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Applied and Environmental Microbiology, September 1999, p. 4094-4098, Vol. 65, No. 9
0099-2240/99/$04.00+0
Copyright © 1999, American Society for Microbiology. All rights reserved.
Bactericidal Activity of Photocatalytic
TiO2 Reaction: toward an Understanding of Its Killing
Mechanism
Pin-Ching
Maness,1,*
Sharon
Smolinski,1
Daniel M.
Blake,1
Zheng
Huang,1
Edward J.
Wolfrum,1 and
William
A.
Jacoby2
The National Renewable Energy Laboratory,
Golden, Colorado 80401-3393,1 and
Department of Chemical Engineering, University of
Missouri-Columbia, Columbia, Missouri 652112
Received 5 February 1999/Accepted 29 June 1999
 |
ABSTRACT |
When titanium dioxide (TiO2) is irradiated with near-UV
light, this semiconductor exhibits strong bactericidal activity. In this paper, we present the first evidence that the lipid peroxidation reaction is the underlying mechanism of death of Escherichia
coli K-12 cells that are irradiated in the presence of the
TiO2 photocatalyst. Using production of malondialdehyde
(MDA) as an index to assess cell membrane damage by lipid peroxidation,
we observed that there was an exponential increase in the production of
MDA, whose concentration reached 1.1 to 2.4 nmol · mg (dry
weight) of cells
1 after 30 min of illumination, and that
the kinetics of this process paralleled cell death. Under these
conditions, concomitant losses of 77 to 93% of the cell respiratory
activity were also detected, as measured by both oxygen uptake and
reduction of 2,3,5-triphenyltetrazolium chloride from succinate as the
electron donor. The occurrence of lipid peroxidation and the
simultaneous losses of both membrane-dependent respiratory activity and
cell viability depended strictly on the presence of both light and
TiO2. We concluded that TiO2 photocatalysis promoted peroxidation of the polyunsaturated phospholipid component of
the lipid membrane initially and induced major disorder in the E. coli cell membrane. Subsequently, essential functions that rely
on intact cell membrane architecture, such as respiratory activity,
were lost, and cell death was inevitable.
 |
INTRODUCTION |
The use of photocatalysts to destroy
organic compounds in contaminated air or water has been extensively
studied for the last 25 years. The P25 formulation of titanium dioxide
(TiO2) from Degussa Chemical Company (Teterboro, N.J.) is
the most widely used photocatalyst. TiO2 in the anatase
crystal form is a semiconductor with a band gap of 3.2 eV or more. Upon
excitation by light whose wavelength is less than 385 nm, the photon
energy generates an electron hole pair on the TiO2 surface.
The hole in the valence band can react with H2O or
hydroxide ions adsorbed on the surface to produce hydroxyl radicals
(OH·), and the electron in the conduction band can reduce
O2 to produce superoxide ions
(O2
). Both holes and OH· are extremely
reactive with contacting organic compounds. Detection of other reactive
oxygen species (ROS), such as hydrogen peroxide
(H2O2) and singlet oxygen, has also been reported. Complete oxidation of organic compounds and Escherichia coli cells to carbon dioxide can be achieved (17, 19).
In the absence of O2 or a suitable electron acceptor, no
photocatalytic reaction occurs due to the extremely deleterious
electron hole recombination processes (34). The detailed
mechanism of the TiO2 photochemical reaction and the
various ROS produced have been well-documented (3, 14, 22).
In 1985, Matsunaga and coworkers reported that microbial cells in water
could be killed by contact with a TiO2-Pt catalyst upon
illumination with near-UV light for 60 to 120 min (20). Later, the same group of workers successfully constructed a practical photochemical device in which TiO2 powder was immobilized
on an acetylcellulose membrane. An E. coli suspension
flowing through this device was completely killed (21). The
findings of Matsunaga et al. created a new avenue for sterilization and
resulted in attempts to use this novel photocatalytic technology for
disinfecting drinking water and removing bioaerosols from indoor air
environments (5, 12, 16, 25, 30, 34). Killing of cancer
cells with the TiO2 photocatalyst for medical applications
has also been reported (6). The previous work on
photocatalytic disinfection and cell killing has recently been reviewed
(3). Because of the widespread use of antibiotics and the
emergence of more resistant and virulent strains of microorganisms,
there is an immediate need to develop alternative sterilization
technologies. The TiO2 photocatalytic process is a
conceptually simple and promising technology.
