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Applied and Environmental Microbiology, February 1999, p. 626-631, Vol. 65, No. 2
0099-2240/99/$04.00+0
Copyright © 1999, American Society for Microbiology. All rights reserved.
Effect of Compressed Carbon Dioxide on Microbial Cell
Viability
E.
Debs-Louka,*
N.
Louka,
G.
Abraham,
V.
Chabot, and
K.
Allaf
Laboratoire Maîtrise des Technologies
Agro-Industrielles, Université de La Rochelle, Pôle
Sciences et Technologies, 17042 La Rochelle Cedex, France
Received 28 April 1998/Accepted 25 October 1998
 |
ABSTRACT |
In order to study the influence of compressed carbon dioxide, over
a range of pressures (1.5 to 5.5 MPa) and exposure times (up to 7 h), on the survival of Escherichia coli,
Saccharomyces cerevisiae, and Enterococcus
faecalis, a new pressurizable reactor system was conceived.
Microbial cells were inoculated onto a solid hydrophilic medium and
treated at room temperature; their sensitivities to inactivation varied
greatly. The CO2 treatment had an enhanced efficiency in
cell destruction when the pressure and the duration of exposure were
increased. The effects of these parameters on the loss of viability was
also studied by response-surface methodology. This study showed that a
linear correlation exists between microbial inactivation and
CO2 pressure and exposure time, and in it models were
proposed which were adequate to predict the experimental values. The
end point acidity was measured for all the samples in order to
understand the mechanism of microbial inactivation. The pHs of the
treated samples did not vary, regardless of the experimental
conditions. Other parameters, such as water content and pressure
release time, were also investigated.
 |
INTRODUCTION |
Carbon dioxide has a dual
physiological role in microorganisms since it can both stimulate and
inhibit cell development. The inhibitory action has been increasingly
exploited to improve the hygiene of both liquid and solid foodstuffs by
protecting them from bacterial spoilage (6, 7, 9, 20).
Blickstad et al. (3) reported the effect of carbon dioxide
on the microflora of pork and found that increasing the partial
pressure of carbon dioxide added to the packaging atmosphere prolonged
the shelf life of the meat.
The effect of compressed carbon dioxide on different types of
microorganisms has been studied by several researchers (1, 4, 5,
8-11, 15-17). Microbial inactivation by CO2 is
dependent on many parameters. Some of the experimental conditions, such as temperature, pressure, and moisture, contribute to a more effective treatment by increasing the diffusivity of CO2 (10,
11, 16, 19). Within certain limits, a longer duration of exposure
to carbon dioxide permits better sterilization; exposure time can be
decreased by increasing the temperature (1). Microbial
resistance to CO2 also depends on the type of
microorganism, the phase of growth, and the suspension medium, the last
of which can inhibit the bactericidal effect of compressed
CO2, especially in some food systems rich in proteins
(20).
Various hypotheses have been proposed to explain the microbicidal
activity of carbon dioxide. Lin et al. (13, 14) have observed that, at high pressure, supercritical carbon dioxide penetrates cells and ruptures them when it is released suddenly. They
were even able to improve the rate of disruption by repeatedly releasing the CO2 pressure. Fraser (8) has also
evoked this subject; he observed that the best microbial destruction
results were obtained when the CO2 pressure was released as
rapidly as possible. In food with a high water content, CO2
dissolves in the water to form carbonic acid, according to the
following equilibrium reactions:
Thus, dissolved CO2 acts by lowering the pH of the
medium, and the resulting acidity leads to a disturbance of some
biological systems within the cells. It was therefore suggested that
microbial inhibition was due to an alteration in the properties of the
cell (membrane, cytoplasm, enzymes, etc.) (6). However, a
reduction in the pH of the medium is not sufficient to account for the
antimicrobial action of CO2, since it shows a specific
inhibitory effect which is greater than that of the other acids used to
lower medium acidity (hydrochloric acid, phosphoric acid, etc.)
(2, 9, 12, 16). These acids do not penetrate the microbial
cells as easily as carbon dioxide.
This paper describes the feasibility of using a new pressurizable
reactor system, developed by our laboratory, to destroy microorganisms.
Our work focused on the study of the inactivation by compressed carbon
dioxide of three microorganism strains inoculated onto filter paper
disks. The parameters explored were mainly exposure time and pressure
at room temperature. The effect of each parameter was investigated in a
systematic study and followed up by response-surface methodology. The
end point acidity of the samples was determined by measuring the pH of
the suspensions in which the filter paper disks were disintegrated.
