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A THESIS FOR THE DEGREE OF MASTER OF SCIENCE
Application of Innovative Processing of deep UV-LED
to Control Food-borne Pathogens
병원 미생물 저감화를 한 DUV-LED 적 최적화 연
February, 2015
Joo Yeon Shin
Department of Agricultural Biotechnology
Seoul National University
Joo Yeon Shin
사학 문
Application of Innovative Processing of deep UV-LED
to Control Food-borne Pathogens
병원 미생물 저감화를 한 DUV-LED 적 최적화 연
지도 수 강동현
논문 사학 논문 로 제출함
2015 년 2 월
울대학 대학원 농생명공학
신 주 연
신주연 사 학 논문 함
2015 년 2 월
원 문 태 화 ( )
원 강 동 현 ( )
원 진 호 ( )
III
ABSTRACT
The UV irradiation for treating food has been approved by the U.S. Food
and Drug Administration. So far, most UV treatment is performed by low-
pressure (LP) UV lamp of 253.7 nm. But these lamps have some potential
risks such as possibility of mercury leakage, short life time and requirement
of significant amount of energy. As an alternative to UV mercury lamps,
deep UV-LEDs (DUV-LEDs) are of great interest for disinfection. The
objectives of this study were to examine the basic spectral properties of
DUV-LEDs and the effects of UV-C irradiation for inactivating food-borne
pathogens on solid medium as well as in water. A cocktail of Escherichia
coli O157:H7, Salmonella Typhimurium and Listeria monocytogenes strains
was spread-plated onto each selective medium or inoculated to the sample of
water. As temperature increased, intensity of LED was slightly decreased
while LP lamp showed intensity increasing until it reaches to the peak
temperature around 30 °C. As the dose of UV radiation increased from 0 to
1.67 mJ/cm2, all kinds of food-borne pathogens showed great reduction by
IV
>5 log. When treatment temperature increases, reduction level of E. coli
O157:H7 and S. Typhimurium were gradually increased, but L.
monocytogenes showed no significant different (P > 0.05). Only for E. coli
O157:H7, the significant reduction (P < 0.05) was observed at 90% relative
humidity condition compared with other conditions such as 30 and 60 %. In
case of 10 ml of water treatment, levels of surviving cells of all pathogens
were reduced to below the detection limit (1.0 log CFU/g). At the scaled-up
test, surviving populations of general bacteria were reduced by 5.38 and 4.37
log CFU/ml for 2 L and 3 L of water, respectively, and lowered to below
detection limit for 1 L of water at the dose of 3 mJ/cm2. Linear correlation
between inactivation and dosage of UV irradiation was indicated at
continuous water decontamination system. The result of this study suggests
that a novel type of DUV-LED’s applicability was confirmed as an
alternative to the lamp type in inactivating food-borne pathogens.
Keywords: DUV-LED, ultraviolet irradiation, food-borne pathogens,
surface and water decontamination, environmental device
Student Number: 2013-21176
V
CONTENTS
ABSTRACT.................................................................................................. III
CONTENTS....................................................................................................V
LIST OF TABLES......................................................................................VIII
LIST OF FIGURES........................................................................................X
I. INTRODUCTION........................................................................................1
II. MATERIALS AND METHODS................................................................4
2.1. Spectral characteristics of DUV-LED
2.1.1. Collimated UV radiation design.................................................4
2.1.2. Experimental setup......................................................................6
2.1.3. Irradiance measurements.............................................................8
2.2. Effect of various conditions on inactivation of food-borne pathogens
by using DUV-LED
2.2.1. Bacterial strains and inoculum conditions..................................8
2.2.2. Culture preparation...................................................................9
2.2.3. Culture inoculation....................................................................9
2.2.4. UV treatment.............................................................................10
2.2.5. Bacterial enumeration...............................................................11
2.2.6. Statistical analysis.....................................................................11
VI
2.3. UV treatment for water decontamination
2.3.1. Bacterial strains and inoculum conditions................................12
2.3.2. Culture preparation...................................................................13
2.3.3. Culture inoculation....................................................................13
2.3.4. UV treatment.............................................................................14
2.3.5. Bacterial enumeration...............................................................16
2.3.6. Statistical analysis.....................................................................16
III. RESULTS................................................................................................17
3.1. Spectral characteristics of DUV-LED