Although a wealth of information has demonstrated the efficacy of the
biocidal actions of the TiO2 photocatalyst, the fundamental mechanism underlying the photocatalytic killing process has not been
well-established yet. An in-depth understanding of the mechanism is
essential in order to devise a strategy and apply the technology in a
practical system to efficiently kill a wide array of microorganisms. The first mechanism proposed was the mechanism proposed by Matsunaga and coworkers, who believed that direct photochemical oxidation of
intracellular coenzyme A to its dimeric form was the root cause of
decreases in respiratory activities that led to cell death (20,
21). They reported that the extent of killing was inversely proportional to the thickness and complexity of the cell wall. Saito
and workers (25) proposed that the TiO2
photochemical reaction caused disruption of the cell membrane and the
cell wall of Streptococcus sobrinus AHT, as shown by leakage
of intracellular K+ ions that paralleled cell death.
Leakage of intracellular Ca2+ ions has also been observed
with cancer cells (26, 27). Perhaps more direct evidence
that outer membrane damage occurs was described recently by Sunada et
al. (31), who studied E. coli and found that the
endotoxin, an integral component of the outer membrane, was destroyed
under photocatalytic conditions when TiO2 was used.
The lack of data regarding a specific mechanism of cell death prompted
us to investigate the effect of photocatalytic oxidation on cell
membrane polyunsaturated phospholipids. Hydroxyl radicals generated by
the TiO2 photocatalyst are very potent oxidants and are
nonselective in reactivity (22). Because of their high
levels of reactivity, they are also very short lived. When irradiated TiO2 particles are in direct contact with or close to
microbes, the microbial surface is the primary target of the initial
oxidative attack. Polyunsaturated phospholipids are an integral
component of the bacterial cell membrane, and the susceptibility of
these compounds to attack by ROS has been well-documented (13,
18). Many functions, such as semipermeability, respiration, and
oxidative phosphorylation reactions, rely on an intact membrane
structure. Lipid peroxidation is, therefore, detrimental to all forms
of life. In this paper, we report for the first time that the
TiO2 photocatalytic reaction indeed causes the lipid
peroxidation reaction to take place and that, as a result, normal
functions associated with an intact membrane, such as respiratory
activity, are lost. We propose that the loss of membrane structure and,
therefore, membrane functions is the root cause of cell death when
photocatalytic TiO2 particles are outside the cell.
 |
MATERIALS AND METHODS |
Culture of microorganisms.
E. coli K-12 strain
ATCC27325 was grown aerobically in 100 ml of Luria-Bertani broth at
30°C on a rotary shaker (200 rpm) for 18 h. The cells used for
respiratory measurements were cultured at 25°C. E. coli
cells were harvested by centrifugation at 7,800 × g
for 15 min, washed, and suspended in sterile deionized water. The final
optical density at 660 nm of the suspension was determined by measuring
the turbidity with a Spectronic 21D spectrophotometer (Milton Roy Co.).
The correlation between optical density at 660 nm and amount of cell
mass produced was determined by measuring the dry weights of washed
cells at different stages of cell growth.
Photocatalytic reaction.
TiO2 (P25 formulation;
Degussa) particles with an average composition of 75% anatase and 25%
rutile and a surface area of about 50 m2 g
1
were used for all experiments. A 100-mg ml
1 stock
suspension was freshly prepared with deionized water and kept in the
dark. TiO2 was added to cells in water immediately prior to
the reaction. The final concentrations ranged from 0.1 to 1 mg
ml
1. All experiments were conducted in continuously
stirred aqueous slurry solutions to ensure maximal mixing and to
prevent settling of the TiO2 particles. Overhead
illumination by long-wavelength UV light was provided by two 40-W black
light tubes (type F40/BL-B; Sylvania) with a spectral maximum at 356 nm. The light intensity reaching the surface at the center of the glass
reaction vessel was approximately 8 W m
2; this was
determined by using a Blak-Ray UV meter with the peak intensity at 365 nm (model J-221 long-wavelength UV meter; UVP Inc., San Gabriel,
Calif.). The reaction was terminated by removing the reaction vessel
from the light, and the reaction mixture was used immediately for
various assays, as described below. Dark control samples were covered
with black cloth and stirred under the same conditions.
Cell viability.
The numbers of viable cells in cell
suspensions that were subjected to the TiO2-light treatment
or were not subjected to the TiO2-light treatment were
determined by plating 30- to 100-µl aliquots of serially diluted
suspensions onto Luria-Bertani agar plates. The plates were incubated
at 30°C for 24 h, and then the numbers of colonies on the plates
were counted.
Determination of lipid peroxidation.
Formation of
malondialdehyde (MDA) was used as an index to measure lipid
peroxidation. MDA was quantified based on its reaction with
thiobarbituric acid (TBA) to form a pink MDA-TBA adduct
(10). One milliliter of a TiO2-cell slurry was
mixed with 2 ml of 10% (wt/vol) trichloroacetic acid, and the solids
were removed by centrifugation at 11,000 × g for 35 min and then for an additional 20 min to ensure that the
TiO2 particles, cells, and precipitated proteins were
completely removed. Three milliliters of a freshly prepared 0.67%
(wt/vol) TBA (Sigma Chemical Co.) solution was then added to the
supernatant. The samples were incubated in a boiling water bath for 10 min and cooled, and the absorbance at 532 nm was measured with a Cary
5E spectrophotometer (Varian Instruments, Sugar Lane, Tex.). The
concentrations of the MDA formed were calculated based on a standard
curve for the MDA (Sigma Chemical Co.) complex with TBA; the
E532 was 49.5 mM
1
cm
1. The extent of lipid peroxidation was expressed in
nanomoles of MDA per milligram (dry weight) of cells.