Moreover, we observed the effect of water content on cell destruction
and compared the results obtained with sudden and slow decompression rates.
 |
MATERIALS AND METHODS |
Growth of cells.
Three microbial strains were used as test
organisms: Escherichia coli IP 6532, Enterococcus
faecalis ATCC 29212, and Saccharomyces cerevisiae CBS
400. Before each test, microorganisms from cultures stored at 4°C
were grown overnight in recovery medium containing (per liter) 5 g
of peptone, 2 g of yeast extract, 5 g of NaCl, and 5 g
of glucose. The bacteria were incubated at 37°C; the yeast was
incubated at 30°C. The cell concentration in the resulting suspensions was generally about 108 CFU/ml. The absence of
contamination in the suspensions was confirmed by Gram staining.
Sample preparation.
Hydrophilic filter paper disks (50-mm
diameter, Whatman no. 1) were autoclaved at 120°C for 20 min. Just
before the tests were conducted, each microbial suspension was
aseptically dispersed onto a filter paper disk, which will retain all
the deposited suspension volume (100 µl). The inoculated disk was
placed vertically inside a sterile flask (50 ml) containing a small
Teflon-covered magnetic stirring bar and five sterile glass beads (5-mm
diameter). Flasks were kept closed until it was time to perform the experiment.
Apparatus.
The processing reactor used in this work was made
entirely of stainless steel (Fig. 1). The
reactor consisted of a pressure vessel with an internal volume of 5 liters (Fig. 1b) connected to a 1,600-liter vacuum tank (Fig. 1c); the
two tanks were separated by a large-diameter valve (Fig. 1d).
Compressed carbon dioxide was supplied from a gas cylinder (Fig. 1a)
which was linked, by a valve (Fig. 1g), to the pressure vessel. A
precision manometer (Fig. 1f), CITEC (AISI 316 TI/L), was installed in
the vessel to measure the pressure. Except where mentioned, experiments
were carried out with a sudden release of pressure, which was obtained by opening the decompression valve (Fig. 1d) between the two tanks. The
pressure in the vacuum tank could be adjusted between 5 kPa and
atmospheric pressure, and the pressure at the end of the experiment could be controlled. On the other hand, the vacuum was maintained in
the vessel before application of CO2 pressure, and this
avoided any possibility of having a CO2-air mixture at the
beginning of the experiment.

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FIG. 1.
Schematic representation of the pressurizable reactor
configuration. a, compressed CO2; b, pressure vessel; c,
vacuum tank; d, decompression valve; e, vacuum pump; f, precision
manometer; g, compression valve; h, outlet; i, pressure regulator.
|
|
Process.
Open flasks containing filter paper disks were
placed in the pressure vessel at the beginning of each experiment. The
vessel was immediately sealed, and when all the tubing connections were secured, the vacuum was established by connecting the vessel to the
vacuum tank. After the decompression valve was closed, carbon dioxide
(Air Liquide, 99.7% pure) was injected into the vessel at the selected
pressure. Microbial cells were treated at pressures ranging from 1.5 to
5.5 MPa and for various exposure times. The apparatus allows carbon
dioxide to be injected very quickly (within 10 s). The holding
time began as soon as the vessel reached the experimental pressure and
ended with a sudden (0.4-s) release of the CO2 pressure.
All of the experiments were carried out at room temperature. The flasks
in the vessel were closed and removed, and the surviving cells were
immediately counted. Before each test, the inside surfaces of the
vessel were wiped clean with cotton moistened with a 70% alcohol
solution. The reported results are the average of at least duplicate tests.
Enumeration of living microorganisms.