3.1.1. Emission spectrum of DUV-LED.............................................17
3.1.2. Comparison of properties between DUV-LEDs and LP lamps
.............................................................................................................19
3.1.3. Assessment of the effective area by LED arrangements...........21
3.2. Effect of various conditions on inactivation of food-borne pathogens
by using DUV-LED
3.2.1. Bactericidal effect by UV treatment on media..........................25
3.2.2. Effect of UV irradiation temperature........................................27
3.2.3. Effect of UV irradiation humidity.............................................29
3.3. UV treatment for water decontamination
3.3.1. Bactericidal effect by UV treatment at batch water system......31
3.3.2. Bactericidal effect by UV treatment at scale-up system...........33
VII
3.3.3. Bactericidal effect by UV treatment at continuous water system
.............................................................................................................37
IV. DISCUSSIONS.......................................................................................45
V. REFERENCES….....................................................................................51
VI. 문초록................................................................................................58
VIII
LIST OF TABLES
Table 1. Surviving populations of E. coli O157:H7, S. Typhimurium, and L.
monocytogenes on media following UV-C irradiation, 4cm distance between
petri dish and LED, for intensity of 5.57 μW/cm2….………........................26
Table 2. Surviving populations of E. coli O157:H7, S. Typhimurium, and L.
monocytogenes on media following UV-C irradiation for 1 min at 0°C, 4 °C,
15 °C, 25 °C, or 37°C. 4 cm distance between petri dish and LED..............28
Table 3. Surviving populations of E. coli O157:H7, S. Typhimurium, and L.
monocytogenes on media following UV-C irradiation for 1 min at the
humidity of 30%, 60% and 90%, 25℃, 12.5 cm distance between petri dish
and LED.........................................................................................................30
Table 4. Surviving populations of E. coli O157:H7, S. Typhimurium, and L.
monocytogenes in batch water system following UV-C irradiation. Treated at
room temp, 4.5 cm distance between sample and LED.................................32
IX
Table 5. Reduction levels of Escherichia coli O157:H7 in continuous water
system following UV-C irradiation at various flow rates and intensities......39
Table 6. Reduction levels of Salmonella Typhimurium in continuous water
system following UV-C irradiation at various flow rates and intensities......40
Table 7. Reduction levels of Listeria monocytogenes in continuous water
system following UV-C irradiation at various flow rates and intensities......41
X
LIST OF FIGURES
Fig. 1. Spatial arrangements for DUV-LEDs (a set of four LEDs)................5
Fig. 2. Schematic diagram of DUV-LED irradiation system at Seoul National
University (Seoul, Korea)................................................................................7
Fig. 3. Continuous water decontamination system at Seoul National
University (Seoul, Korea)..............................................................................15
Fig. 4. External appearance (a) and emission spectrum (b) of the DUV-LED
module...........................................................................................................18
Fig.5. Comparison between DUV-LED and LP lamp for (a) warm-up time
and (b) variation of intensity in accordance with temperature. �, DUV-LED;
s, LP mercury lamp.....................................................................20
Fig. 6. Petri factor (a) and irradiance (b) for LEDs accordance with spatial
arrangements as a function of distance from the LED...................................22
XI
Fig. 7. Irradiance of four corner arranged LEDs as a function of distance
from
LED................................................................................................................24
Fig. 8. Survival curves for Escherichia coli O157:H7 (A), Staphylococcus
aureus (B) and General bacteria (C) by UV-C irradiation from DUV-LED
with water volume of �, 1L; ¡, 2L; q,
3L....................................................34
Fig. 9. Survival curves for Escherichia coli O157:H7 (A), Salmonella
Typhimurium (B) Listeria monocytogenes (C) by UV-C irradiation from
DUV-LED with power of �, 100mW; ¡, 150mW; q,
200mW....................42
XII
1
I. INTRODUCTION
Food safety has definite correlation to the public health. Each year,
about more than 16% of people get an illness and 3,000 are killed by
consuming contaminated food in the United States (CDC, 2011). Also,
higher than 50 billion dollars of economic cost related with foodborne
illnesses is burdened in the United States per year (Scharff, 2012). For these
major causes of food-borne outbreaks are generally recognized as E. coli
O157:H7, Salmonella spp. and L. monocytogenes. E. coli O157:H7 has
become notifiable foodborne pathogen which causing severe hemorrhagic
colitis and hemolytic-uremic syndrome (Doyle, 1991; Sodha et al., 2014).