Determination of cellular respiration.
After the
photocatalytic reaction, a 300-ml TiO2-cell slurry
containing 0.5 mg of TiO2 ml
1 and 1.2 × 108 CFU ml
1 was centrifuged at
5,000 × g for 45 min, and the pellet was resuspended in 15 ml of sterile H2O and used for the following assays.
An oxygen uptake assay was conducted in a 2-ml water-jacketed chamber fitted with a model 5331 Clark type oxygen electrode (Yellow Springs Instrument Co., Yellow Springs, Ohio). The reaction mixture contained 2 ml of resuspended TiO2-cell slurry and 12.5 mM potassium
phosphate buffer (pH 7.0). The reaction was initiated by injecting 50 µl of either 1 M sodium succinate (pH 7.0) or 1 M glucose as the electron donor. The reduction of 2,3,5-triphenyltetrazolium chloride (TTC) to its reduced product, 2,3,5-triphenyltetrazolium formazan (TTF), was measured as described by Smith and Pugh (29),
with minor modifications. A 1-ml aliquot of the resuspended
TiO2-cell slurry was mixed with 1 ml of a 1% (wt/vol) TTC
(Sigma Chemical Co.) solution, and then 50 µl of 0.5 M potassium
phosphate buffer (pH 7.0) and 50 µl of 1 M sodium succinate (pH 7.0)
were added. The mixture was incubated for 60 min at 20°C in the dark.
After incubation, samples were centrifuged at 8,000 × g for 15 min, and the pellets were extracted with 3 ml of methanol
for 15 min with shaking. The extracted cells were then removed by
centrifugation at 8,000 × g for 15 min, and the
absorbance at 485 nm of the red supernatant was measured with a Cary 5E
spectrophotometer. The concentrations of the TTF formed were determined
based on a standard curve for freshly prepared TTF (Sigma Chemical Co.)
in methanol, which had an E485 of 27.5 mM
1 cm
1. The rate of O2 or TTC
reduction was expressed in nanomoles of O2 or TTF per
minute per milligram (dry weight) of cells.
 |
RESULTS |
Effects of cell and TiO2 concentrations on
disinfection.
In order to study the killing mechanism, a high
concentration of E. coli cells is required to examine any
changes in cellular processes resulting from TiO2 biocidal
action. To determine the optimal dose of TiO2 for a certain
cell concentration, photocatalytic reactions were carried out with cell
concentrations ranging from 9.1 × 102 to 5 × 108 CFU ml
1 and TiO2
concentrations ranging from 0.1 to 1 mg ml
1 (Table
1). After 30 min of irradiation with
near-UV light in the presence of 0.1 mg of TiO2
ml
1, 92 to 98% of the E. coli cells were
killed when the initial cell concentration was less than
105 CFU ml
1. This low dose of
TiO2, however, did not effectively kill the cells in a
suspension containing 108 CFU ml
1. However,
when this cell concentration was used and the TiO2 dose was
increased to 0.5 or 1 mg ml
1, there was a significant
improvement in the killing efficiency. At a still higher cell
concentration (5 × 108 CFU ml
1), the
killing efficiency observed with 1 mg of TiO2
ml
1 was much lower. TiO2 concentrations
greater than 1 mg ml
1 resulted in decreases in the
killing efficiency. This was probably due to shading of the cells by
the TiO2 particles so that light in the
TiO2-cell slurry became limiting. Thus, the most effective TiO2 concentration for killing E. coli cells at
concentrations ranging from 103 to 108 CFU
ml
1 was 1 mg ml
1. Nonetheless, due to
TiO2 interference with various cellular assays, a lower
TiO2 concentration had to be used in several of the studies
described below.
Effect of irradiated TiO2 on lipid peroxidation.
To estimate membrane damage, we examined production of MDA, a product
of lipid peroxidation, by E. coli cells. The effects of
irradiated TiO2 on MDA formation in E. coli
cells under various conditions were determined (Fig.