The viability of
S. cerevisiae, E. coli, and E. faecalis was determined by counting the number of CFU per
milliliter. Each processed disk was diluted with 30 ml of an aqueous TS
solution (1 g of tryptone per liter, 8.5 g of NaCl per liter). The
contents of the flask were then mixed well by magnetic stirring for 30 min. This mixing led to a total disintegration of the filter paper, and
the microorganisms were subsequently dispersed in the solution. The
dispersion obtained was then diluted, and 1 ml of the appropriate dilution was plated on duplicate petri dishes containing a suitable growth medium. Yeast was grown on yeast glucose agar (Biokar
Diagnostics, BK 053) (per liter: yeast extract, 5 g; glucose,
20 g; bacteriological agar, 15 g). The bacteria were grown on
nutrient agar (Biokar Diagnostics, BK 021) (per liter: meat extract,
5 g; tryptone, 10 g; NaCl, 5 g; bacteriological agar,
15 g). Colonies were counted after 24 h of incubation at
37°C (bacteria) and at 30°C (yeast). Microbial cells in the control
samples were counted by the same procedures described for treated
samples. The acidity of each inoculated disk was expressed by measuring
the pH of the TS solution in which the filter paper was suspended after
its disintegration. Measurements were realized with an electrode
connected to a pH meter (pH 539, Wissenschaftlich-Technische-Werkstätten). Whenever necessary, the
water content of the inoculated disks was determined at 100°C with an
infrared balance (Mettler LP16).
Design of experiments.
Response surface is a statistical
methodology which consists of two distinct parts, the design of the
experiment and the analysis of the data (18). As for the
experimental design, two factors, CO2 pressure
(P) and exposure time (t), were studied at five
levels. The response for each treatment level is the response variable. It was assumed that the main response variables were the rate of
inactivation and the acidity. Response-surface methodology is used to
study the relationship between the response variables and the factors;
it also allows a mathematical model to be developed that can predict
the value of the response variable for given levels of pressure and
exposure time. A central composite design with two factors was used
(Table 1). This set of designs consists of a full or fractional two-level experiment (coded as ±1), designed to value all of the linear and interaction terms, and of center points
and star points (coded as 0 and ±
, respectively) used to estimate
the quadratic terms (18). This randomized design yielded 10 experiments with 4 (22) factorial points, 4 (22) star points with
= 1.68, and 2 replications of the
center point. The levels of the two factors were chosen on the basis of
preliminary trials. Response-surface contours and other statistical analyses were obtained by the appropriate procedures described in
STATGRAPHICS Plus 1.4 (Manugistics, Inc., Rockville, Md.).
The response variable
Y was experimentally measured. In our
case, a second-degree polynomial equation was assumed to approach
the
true function, suggesting an interaction between the two factors,
Y =
0 +
1x1 +
2x2 +
11x12 +
22x22 +
12x1x2, where
0,
1,
2,
11,
22, and
12 are
coefficients
for the coded model and
x1 and
x2 are the coded factors related
to
P
and
t, respectively. The linear relationship is expressed
by
the equations
x1 = 2(
P
P*)/
d1 and
x2 = 2(
t
t*)/
d2, where
* is the mean of the factorial levels
and
d1 and
d2 are the
differences
between the low and high levels, respectively, of the
factor;
x1,
x2 
[

1;+1],
P 
[30;50], and
t 
[90;300].
 |
RESULTS AND DISCUSSION |
Systematic study of pressure and exposure time.
The rate of
inactivation of the three microorganisms as a function of exposure time
was expressed as the logarithm of the ratio of surviving cells after
treatment with CO2 (N) to the cell count in the
control culture (N0) (Fig.
2). The error of the initial countable
population (N0) of an inoculated filter paper
disk was about 25% (12 replicates). The treatment pressure chosen was
5 MPa. Zero time of treatment represents the control samples. The inactivation of the microbial cells was enhanced by increasing the
exposure time. The curve for each strain has a characteristic shape
that defines its own resistance. E. coli was destroyed the most quickly. The survival curves showed that E. coli was
inactivated by about 3.6 log cycles after 60 min of treatment, whereas
only 1.5-log and 0.2-log inactivation occurred for S. cerevisiae and E. faecalis, respectively. Experimental
plots corresponding to the inactivation of E. faecalis could
be placed on a straight line, showing a linear regression with a
158.7-min D value (decimal reduction time). The mechanism of
destruction, ruled by a first-order kinetics, agreed with results
obtained by Cuq et al. (5) at constant pressure (0.6 MPa)
and temperature (55°C). Carbon dioxide under pressure exhibited a
different effect against S. cerevisiae and E. coli. The results presented survival curves of two linear stages.
The rate of inactivation is rapid at first, with a significantly slower
rate at the later stage. The two biphasic curves showed an inflexion
point which occurred after about 90 min of exposure time. These results
suggest that the microorganisms were destroyed more easily at the first
straight portion; the second one involved an increase in the
destruction resistance. At higher pressure and temperature, Lin et al.
