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Applied and Environmental Microbiology, October 2005, p. 6410-6413, Vol. 71, No. 10
0099-2240/05/$08.00+0 doi:10.1128/AEM.71.10.6410-6413.2005
Copyright © 2005, American Society for Microbiology. All Rights Reserved.
Disinfection of Microorganisms by Use of Electrochemically Regenerated Periodate
Mina Okochi,1
Hiroshi Yokokawa,1
Tae-Kyu Lim,1
Tomoyuki Taguchi,1
Hiromichi Takahashi,1
Hiroko Yokouchi,1
Tatsuo Kaiho,2
Akira Sakuma,3 and
Tadashi Matsunaga1*
Department of Biotechnology and Life Sciences, Tokyo University of Agriculture and Technology, Koganei, Tokyo 184-8588, Japan,1
Mitsui Chemical Inc., Togo, Mobara-city, Chiba 297-8666, Japan,2
Kanto Natural Gas Development Co., Ltd., Nihonbashi Muromachi Chuo-ku, Tokyo 103-0022, Japan3
Received 8 October 2004/
Accepted 13 May 2005

ABSTRACT
A new method for disinfection of microorganisms by electrochemically
regenerated periodate was developed. Oxidation of iodate to
periodate was observed at 1.25 V versus a silver/silver chloride
electrode in a cyclic voltammogram of potassium iodate. When
1.25 V was applied in 1.0 mM potassium iodate, approximately
4-log inactivation of
Escherichia coli was observed in 30 min.

INTRODUCTION
Iodine-based disinfectant has been used for many years in the
medical field and for potable water disinfection where municipal
water treatment is not reliable. The mechanism of antimicrobial
disinfection is based on the fact that iodine is a strong oxidant
(
1,
6,
7,
17). Iodine-based disinfectants are more stable chemically
and have a more acceptable taste than chlorine-based disinfectants,
which makes them useful for disinfection in field work. Euthyroid
individuals can be treated safely with iodine-containing solutions
at a residual concentration less than 1.0 mg/liter, even for
a long period of time (
4,
5). However, excess iodine ingestion
can be deleterious to human health. The major health effect
of excess iodine ingestion is the development of thyroid diseases
(
2). Therefore, removal of excess iodine using activated carbon
is required to ensure safe levels of iodine while efficient
disinfection activity is maintained.
In studies evaluating the efficacy of electrochemical disinfection methods to prevent biofilm formation and biofouling, workers have used a potential of approximately 1.0 V (12, 15, 16). A potential of 0.74 V versus a saturated calomel electrode applied to Saccharomyces cerevisiae resulted in decreased respiratory activity and cell death (12). This method has been applied to disinfection of drinking water utilizing granular activated carbon (10), carbon-cloth sheets (11), activated carbon fibers (9, 14), and titanium nitride mesh (13) as electrodes. Disinfection and chlorine removal were carried out using activated carbon fiber reactors by applying 0.8 to 1.0 V versus a saturated calomel electrode. A distinct advantage of this methodology is that bacterial regrowth on electrode surfaces can be controlled continuously without the production of hazardous by-products.
In the present study, a new method for disinfection using electrochemically generated periodate was developed. Periodate is also a strong oxidizing agent (3) and can be used for disinfection (8). A combination of electrochemical treatment and iodine-based disinfectant could result in effective disinfection.
Potassium periodate (KIO4) and potassium iodate (KIO3) were purchased from Wako Pure Chemical Industries Ltd. (Osaka, Japan). Cyclic voltammetry was carried out in 0.1 M KIO3 at room temperature using an electroanalytical system (model CS-1090; Cypress System Inc., Kansas City, MO). The potential was referenced against a silver/silver chloride electrode (Ag/AgCl), and a coiled platinum wire was used as a counter electrode. A basal-plane pyrolytic graphite electrode (0.2 cm2) was employed as the working electrode.
Escherichia coli strain DH5
(obtained from Toyobo Co. Ltd., Osaka, Japan) was cultured aerobically at 37°C for 12 h in Luria-Bertani medium (pH 7.0). The cells were centrifuged at 1,700 x g for 10 min, washed, and resuspended in 0.1 M phosphate buffer (pH 7.0). The cell concentration was determined using a cell counting chamber for bacteria (chamber area, 0.0025 mm2; depth, 0.02 mm). Potassium periodate or potassium iodate was added to cell suspensions (104 cells/ml, 30 ml) to final concentrations of 0.1 and 1.0 mM. Cell mixtures were stirred continuously using a magnetic stirring bar, and 1.25 V was applied to the electrode using a potentiostat (model HA-151; Hokuto Denko Co., Tokyo, Japan). An Ag/AgCl reference electrode and a Pt wire counter electrode were used. The number of viable cells remaining after disinfection was determined by plating 50-µl aliquots of the samples on Luria-Bertani medium with 0.7% agar. Colonies that appeared after 24 h of incubation at 37°C were counted.
