supported by studentships supported by the BBSRC,
the Central European University, and the Foreign Commonwealth Office in
collaboration with Avecia Ltd., United Kingdom.
 |
FOOTNOTES |
*
Corresponding author. Mailing address: School of
Biological Sciences, 1.800 Stopford Building, University of Manchester,
Oxford Rd., Manchester M13 9PT, United Kingdom. Phone: 44 (0)161 275 5048. Fax: 44 (0)161 275 5656. E-mail:
geoff.robson{at}man.ac.uk.
 |
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Applied and Environmental Microbiology, December 2001, p. 5614-5620, Vol. 67, No. 12
0099-2240/01/$04.00+0 DOI: 10.1128/AEM.67.12.5614-5620.2001
Copyright © 2001, American Society for Microbiology. All rights reserved.
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