(15) and Ballestra et al. (1) have reported the
presence of the first linear regression in the kinetics of the
inactivation of S. cerevisiae and E. coli,
respectively. But in their studies, this stage was preceded by an
earlier one with a slower rate of inactivation; it corresponded to
little values of exposure time (<30 min) not exploited in this paper.

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FIG. 2.
Rate of destruction of different strains of
microorganisms as a function of exposure time at a CO2
pressure of 5 MPa.
|
|
Figure
3 illustrates the numbers of
surviving cells as a function of CO
2 pressure. Experiments
showed that the inactivation
rates of the three microbial strains
appeared insensitive to pressures
below 3.5 MPa. The beginning of the
inactivation did not occur
at the same pressure; it was strain
dependent.
E. coli had, once
more, the least pressure
resistance. Only a slight effect on
E. faecalis cells was
noted. The drop in viability may have occurred,
for each strain, when
the minimal required pressure allowed carbon
dioxide to penetrate into
the cells during the 30-min incubation
period.

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FIG. 3.
Rate of destruction of different strains of
microorganisms as a function of CO2 pressure with 30 min of
exposure time.
|
|
Methodology of response surfaces.
The effects of the two
factors (P and t) were studied only with E. coli and S. cerevisiae; E. faecalis was much
more resistant than these two strains, and a very slow rate of
destruction occurred at the explored levels. Analysis of variance
showed that the destruction rate, expressed as log
N/N0, was dependent on these two factors, which
confirms our results obtained previously. The regression coefficients
are shown in Table 2, where the
P values (probability) should be less than 0.05 to indicate
whether a correlation exists between the two factors and the response
variable.
The equations describing the response surfaces are as follows: for
E. coli, log
N/
N0 = 10.66

3.84
P 
0.023
t + 0.28
P2 + 0.00005
t2 
0.001
Pt, with
R2 = 0.91; for
S. cerevisiae, log
N/
N0 =

6.66 + 3.96
P + 0.016
t 
0.6
P2 
0.00001
t2 
0.0046
Pt, with
R2 = 0.98.
Table
2 showed that the rate of destruction of the two microbial
strains could have a linear correlation with CO
2 pressure
and exposure time. These data were reflected by the
P
values.
Moreover, in the case of
S. cerevisiae,
CO
2 pressure had a quadratic
effect on the response
variable, as well as a little two-factor
interaction. Exposure time had
no significant quadratic relationship
with the rate of destruction. The
coefficients of determination
(
R2) revealed that
the models were adequate and that they predicted
the experimental
values.
Response surfaces and contour plots of the rate of destruction are
presented in Fig.
4. The numbers on the
contour plots showed
log
N/
N0 values.

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FIG. 4.
Response surfaces and contour plots for the rate of
destruction of E. coli (a) and S. cerevisiae (b)
at different levels of independent variables.
|
|
Compressed CO
2 was highly toxic to both microbes. The
microbial inactivation was affected and improved more by increasing
CO
2 pressure than by prolonging exposure time. The exposure
time
had little effect, particularly at the lowest pressure. Its effect
was enhanced by increasing CO
2 pressure; this observation
is more
clear in the case of
S. cerevisiae, for which the
inactivation
was negligible at 3 MPa. The effect of CO
2
pressure was more marked
even at the shortest exposure times. For
example,
E. coli populations
were reduced 2.5 and 4 logs by
increasing the CO
2 pressure from
3 to 5 MPa after 90 and
330 min of exposure time,
respectively.
The experimental data demonstrated that increasing the CO
2
pressure and exposure time reduced microbial cell numbers
(
9),
even if the microbes were inoculated on hydrophilic
disks. The
three microorganisms differed in their resistances to the
inhibitory
effect of carbon dioxide (
16). This difference in
sensitivity
could be related to their cell envelope and its carbon
dioxide
permeability. Higher pressures and longer exposure times might
favor the solubility of CO
2, which acts by increasing the
acidity
of the suspension medium (
17). Thus, the observed
microbicidal
effect is due not only to the experimental conditions but
also
to the specificity of the gas used (
20). Pressurization
with
a mixture of N
2 and O
2 (80%-20%) at 8.5 MPa for 4 h had no antimicrobial
effect and did not reduce the
counts of any of the three
strains.
The efficiency of the newly developed reactor system in microbial
inactivation by compressed CO
2 has been demonstrated. The
reactor concept offers the advantage of being both a simple and
a safe
process, with controlled rates of compression and decompression.