The effect of iodate or periodate on the concentration of viable E. coli cells was investigated at room temperature. When the cell suspension (1.0 x 104 cells/ml) was incubated in 0.1 mM or 1.0 mM KIO3, a decrease in the concentration of viable cells was not observed (Fig. 1). In contrast, when the cell suspension was incubated with 1.0 mM KIO4, an almost 2-log decrease in the concentration of viable cells was observed after 30 min, and a 3-log decrease was observed after 2 h (Fig. 1). E. coli cells were clearly killed by the addition of periodate. After incubation of the cultures with 0.1 mM periodate, the concentration of iodate (the reduced product of periodate) was measured by high-performance liquid chromatography. During 2 h of incubation, the iodate concentration increased gradually to 0.04 mM as analyzed by an anion-exchange column (Shim-pack IC-A1; Shimadzu Co., Ltd., Kyoto, Japan) with 2.4 mM Tris-HCl buffer containing 2.5 mM phthalic acid as the mobile phase (data not shown). These results indicate that periodate was reduced to iodate during the disinfection process.
Figure
2 shows the cyclic voltammogram obtained at a scan rate
of 100 mV · s
1 in 0.1 M KIO
3. An anodic peak appeared
at approximately 1.25 V, and the peak current was 30 µA.
In contrast, the corresponding peak did not appear when cyclic
voltammetry was performed in 0.1 mM phosphate buffer without
potassium iodate. It was found that iodate was electrochemically
oxidized at a potential of 1.25 V. In order to confirm that
periodate was formed by the oxidation of iodate, the periodate
concentration was measured after 1.25 V was applied in 1.0 mM
KIO
3. The periodate concentration was measured as follows. One
milliliter of a periodate sample, 10 ml of Britton-Robinson
buffer (pH 4.0), 5 ml of distilled water, and 5 ml of tetramethylammonium
iodide (0.5%, wt/vol) were added sequentially and mixed. The
solution was extracted twice with 2.5 ml of chloroform and then
dehydrated with anhydrous sodium sulfate (1.0 g). The absorbance
at 509 nm was measured using a spectrophotometer (model UV2400
PC; Shimadzu Co. Ltd.). When 1.25 V was applied in 1.0 mM KIO
3,
the periodate concentration increased linearly with time (Fig.
3). Therefore, these results demonstrated that iodate is electrochemically
converted to periodate when a potential of 1.25 V is applied.
The effect of the applied potential on the concentration of
viable
E. coli cells in 1.0 mM KIO
3 was investigated. When potentials
between 0 and 1.6 V were applied for 60 min, the survival ratio
was more than 90% in the absence of iodate. In contrast, when
potentials were applied to cell suspensions containing 1.0 mM
KIO
3, the concentration of viable cells decreased with increasing
potential. The survival ratio was 0% at 1.25 V (Fig.
4).
Next, the time course of the concentration of viable cells when
1.25 V was applied in 0.1 mM or 1.0 mM KIO
3 was investigated
(Fig.
5). When a potential was not applied, a decrease in the
concentration of viable cells was not observed, as shown in
Fig.
1. In contrast, when 1.25 V was applied in 1.0 mM KIO
3,
an approximately 4-log decrease in the concentration of viable
cells was observed in 30 min. Furthermore, when 1.25 V was applied
in 0.1 mM KIO
3, the concentration of viable cells also decreased
to 18% and 6% after 60 min and 120 min, respectively. In addition,
a gram-positive bacterium,
Bacillus subtilis, and a eukaryote,
Saccharomyces cerevisiae, were also examined for inactivation.
When 1.25 V was applied for 30 min in 0.1 mM KIO
4, the survival
ratios of
B. subtilis and
S. cerevisiae at an initial cell concentration
of 1.4
x 10
4 cells/ml decreased to 3% and 17%, respectively.
With 1.0 mM KIO
4, more than 99% of the cells were inactivated.
These results demonstrate that when a potential of 1.25 V was
applied, iodate was electrochemically converted to periodate,
which could be used as an efficient disinfectant.
Periodate is a well-known oxidizing agent that has been used
for disinfection for a long time. Here we describe disinfection
utilizing electrochemically regenerated periodate. By regeneration
of periodate, disinfection can be conducted efficiently at low
concentrations. Therefore, since iodine is electrochemically
oxidized to iodate and consequently to periodate, it might be
possible to reduce periodate electrochemically to iodate or
iodine, compounds that are less toxic after disinfection.