The symptoms of salmonella spp. infection are diarrhea, abdominal pain,
mild fever, blood-tinged stools and vomiting (Baird-Parker, 1990; Zansky et
al., 2002). L. monocytogenes can survive and grow at refrigeration
temperatures, which adversely affects pregnant woman and elderly people
like immunocompromised persons (Datta, 2003; Farber and Peterkin, 1991).
Ultraviolet light (UV) which covers the region of the electromagnetic
spectrum from 100 to 400 nm is classified as UV-A (320-400 nm), UV-B
(280-320 nm) and UV-C (200-280 nm) (Guerrero–Beltrán and Barbosa–
Cánovas, 2004). The UV-C light is considered as the most germicidal effect
2
region of the UV spectrum for inactivating microorganisms such as bacteria,
viruses, protozoa, fungi, yeasts and algae by formation of photoproducts in
the DNA (Bintsis et al., 2000; Yaun et al., 2004). The pyrimidine dimer is
the most major product, which formed between adjacent pyrimidine
molecules in the same DNA strand. These dimers can interrupt both proper
transcription and replication of DNA, eventually leading to cell death
(Guerrero–Beltrán and Barbosa–Cánovas, 2004; Franz et al., 2009; Lopez-
Malo et al., 2005)
The use of UV irradiation as a disinfectant to treat food has been
approved by the U.S. Food and Drug Administration (US FDA, 2000). So far,
the majority of UV treatment is performed by low-pressure mercury UV
lamp of 253.7 nm in academic as well as in the industry field. But these
lamps have some potential risks such as possibility of mercury leakage, short
life time and requirement of significant amount of energy (Bowker et al.,
2011). As an alternative to UV mercury lamps, the application form of UV-C
light emitting diodes (DUV-LEDs) have been developing. DUV-LED has
numerous advantages over than conventional type of mercury lamp. While
emitting wavelength of low-pressure mercury lamps is fixed at 253.7 nm, the
emission wavelength of DUV-LED can be tuned at various individual
wavelengths in all UV spectrum. Adjustment to match the most effective
wavelength for disinfection in wide range of environmental conditions can
3
enhance efficiency of inactivation rates (Bettles, 2007). Also DUV-LED has
fracture-resistance to external shock, flexible spatial application by compact
size and reduction of heat generation.
Several studies have been performed for resulting the efficacy of
DUV-LEDs in water (Hamamoto et al., 2007, Chatterley et al., 2011).
Wurtele et al. (2011) and Oguma et al. (2013) developed both static test and
flow-through test system for different figures to examine the inactivation
efficiency. Although they had developed each unique type of water
decontamination system, both established continuous system still has some
limits for applying to practical use. To be a meaningful level of treating
amounts of water, certain level of flow rate is required over than a unit of
liter per minute. Also, to see the effect at high flow rate system, high power
of DUV-LED module should be guaranteed at short UV exposure time. For
these reason new type of flow-through water disinfection system was created
in order to prevent the loss of treating UV radiation.
The objectives of this study were to examine the basic properties of
DUV-LEDs such as a spectrum and intensities in accordance with several
distances and arrangements of LEDs. Also, the effects of UV-C irradiation
for inactivating E. coli O157:H7, Salmonella Typhimurium and L.
monocytogenes on solid medium at various temperatures and humidities as
4
well as at the each batch and continuous water treatment system were
investigated.