1). When E. coli cells
(2.5 × 108 CFU ml
1) were incubated with
0.1 mg of TiO2 ml
1 in a slurry and were
subjected to illumination (8 W m
2) for 30 min with
continuous stirring, approximately 2.4 nmol of MDA per mg of cell mass
was extracted. However, when the TiO2 slurry was not
illuminated, only 0.28 nmol of MDA per mg was detected. When no
TiO2 was present, control cells in the dark and in the light produced comparable low levels of MDA, indicating that the amount
of preexisting MDA was negligible and that UV light alone at the
wavelength and duration used did not result in a significant level of
lipid peroxidation. The lipid peroxidation process, therefore, depends
on the presence of both light and TiO2. A photocatalysis experiment in which an aged TiO2 solution stored in the
presence of room light resulted in a lower level of MDA in the light
and a higher background value in the dark. As a result, a freshly prepared TiO2 solution was used for subsequent experiments
in which the effect of photocatalytic activity was examined. Although a
large amount of TiO2 yielded more MDA in the light, it also resulted in an elevated background value in the dark control. As
expected, when a low level of TiO2 (0.1 mg
ml
1) was used along with a high cell concentration (Fig.
1), only 44% of the viable cells were killed within 30 min, yet the
amount of MDA produced was nearly nine times the amount produced in the TiO2 dark control.

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FIG. 1.
Effects of light and TiO2 on lipid
peroxidation of E. coli. Cells (2.5 × 108
CFU ml 1) were incubated in the dark, in UV light, in the
dark with TiO2 (0.1 mg ml 1), and in UV light
with TiO2 (0.1 mg ml 1) for 30 min with
continuous stirring. The light intensity was 8 W m 2. MDA
was quantified by the TBA assay.
|
|
The validity of using the amount of MDA as an index to assess lipid
peroxidation has been challenged due the complexity of determining
amounts of MDA (2, 9). To prove that MDA was indeed a
product of lipid peroxidation under photocatalytic conditions and that
it did not arise as an artifact or as a decomposition product from
other macromolecules in whole cells, we used phosphatidylethanolamine as a model E. coli membrane phospholipid and studied its
peroxidation. Since phosphatidylethanolamine is one of the predominant
phospholipids in most bacterial cell membranes (35), using
this compound could also confirm that lipid peroxidation occurred and
could support the hypothesis that this pathway is involved in the
biocidal action of TiO2. When phosphatidylethanolamine (0.2 mg ml
1; Sigma Chemical Co.) and TiO2 (1 mg
ml
1) were subjected to UV illumination for 1 h,
approximately 0.72 µM MDA was detected based on the standard MDA-TBA
method. The concentration of MDA obtained with the dark control was
only 0.21 µM and was probably the result of preexisting oxidized
products in the sample. Both the validity of using MDA as an index
compound for the assay and the efficacy of the TiO2
photocatalyst for initiating the lipid peroxidation reaction were
manifested by this experiment.
To determine how the lipid peroxidation process affects cell survival
and to correlate this process with losses of other cellular functions
normally associated with an intact membrane, we carried out experiments
to determine the kinetics of lipid peroxidation (Fig.
2). A 10-ml suspension containing
1.8 × 109 CFU ml
1 and TiO2
(1 mg ml
1) was subjected to illumination with continuous
stirring. Due to the nature of the ROS, once initiated, the
TiO2-mediated reaction cannot be terminated even by placing
the reaction mixture on ice or in the dark. To ensure accuracy, we
first subjected a sample to 60 min of illumination and then after 15 min started a 45-min sample and so on. For the zero-time sample we
mixed the cells with TiO2 in the dark and started the
MDA-TBA analysis immediately. Within 10 min, the MDA levels started to
increase, and then they increased steadily over time and reached a
maximum value of 1.1 nmol · mg (dry weight) of
cells
1 after 30 min, indicating that peroxidation of
membrane lipid was occurring. A slight decrease in MDA production was
observed during prolonged illumination.

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FIG. 2.
Kinetics of lipid peroxidation in E. coli
induced by TiO2 photocatalysis. Cell suspensions (1.8 × 109 CFU ml 1) were treated with
TiO2 (1 mg ml 1) and UV light (8 W
m 2) for various periods of time. MDA was quantified by
the TBA assay.
|
|
Since it is known that a wide range of organic compounds can be
decomposed under photocatalytic conditions (14, 19, 22), it
is possible that the product of lipid peroxidation, MDA, is also a
target of oxidative degradation. To test this hypothesis, we
illuminated an MDA solution (27.5 µM) containing TiO2
(0.1 mg ml
1) for 30 min and then determined the residual
amount of MDA by the MDA-TBA method. Light alone or the
TiO2 photocatalyst in the dark had no effect on the
preexisting MDA. However, as we expected, the illuminated
TiO2 preparation lost nearly 88% of the added MDA within
30 min.
Effect of irradiated TiO2 on cellular respiratory
activity.