The
results obtained are of particular interest for industrial
applications. The filter paper disk is a solid medium, and the
feasibility of inactivation in microbial suspension has also been
demonstrated. These results have encouraged us to pursue this
study
with different types of food or other products with a high
value added
tax (VAT) value. Some products demand a nonthermal
treatment for
sterilization, since heat may cause undesirable
alterations in their
quality.
End-point acidity.
The second response variable investigated
with the same experimental design was the variation in acidity of the
samples before and after treatment. Building on the previous work, the
effect of acidity and its correlation with the rate of destruction were investigated. The results of these measurements were practically the
same for both strains, and so the average values were reported in Table
3. The pHs of the treated samples were
the same, regardless of the treatment pressure and exposure time.
The same drop in pH, compared with the control sample (pH 6.8), was
observed in all of the experiments. Since CO
2 dissolves
in
aqueous solution to form an acid, pH was lower after each treatment,
but with further increases in experimental condition values, the
measured pHs did not change significantly. All the
P values
calculated
by the experimental design were greater than 0.1, confirming
that
the end-point acidity was not a function of the pressure or the
exposure time. The lowered acidity may help increase cell permeability
to ease cellular penetration of the fluid (
16). This drop in
pH will irreversibly inhibit essential metabolic systems, as suggested
by Haas et al. (
9).
Influence of moisture.
We conducted further experiments with
E. coli and S. cerevisiae to investigate the
influence of water content of the samples on microbial inactivation.
Six filter papers were, as usual, inoculated with the microbial
suspension, but the water contents of five of them were increased by
addition of different volumes of sterile distilled water. The water
contents of the six filter papers were 37, 52, 62, 67, 72, and 75%.
All of these samples were treated under the same experimental
conditions (5 MPa over 300 min). After treatment, it appeared that the
rate of destruction and the drop in pH were similar for all the samples
and for the two microbial strains (data not shown). A minimum of water
content seems to allow the mechanism of inactivation. Thus, to clearly
show the effect of a small water content, two filter papers were
inoculated with an E. coli suspension and treated at 5 MPa
for 300 min. Before treatment, one of the samples was dried at 30°C
for 7 h; the second kept its initial water content.
The results in Table
4 indicated a
remarkable decrease in the rate of destruction for the dried filter
paper and showed that
the treatment was much less effective, whereas
the acidity had
a similar decrease in both cases. Microbial
inactivation strongly
depends on the water content. Some researchers
(
9,
11,
19)
demonstrated that moisture was essential to the
antimicrobial
action of carbon dioxide under pressure. Lin et al.
(
16,
17)
suggested that swollen cell walls, due to the
presence of water,
become more CO
2 permeable.
Influence of the rate of decompression.
We have also looked at
the effect of the rate of decompression. All of the experiments in this
work were undertaken with as rapid a release of pressure as possible:
only 0.4 s was necessary to obtain a vacuum in the processing
reactor. In order to evaluate the influence of this factor, comparative
pressurization tests were performed with three different decompression
times: 0.4 s, 15 min, and 50 min. The experiments were conducted
for 195 min at 4 MPa for all microbial strains studied. The
microorganism counts after treatment showed that there was no
significant difference, with similar rates of destruction in the three
experiments. Although the rate of decompression had no effect in our
study, some researchers (8, 13, 14) have insisted that rapid
decompression is a parameter that enhances the inactivation process.
The explanation that we suggest is that these authors worked under
CO2-supercritical conditions (pressure and temperature), in
which the fluid penetrates more easily into the cells. Rapid
decompression may provoke cell rupture as a result of the expansion of
CO2 within the cells. This hypothesis will require further investigation.
 |
ACKNOWLEDGMENT |
We are grateful to the regional council of Poitou-Charentes,
France, for their financial support.
 |
FOOTNOTES |
*
Corresponding author. Mailing address: Laboratoire
Maîtrise des Technologies Agro-Industrielles, Université
de La Rochelle, Pôle Sciences et Technologies, Avenue Marillac,
17042 La Rochelle Cedex, France. Phone: 33-5-46-45-86-15. Fax:
33-5-46-45-86-16. E-mail: edebs{at}lmtai.univ-lr.fr.
 |
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Applied and Environmental Microbiology, February 1999, p. 626-631, Vol. 65, No. 2
0099-2240/99/$04.00+0
Copyright © 1999, American Society for Microbiology. All rights reserved.
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