5
II. MATERIALS AND METHODS
2.1. Spectral characteristics of DUV-LED
2.1.1. Collimated UV radiation design
Four DUV-LED modules (LG Innotek Co., Korea) were connected to the
electronic printed circuit board (PCB) to get a constant electric current of
20mA from the DC power supply (TPM series, Toyotech). All of these LEDs
emitted with a single wavelength, 275 ± 3 nm. Several spatial arrangements
of four DUV-LEDs were set and analyzed to clearly fix the optimal LED
configuration which leads collimated radiation. Fig. 2 shows the five kinds
of disposition of LEDs which are tested in this study. (Colleen Bowker et al.,
2011)
6
Fig. 1. Spatial arrangements for DUV-LEDs (a set of four LEDs).
Evenly spaced Original Straight line
4 Corners Staggered line
7
2.1.2. Experimental setup
Four LED modules were arranged at each corner, 6 cm distance from
each other with 4cm distance between LEDs and petri dish were set because
this method showed generally equal intensity on the whole petri dish (90mm
diameter) above 4 cm of the sample. More concisely, the petri factor was
higher than 0.9 that means an ideal configuration for UV irradiance (Bolton
and Linden, 2003). The PCB with LED and inoculated media were placed in
the constant temperature chamber (IL-11, Lab Companion, Daejeon, Korea)
to optimize treatment conditions. The petri dish was located at the right
down side of the LEDs to get the maximum UV exposure (Fig. 1).
8
Fig. 2. Schematic diagram of DUV-LED irradiation system at Seoul National
University (Seoul, Korea).
9
2.1.3. Irradiance measurements
Irradiance of DUV-LED was measured by spectrometer (AvaSpec-
ULS2048-USB2-UA-50, Avantes, Netherlands) calibrated for 200 to 400nm
range of all UV spectrum. Optical probe was placed 4 cm above the LEDs
and peak irradiance value of spectrum was read. In order to calculate petri
factor, the optical probe scanned every 5mm over the petri dish (Bolton and
Linden, 2003). The maximum intensity value was multiplied by obtained
petri factor to get corrected Irradiance which means an average fluence rate.
2.2. Effect of various conditions on inactivation of food-borne pathogens
by using DUV-LED
2.2.1. Bacterial strains and inoculum conditions
Three bacterial strains of E. coli O157:H7 (ATCC 35150, ATCC 43889,
ATCC 43890), S. Typhimurium (ATCC 19585, ATCC 43971, DT 104), and
L. monocytogenes (ATCC 7644, ATCC 19114, ATCC 19115) were obtained
from the Bacterial Culture Collection at Seoul National University (Seoul,
Korea). Stock cultures were prepared at – 80 °C in 0.7ml of Tryptic Soy
Broth (TSB; Difco, Becton Dickinson, Sparks, MD, USA) and 0.3ml of 50%
10
glycerol solution. In this study bacteria were streaked onto Tryptic Soy Agar
(TSA; Difco), incubated at 37 °C for 24 h, and stored at 4°C before used.
2.2.2. Culture preparation
Each strain of E. coli O157:H7, S. Typhimurium, and L. monocytogenes
was cultured in 5 ml TSB at 37 °C for 24 h and harvested by centrifugation
at 4000 ×g for 20 min at 4 °C. Cell pellets were obtained by washing with
sterile 0.2% peptone water (Bacto, Sparks, MD) in three times and the final
pellets were resuspended in 9ml PW, corresponding to approximately 108 to
109 CFU/g. Resuspended pellets of each strain of all pathogen species were
combined to constitute a 3-pathogen mixed culture cocktail. By three times
of 10-fold serial dilution with 0.2% sterile peptone water, initial
concentration of prepared culture was approximately 5-6 log CFU/g.
2.2.3. Culture inoculation
Culture suspension was serially diluted with 0.2% sterile peptone water
and 0.1ml diluent was spread-plated onto selective media. Sorbitol
MacConkey Agar (SMAC; Difco), Xylose Lysine Desoxycholate Agar
(XLD; Difco), and Oxford Agar Base with antimicrobial supplement MB
11
Cell (MOX; MB Cell) were used as selective media to enumerate E. coli
O157:H7, S. Typhimurium and L. monocytogenes respectively. To get a
numerable number of colonies on the tested media, two kinds of sequential
diluents were spread-plated. After the inoculation, the media was dried for
30 min approximately.