Since the bacterial cell membrane contains essential
components of the respiratory chain, it was reasonable to investigate the effect of TiO2 photocatalysis on cellular respiratory
activities. Respiration was monitored by determining the uptake of
O2 with a Clark type oxygen electrode and by studying the
reduction of TTC to TTF, a red precipitate. Succinate was used as the
electron donor in both assays. When E. coli cells at a
concentration of 1.2 × 108 CFU ml
1 were
irradiated with TiO2 (0.5 mg ml
1) for various
periods of time, the kinetic data (Fig.
3) revealed an apparent loss of
respiratory activity with reaction time, and the kinetics coincided
well with the loss of cell viability. After 30 min, both viability and
respiratory activity were reduced drastically. Similar results were
obtained when glucose was used instead of succinate as the electron
donor. The progressive loss of viability and respiratory activity is in
good agreement with the lipid peroxidation kinetics shown in Fig. 2.

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FIG. 3.
Kinetic losses of respiratory activity and viability of
E. coli induced by TiO2 photocatalysis. Cells
(1.2 × 108 CFU ml 1) were treated with
TiO2 (0.5 mg ml 1) and incubated under UV
light (8 W m 2). Respiratory activity was determined by
measuring the reduction of oxygen and the reduction of TTC to TTF.
Viability was determined by the plate count method. Gray bars, oxygen
uptake; black bars, TTC reduction; open bars, survival. The 100%
activities at time zero were 16 nmol of O2 · min 1 · mg (dry weight) of cells 1 for
oxygen uptake and 0.27 nmol of TTF · min 1 · mg (dry weight) of cells 1 for TTC reduction.
|
|
Light alone did not have a significant effect on cell viability or on
O2 uptake and TTC reduction activities. Incubation of TiO2 with E. coli cells in the dark had only a
slight impact on the O2 uptake rate and viability. However,
we observed that TiO2 alone consistently caused a decrease
in the whole-cell TTC reduction rate in the dark. After
TiO2 was incubated with E. coli cells for 15 min
in the dark, 27% of the TTC reduction rate was lost, and after 30 min,
only 60% of the activity remained. However, Fig. 3 shows that when
light was present along with TiO2, the residual TTC
reduction activity was only 9% after 30 min of reaction. Even though
TiO2 had an impact on TTC reduction activity in the dark,
the additional decrease caused by light is significant. As observed
with lipid peroxidation, the loss of respiratory activity depends on
the presence of both light and TiO2.
 |
DISCUSSION |
The results of our viability study confirmed the previous findings
of Matsunaga et al. (20, 21), Saito et al. (25), and Wei et al. (34) that illuminated TiO2
exhibits bactericidal activity and that disinfection is positively
correlated with the TiO2 dose used up to a concentration of
1 mg ml
1. The survival ratios in Table 1 compare the
levels of viability in the light with those in the dark at
corresponding cell and TiO2 concentrations. Including
TiO2 in the dark control was necessary since when the
TiO2-cell slurry was stirred in the dark for 30 min, it
yielded a slightly lower viable cell count than a similar sample
without TiO2 would. We attributed this phenomenon to
aggregation of TiO2 particles with cells in the dark. This
could result in the formation of one colony from more than one cell on
an agar plate. A similar observation was made by Saito et al.
(25).
Our results demonstrate for the first time that as determined with MDA
as the index compound, lipid peroxidation of polyunsaturated phospholipids in E. coli occurs as a result of oxidative
actions exerted by the TiO2 photocatalyst. The process
requires the presence of both light and TiO2 (Fig. 1). It
is apparent from the time course of MDA production that the initial
phase of lipid peroxidation progresses at an exponential rate. The
subsequent decrease in the MDA concentration after prolonged
illumination is attributed to photocatalytic oxidation of MDA.
Initiation of lipid peroxidation is known to require some form of
radical attack. However, once initiated, the reaction propagates by
generating a peroxy radical intermediate that, by itself, undergoes
peroxidation with another unsaturated lipid molecule (13).
It has also been suggested that superoxide ions, which are known to be
produced on the irradiated TiO2 surface, react with the
intermediate hydroperoxide to initiate new radical chain reactions
(32, 33), assuming that the molecule can penetrate the cell
membrane once its semipermeability is compromised. If not terminated,
the cascades of autoxidation reactions explain the exponential increase
in MDA production and ultimately lead to destruction of the lipid
phase, which is the cell membrane itself.
Another serious effect of the lipid peroxidation process is that many
of the intermediates in this process can react with important
biological molecules to cause additional damage. It is thought that
lipid peroxidation products may be mutagenic (1, 7, 8).