FOOTNOTES
* Corresponding author. Mailing address: Department of Biotechnology and Life Sciences, Tokyo University of Agriculture and Technology, 2-24-16, Naka-cho, Koganei, Tokyo 184-8588, Japan. Phone: 81-42-388-7020. Fax: 81-42-385-7713. E-mail:
tmatsuna{at}cc.tuat.ac.jp.


REFERENCES
1 - Atwater, J. E., R. L. Sauer, and J. R. Schultz. 1996. Numerical stimulation of iodine speciation in relation to water disinfection aboard manned spacecraft I. Equibria. J. Environ. Sci. Health A31:1965-1979.
2 - Baker, H., and J. Hollowell. 2000. Use of iodine for water disinfection: iodine toxicity and maximum recommended dose. Environ. Health Perspect. 108:679-684.[Medline]
3 - Beppu, M., H. Ochiai, and K. Kikugawa. 1989. Macrophage recognition of periodate treated erythrocytes: involvement of disulfide formation of the erythrocyte membrane proteins. Biochim. Biophys. Acta 979:35-45.[Medline]
4 - Braverman, L. 1994. Iodine and the thyroid: 33 years of study. Thyroid 4:351-355.[Medline]
5 - Dunn, J. 1998. What's happening to our iodine. J. Clin. Endocrinol. Metab. 83:3398-3400.[Free Full Text]
6 - Gottardi, W. 1991. Iodine and iodine compounds, p. 152-167. In S. Block (ed.), Disinfection, sterilization, and preservation. Lea & Febiger, Philadelphia, Pa.
7 - Gottardi, W. 1999. Iodine and disinfection: theoretical study on mode of action, efficacy, stability and analytical aspects in the aqueous system. Arch. Pharm. Med. Chem. 332:151-157.[CrossRef]
8 - Kaiho, T. 2001. Novel applications of iodine compound, p. 32. In Proceedings of the 4th Symposium on Iodine Utilization, Chiba, Japan, October 23, 2001. Yoso Riyo Kenkyukai, Chiba, Japan.
9 - Matsunaga, T., S. Nakasono, Y. Kitajima, and K. Horiguchi. 1994. Electrochemical disinfection of bacteria in drinking water using activated carbon fibers. Biotechnol. Bioeng. 43:429-433.[CrossRef]
10 - Matsunaga, T., S. Nakasono, and S. Masuda. 1992. Electrochemical sterilization of bacteria adsorbed on granular activated carbon. FEMS Microbiol. Lett. 93:255-260.[CrossRef]
11 - Matsunaga, T., S. Nakasono, T. Takamuku, J. G. Burgess, N. Nakamura, and K. Sode. 1992. Disinfection of drinking water by using a novel electrochemical reactor employing carbon-cloth electrodes. Appl. Environ. Microbiol. 58:686-689.[Abstract/Free Full Text]
12 - Matsunaga, T., Y. Namba, and T. Nakajima. 1984. Electrochemical sterilization of microbial cells. Bioelectrochem. Bioenerg. 13:393-400.[CrossRef]
13 - Matsunaga, T., M. Okochi, M. Takahashi, T. Nakayama, H. Wake, and N. Nakamura. 2000. TiN electrode reactor for disinfection of drinking water. Water Res. 34:3117-3122.[CrossRef]
14 - Okochi, M., T. Lim, N. Nakamura, and T. Matsunaga. 1997. Electrochemical disinfection of drinking water using an activated-carbon-fiber reactor capable of monitoring its microbial fouling. Appl. Microbiol. Biotechnol. 47:18-22.[CrossRef][Medline]
15 - Okochi, M., N. Nakamura, and T. Matsunaga. 1998. Electrochemical control of bacterial cell accumulation on submerged glass surfaces. Clean Prod. Processes 1:53-59.
16 - Nakasono, S., J. G. Burgess, K. Takahashi, M. Koike, C. Murayama, S. Nakamura, and T. Matsunaga. 1993. Electrochemical prevention of marine biofouling with a carbon-chloroprene sheet. Appl. Environ. Microbiol. 59:3757-3762.[Abstract/Free Full Text]
17 - von Gunten, U. 2003. Ozonation of drinking water: part II. Disinfection and by-product formation in presence of bromide, iodide, chlorine. Water Res. 37:1469-1487.[Medline]
Applied and Environmental Microbiology, October 2005, p. 6410-6413, Vol. 71, No. 10
0099-2240/05/$08.00+0 doi:10.1128/AEM.71.10.6410-6413.2005
Copyright © 2005, American Society for Microbiology. All Rights Reserved.