2.2.4. UV treatment
In order to minimize photoreactivation, all of the UV-treated petri dishes
were covered with an aluminum foil. Inoculated samples were treated with
275nm LEDs, 5.57 μW/cm2 intensity for 0, 0.5, 1, 3, 5 min at adjusted
temperature. Doses of UV were calculated by multiplying UV intensities by
the UV irradiation times. For testing at different temperature, UV irradiation
was applied to samples for 1 min at 4, 15, 25, 37 °C. In all temperature tests,
samples were kept at the controlled temperature of chamber for 5 min to
accommodate for the environmental change. For examining of humidity
impact to the UV irradiation, temperature and humidity chamber (TH-TG-
300, JEIO TECH, Korea) was used to adjust humidity of 30, 60, 90% with
maintained temperature at 25°C.
12
2.2.5. Bacterial enumeration
For enumeration of E. coli O157:H7 and S. Typhimurium, and L.
monocytogenes, Sorbitol MacConkey Agar (SMAC; Difco) and Xylose
Lysine Desoxycholate Agar (XLD; Difco) and Oxford Agar Base with
antimicrobial supplement MB Cell (MOX; MB Cell) were used respectively.
All plates were incubated at 37 °C for 24 h and enumerated.
2.2.6. Statistical analysis
All experiments were duplicate-plated and replicated three times. All
data were analyzed with ANOVA using Statistical Analysis System (SAS
Institute, Cary, NC, USA) and Duncan`s multiple range test to determine if
there were significant differences (P < 0.05) in mean values of
microorganism populations.
13
2.3. UV treatment for water decontamination
2.3.1. Bacterial strains and inoculum conditions
Bacterial strains, E. coli O157:H7 (ATCC 35150, ATCC 43889, ATCC
43890), S. Typhimurium (ATCC 19585, ATCC 43971, DT 104), L.
monocytogenes (ATCC 7644, ATCC 19114, ATCC 19115, and
Staphylococcus aureus (ATCC 13565, ATCC 25923, ATCC 29213) were
obtained from the Bacterial Culture Collection at Seoul National University
(Seoul, Korea). Stock cultures were prepared at - 80℃ in 0.7ml of Tryptic
Soy Broth (TSB; Difco, Becton Dickinson, Sparks, MD, USA) and 0.3ml of
50% glycerol solution. In this study bacteria were streaked onto Tryptic Soy
Agar (TSA; Difco), incubated at 37°C for 24 h, and stored at 4°C before
used. For the scale-up water experiment, general bacteria were obtained from
a creek (Seoul, Korea).
14
2.3.2. Culture preparation
Each strain of E. coli O157:H7, S. Typhimurium, L. monocytogenes, and
Staphylococcus aureus was cultured in 5 ml TSB at 37 °C for 24 h and in
case of general bacteria, 1 ml of creek water was mixed with 20 ml TSB and
cultured at 37 °C for 24 h. Then harvested by centrifugation at 4000 ×g for
20 min at 4 °C. Cell pellets were obtained by washing with sterile 0.2%
peptone water (Bacto, Sparks, MD) in three times. The final pellets were
resuspended in 9 ml PW, corresponding to approximately 108 to 109 CFU/ml.
2.3.3. Culture inoculation
Sterile distilled water (DW) was used in this experiment. In case of small
batch system for water decontamination, mixed culture cocktail (0.1 ml) was
inoculated into 25 ml of DW at room temperature. For scale-up system, each
4 ml, 8 ml, 12 ml aliquot of mixed culture cocktail of E. coli O157:H7 and S.
aureus was inoculated into 1 L, 2 L and 3 L of DW respectively. Equal
amount of cultured general bacteria inoculum was separately inoculated into
the DW suspension to investigate the single decontamination effect of
15
general bacteria. 8 ml of culture cocktail was inoculated into 2 L of DW to
be used in the continuous type of water decontamination system.