Furthermore, MDA itself is quite reactive and is able to modify
proteins via carbonylation or to form protein-MDA adducts (4,
24). Both pathways account for the disappearance of MDA from
assay mixtures after 30 min (Fig. 2). Our data also establish that MDA
is oxidatively destroyed by TiO2 photocatalysis. This is
not surprising given the nonspecific nature of the oxidative attacks by
ROS that occur under photocatalytic conditions. Our MDA values,
therefore, were the net result of the rate of MDA production and the
rate of MDA destruction that occurred concurrently by the same
photocatalytic process or during the subsequent participation of MDA in
other chemical reactions. Under prolonged illumination conditions, cell
wall breakdown and cell membrane breakdown would presumably allow
TiO2 particles to gain access to and attack the cell
membrane directly. Eventually, the rate of MDA destruction exceeds the
rate of MDA production, as observed after 30 min of reaction (Fig. 2).
Based on this evidence, the rate and extent of lipid peroxidation in
E. coli cells have very likely been underestimated previously, as has the severity of the impact of the TiO2
photocatalytic process. Consequently, the idea that ROS derived from
the irradiated TiO2 reaction can disturb cell membrane
phospholipids, lipoproteins, and nucleic acids, which places cells in a
state of oxidative stress and eventually leads to cell death, is a
viable concept.
Alterations in membrane architecture caused by lipid peroxidation
ultimately lead to conformational changes in many membrane-bound proteins and electron mediators and to changes in how these compounds are oriented across the cell membrane. Consequently, functional changes
are expected. Parallel research in our laboratory has also established
that illuminated TiO2 has an adverse effect on the
semipermeability of E. coli cell membranes (15).
Our findings explain the observed leakage of K+ ions from
Streptococcus sobrinus (25) and the leakage of
Ca2+ ions from cancer cells (26, 27) following
TiO2 photocatalytic treatments. Our results also confirm
previous reports of Matsunaga et al. (20, 21) and provide
additional evidence that the TiO2 photocatalytic reaction
has a deleterious effect on cellular respiratory activity, the loss of
which parallels cell death. Presumably, membrane disorder disrupts the
spatial organization of the electron mediators that span the cell
membrane and causes the electron transport pathway from succinate or
glucose to oxygen or TTC to be short-circuited. Tetrazolium dyes, such
as TTC in its oxidized form, are reducible by the cytochrome systems of
bacteria during respiration (28). Reduction of TTC has been
used frequently to assess metabolic activities in various
microorganisms (23, 36). Failure to reduce an artificial
acceptor, such as TTC, following TiO2 treatment implies
that the damaged cell membrane can no longer generate or maintain a
sufficiently negative redox potential. When Farr and coworkers
subjected E. coli to oxidative stress, both
radical-generating conditions and H2O2
treatments caused a rapid decrease in proton motive force-dependent and
-independent transport across the cell membrane (11). These
authors suggested that oxidative disruption of the membrane integrity
reduces the proton motive force, which is the driving force for ATP synthesis.
Based on our findings, we propose that ROS, such as OH·,
O2
, and H2O2
generated on the irradiated TiO2 surface, operate in concert to attack polyunsaturated phospholipids in E. coli.
The lipid peroxidation reaction that subsequently causes a breakdown of
the cell membrane structure and therefore its associated functions is
the mechanism underlying cell death. All life forms have a cell
membrane made up of a variety of lipids with various degrees of
unsaturation and rely on their structures to carry out essential functions. Thus, the proposed killing mechanism is applicable to all
cell types. Indeed, preliminary data for TiO2
photocatalysis of a gram-positive organism, Micrococcus
luteus, demonstrated that lipid peroxidation occurred and that
there was a simultaneous loss of cell viability. The attack by ROS
generated by the photocatalytic process outside the cell is very likely
the initial mode of killing that is observed for bacteria and other
cell types. However, the findings reported here do not rule out the
possibility of photocatalytic attack inside a cell after
TiO2 particles are ingested via phagocytosis, as observed
in eucaryotic cells (6).
 |
ACKNOWLEDGMENTS |
This work was supported by the FIRST Program at the National
Renewable Energy Laboratory and the Center for Indoor Air Research.
 |
FOOTNOTES |
*
Corresponding author. Mailing address: The National
Renewable Energy Laboratory, 1617 Cole Boulevard, Golden, CO
80401-3393. Phone: (303) 384-6114. Fax: (303) 384-6150. E-mail:
pinching_maness{at}nrel.gov.
 |
REFERENCES |
| 1.
|
Akasaka, S., and K. Yamamoto.
1994.
Mutagenesis resulting from DNA damage by lipid peroxidation in the supF gene of Escherichia coli.
Mutat. Res.
315:105-112[Medline].
|
| 2.
|
Aust, S.
1987.
Lipid peroxidation, p. 203-207.
In
R. A. Greenwald (ed.), CRC handbook of methods for oxygen radical research. CRC Press, Inc., Boca Raton, Fla.
|
| 3.
|
Blake, D. M.,
P.-C. Maness,
Z. Huang,
E. J. Wolfrum,
W. A. Jacoby, and J. Huang.
1999.