2.3.4. UV treatment
For small scale of decontamination system, inoculated samples were
treated with a 278 nm LED at 4.5 cm distance between sample and the UV
source. 10 ml of inoculated water sample was contained in the petri dish (50
mm x 15 mm; internal dimension) and the sample was serially mixed by
stirring bar to irradiate evenly. Dosage of UV were calculated by multiplying
UV intensities by the UV irradiation times.
For the scale-up system, treatment method was roughly similar to the
previous small scale system, but in this case 4 LEDs were used in order to
irradiate uniformly on the large surface of water.
Continuous system (Fig. 3) consisted of a power supply (TPM series,
Toyotech, Japan), a peristaltic pump (JWS600, JenieWell, Korea), and a
manufactured quartz pipe (Kum-kang quartz, Korea) which is attached with
LED modules. Inoculated water sample was moved by the pump, along the
silicon tube and treated on the way of flowing. 2 to 4 LED modules which
have the intensity of 50 mW were attached to the quartz pipe and flow rates
were adjusted to the 0.5, 1, 1.5 and 2 liter per minute (LPM).
16
Fig. 3. Continuous water decontamination system at Seoul National University (Seoul, Korea).
Quartz line with
LED modules
Peristaltic Pump Before After
Power supply
supply
17
2.3.5. Bacterial enumeration
1-ml aliquots of sample were 10-fold serially diluted in 9-ml blanks of 0.2%
PW, and 0.1 ml of sample or diluent was spread-plated onto each selective
medium. Sorbitol MacConkey Agar (SMAC; Difco), Xylose Lysine
Desoxycholate Agar (XLD; Difco), Oxford Agar Base with antimicrobial
supplement MB Cell (MOX; MB Cell), Baird-Parker Agar (BP; Oxoid) with
egg-yolk tellurite enrichment, and Tryptic Soy Agar (TSA; Difco) were used
as selective media to enumerate E. coli O157:H7, S. Typhimurium, L.
monocytogenes, S. aureus and general bacteria respectively. All agar media
were incubated at 37°C for 24-48 h and typical colonies were counted.
2.3.6. Statistical analysis
All experiments were duplicate-plated and replicated three times. All
data were analyzed with ANOVA using Statistical Analysis System (SAS
Institute, Cary, NC, USA) and Duncan`s multiple range test to determine if
there were significant differences (P < 0.05) in mean values of
microorganism populations.
18
III. RESULTS
3.1. Spectral characteristics of DUV-LED
3.1.1. Emission spectrum of DUV-LED
Typical spectral irradiance of 275 nm UV-LED was measured by
spectrometer (AvaSpec-ULS2048-USB2-UA-50) as shown in fig.3. The full
width at half maximum (FWHM) which means the wavelength gap between
the half output of the peak intensity was 11.3 nm for the 275nm LED.
19
(A)
(B)
Wavelength (nm)
240 260 280 300 320 340 360
Norm
aliz
ed inte
nsi
ty
0.0
0.2
0.4
0.6
0.8
1.0
Fig. 4. External appearance (A) and emission spectrum (B) of the DUV-LED
module.
20
3.1.2. Comparison of properties between DUV-LEDs and LP lamps
Warm-up time of both DUV-LEDs and low pressure (LP) lamps was
determined by measuring the intensity over time (0 to 10 min). After 5 min,
intensity of DUV-LEDs was decreased about 5.45%, on the other hand
intensity of LP lamps was increased about 90.43%. Intensity change
accordance to temperature presented different patterns between DUV-LED
and LP lamp. As temperature increases, intensity of LED was slightly
decreased while LP lamp showed intensity increasing until it reaches to the
peak temperature around 30 °C and then decreased.