Application of the photocatalytic chemistry of titanium dioxide to disinfection and the killing of cancer cells.
Sep. Purif. Methods
28:1-50.
|
| 4.
|
Burcham, P. C., and Y. T. Kuhan.
1996.
Introduction of carbonyl groups into proteins by the lipid peroxidation product, malondialdehyde.
Biochem. Biophys. Res. Commun.
220:996-1001[Medline].
|
| 5.
|
Byrne, J. A.,
B. R. Eggins,
N. M. D. Brown,
B. McKinnery, and M. Rouse.
1998.
Immobilisation of TiO2 powder for the treatment of polluted water.
Appl. Catal. B Environ.
17:25-36.
|
| 6.
|
Cai, R.,
K. Hashimoto,
K. Itoh,
Y. Kubota, and A. Fujishima.
1991.
Photokilling of malignant cells with ultrafine TiO2 powder.
Bull. Chem. Soc. Jpn.
64:1268-1273.
|
| 7.
|
Cao, E. H.,
X. Q. Liu,
L. G. Wang, and N. F. Xu.
1995.
Evidence that lipid peroxidation products bind to DNA in liver cells.
Biochim. Biophys. Acta
1259:187-191[Medline].
|
| 8.
|
Chaudhary, A. K.,
M. Nokubo,
G. R. Redy,
S. N. Yeola,
J. D. Morrow,
I. A. Blair, and L. J. Marnett.
1994.
Detection of endogenous malondialdehyde-deoxyguanosine adducts in human liver.
Science
265:1580-1582[Abstract/Free Full Text].
|
| 9.
|
Draper, H. H., and M. Hadley.
1990.
Malondialdehyde determination as index of lipid peroxidation.
Methods Enzymol.
186B:421-431[Medline].
|
| 10.
|
Esterbauer, H., and K. H. Cheeseman.
1990.
Determination of aldehydic lipid peroxidation products: malonaldehyde and 4-hydroxynonenal.
Methods Enzymol.
186B:407-421[Medline].
|
| 11.
|
Farr, S. B.,
D. Touati, and T. Kogoma.
1988.
Effects of oxygen stress on membrane functions in Escherichia coli: role of HPI catalase.
J. Bacteriol.
170:1837-1842[Abstract/Free Full Text].
|
| 12.
|
Gaswami, D. Y.,
D. M. Trivedi, and S. S. Block.
1997.
Photocatalytic disinfection of indoor air.
J. Sol. Energy Eng.
119:92-96.
|
| 13.
|
Gutteridge, J. M. C.
1987.
Lipid peroxidation: some problems and concepts, p. 9-19.
In
B. Halliwell (ed.), Oxygen radicals and tissue injury. Proceedings of a Brook Lodge Symposium. Upjohn Co., Bethesda, Md.
|
| 14.
|
Hoffmann, M. R.,
S. T. Martin,
W. Choi, and D. W. Bahnemann.
1995.
Environmental applications of semiconductor photocatalysis.
Chem. Rev.
95:69-96.
|
| 15.
|
Huang, Z.,
P. C. Maness,
S. Smolinski,
D. M. Blake,
W. A. Jacoby, and E. J. Wolfrum.
1999.
Effects of titanium dioxide photocatalytic reaction on the permeability of E. coli, abstr. Q-234, p. 578.
In
Abstracts of the 99th General Meeting of the American Society for Microbiology 1999. American Society for Microbiology, Washington, D.C.
|
| 16.
|
Ireland, J. C.,
P. Klostermann,
E. W. Rice, and R. M. Clark.
1993.
Inactivation of Escherichia coli by titanium dioxide photocatalytic oxidation.
Appl. Environ. Microbiol.
59:1668-1670[Abstract/Free Full Text].
|
| 17.
|
Jacoby, W. A.,
P. C. Maness,
E. J. Wolfrum,
D. M. Blake, and J. A. Fennel.
1998.
Mineralization of bacterial cell mass on a photocatalytic surface in air.
Environ. Sci. Technol.
32:2650-2653.
|
| 18.
|
Kappus, H.
1985.
Lipid peroxidation: mechanisms, analysis, enzymology and biological relevance, p. 273-310.
In
H. Sies (ed.), Oxidative stress. Academic Press, Inc., New York, N.Y.
|
| 19.
|
Legrini, O.,
E. Oliveros, and A. M. Braun.
1993.
Photochemical processes for water treatment.
Chem. Rev.
93:671-698.
|
| 20.
|
Matsunaga, T.,
R. Tomada,
T. Nakajima, and H. Wake.
1985.
Photochemical sterilization of microbial cells by semiconductor powders.
FEMS Microbiol. Lett.
29:211-214.
|
| 21.
|
Matsunaga, T.,
R. Tomoda,
Y. Nakajima,
N. Nakamura, and T. Komine.
1988.
Continuous-sterilization system that uses photosemiconductor powders.
Appl. Environ. Microbiol.
54:1330-1333[Abstract/Free Full Text].
|
| 22.
|
Mills, A., and S. Le Hunte.
1997.
An overview of semiconductor photocatalysis.
J. Photochem. Photobiol. A Chem.
108:1-35.
|
| 23.
|
Parrington, L. J.,
A. N. Sharpe, and P. I. Peterkin.
1993.
Improved aerobic colony count technique for hydrophobic grid membrane filters.
Appl. Environ. Microbiol.
59:2784-2789[Abstract/Free Full Text].
|
| 24.
|
Requena, J. R.,
M. X. Fu,
M. J. Ahmed,
A. J. Jenkins,
T. J. Lyons,
J. M. Baynes, and S. R. Thorpe.
1997.
Quantification of malondialdehyde and 4-hydroxynonenal adducts to lysine residue in native and oxidized human low-density lipoprotein.
Biochem. J.
322:317-325.
|
| 25.
|
Saito, T.,
T. Iwase, and T. Morioka.
1992.
Mode of photocatalytic bactericidal action of powdered semiconductor TiO2 on mutans streptococci.
J. Photochem. Photobiol. B Biol.
14:369-379[Medline].
|
| 26.
|
Sakai, H.,
R. Cai,
K. Hashimoto,
T. Kato,
K. Hashimoto,
A. Fujishima,
Y. Kubota,
E. Ito, and T. Yoshioka.
1990.
Photocatalytic effect of TiO2 particles on tumor cells study on mechanism of cell death by measuring concentration of intracellular calcium ion.
Photomed. Photobiol.
12:135-138.
|
| 27.
|
Sakai, H.,
E. Ito,
R.-X. Cai,
T. Yoshioka,
K. Hashimoto, and A. Fujishima.
1994.
Intracellular Ca+2 concentration change of T24 cell under irradiation in the presence of TiO2 ultrafine particles.
Biochim. Biophys. Acta
1201:259-265[Medline].
|
| 28.
|
Smith, J. J., and G. A. McFeters.
1997.
Mechanisms of INT (2-(4-iodophenyl)-3-(4-nitrophenyl)-5-phenyl tetrazolium chloride), and CTC (5-cyano-2,3-ditolyl tetrazolium chloride) reduction in Escherichia coli K-12.
J. Microbiol. Methods
29:161-175.
|
| 29.
|
Smith, S. N., and G. J. F. Pugh.
1979.
Evaluation of dehydrogenase as a suitable indicator of soil microflora activity.
Enzyme Microb. Technol.
1:279-281.
|
| 30.
|
Stevenson, M.,
K. Bullock,
W.-Y. Lin, and K. Rajeshwar.
1997.
Sonolytic enhancement of the bactericidal activity of irradiated titanium dioxide suspensions in water.
Res. Chem. Intermed.
23:311-323.
|
| 31.
|
Sunada, K.,
Y. Kikuchi,
K. Hashimoto, and A. Fujishima.
1998.
Bactericidal and detoxification effects of TiO2 thin film photocatalysts.
Environ. Sci. Technol.
32:726-728.
|
| 32.
|
Sutherland, M. W., and J. M. Gebicki.
1982.
A reaction between the superoxide free radical and lipid peroxidation in sodium linoleate micelles.
Arch. Biochem. Biophys.
214:1-11[Medline].
|
| 33.
|
Thomas, M. J.,
K. S. Mehl, and W. A. Pryor.
1982.
The role of superoxide in xanthine oxidase-induced autooxidation of linoleic acid.
J. Biol. Chem.
257:8343-8347[Abstract/Free Full Text].
|
| 34.
|
Wei, C.,
W.-Y. Lin,
Z. Zaina,
N. E. Williams,
K. Zhu,
A. P. Kruzic,
R. L. Smith, and K. Rajeshwar.
1994.
Bactericidal activity of TiO2 photocatalyst in aqueous media: toward a solar-assisted water disinfection system.
Environ. Sci. Technol.
28:934-938.
|
| 35.
|
Wilkinson, S. G.
1988.
Gram-negative bacteria, p. 299-317.
In
C. Ratledge, and S. G. Wilkinson (ed.), Microbial lipids, vol. 1. Academic Press, San Diego, Calif.
|
| 36.
|
Zimmermann, R.,
R. Iturriaga, and J. Becker-Birck.
1978.
Simultaneous determination of the total number of aquatic bacteria and the number thereof involved in respiration.
Appl. Environ. Microbiol.
36:926-935[Abstract/Free Full Text].
|
Applied and Environmental Microbiology, September 1999, p. 4094-4098, Vol. 65, No. 9
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Copyright © 1999, American Society for Microbiology. All rights reserved.
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