21
(A)
(B)
Fig. 5. Comparison between DUV-LED and LP lamp for (A) warm-up time
and (B) variation of intensity in accordance with temperature
time (min)
0 2 4 6 8 10 12
Irra
dia
nce
rate
0.0
0.2
0.4
0.6
0.8
1.0
1.2
DUV-LED
LP lamp
Temperature ( )℃
0 10 20 30 40 50
UV
outp
ut (%
)
0
20
40
60
80
100
DUV-LED
LP lamp
22
3.1.3. Assessment of the effective area by LED arrangements
Intensity at a specified distance from DUV-LED is measured and petri
factor of each point was calculated. Fig. 4 shows each spatial disposition of
four LEDs. In order to get collimated beam of UV irradiation, the petri factor
should satisfy the value of over than 0.9. For arrangement of 4 corners, the
petri factor was calculated as 0.48, 0.90, 0.82 and 0.80 at the distance of 2, 4,
6, 8 cm respectively. In other configuration, the petri factor was steadily
increased from around 0.5 to 0.9. All configuration showed decreasing
intensity with increasing distance between LED and probe. The 4 corner
configuration at 4cm distance had an intensity of 4.41 μW/cm2 while other
configuration at 8cm distance which have petri factor of 0.9, that means even
distribution measured as lower than 3.2 μW/cm2. Also, intensity at a
specified distance from DUV-LED is measured. Intensity varied from 7.1 to
0.7 μW/cm2 as distance from lighting sources increases from 2 to 20cm.
23
(A)
Distance from LEDs (cm)
1 2 3 4 5 6 7 8 9
Pe
tri f
act
or
0.0
0.2
0.4
0.6
0.8
1.0
Original Evenly spacedStraight line4 CornersStaggered line
24
(B)
Distance from LEDs (cm)
1 2 3 4 5 6 7 8 9
Inte
nsi
ty (
μW
/cm
2)
0
2
4
6
8
10
12
14
OriginalEvenly spacedStraight line4 CornersStaggered line
Fig. 6. Petri factor (A) and irradiance (B) for LEDs accordance with spatial
arrangements as a function of distance from the LED.
25
Distance from LEDs (cm)
0 5 10 15 20
Inte
nsi
ty (
μW
/cm
2)
0
1
2
3
4
5
6
7
8
y = 0.0255x2 - 0.9080x + 8.7243
Fig. 7. Irradiance of four corner arranged LEDs as a function of distance
from LED
26
3.2. Effect of various conditions on inactivation of food-borne pathogens
by using DUV-LED
3.2.1. Bactericidal effect by UV treatment on media
The reduction in viability of food-borne pathogen by UV radiation is
presented in table 1. As the dose of UV radiation increased from 0 to 1.67
mJ/cm2, all kinds of food-borne pathogens such as E. coli O157:H7, S.
Typhimurium and L. monocytogenes showed great reduction by >5 log.
Initial populations of E. coli O157:H7, S. Typhimurium and L.
monocytogenes were 6.21, 6.11, and 5.75 log CFU/ml respectively. The
population (log CFU/ml) of surviving E. coli O157:H7 was decreased by
4.58 and 2.70 after UV irradiation of 0.17 and 0.34 mJ/cm2, >5 log reduction
was observed at the dose of 1 mJ/cm2. For S. Typhimurium, the overall
reduction pattern is similar to that of E. coli O157:H7. The number of S.
Typhimurium treated by UV-C irradiation was 4.45 and 3.46 log CFU/ml
after irradiation of 0.17 and 0.34 mJ/cm2 respectively. After 1 mJ/cm2 of UV
treatment, S. Typhimurium were also reduced below the detection limit. In
the response of L. monocytogenes to different UV doses, the level of
surviving population was 5.36, 4.82, 2.16 log CFU/ml after UV dose of 0.17,
27
0.34, 1.00 mJ/cm2 respectively. UV dose of 1.67 mJ/cm2 was required to
inactivate below the detection limit.
28
Table 1. Surviving populations a of E. coli O157:H7, S. Typhimurium, and L. monocytogenes on media following UV-
C irradiation, 4cm distance between petri dish and LED, for intensity of 5.57 μW/cm2
a Data represent means ± standard deviations from three replications.
b Values followed by the same letters within the column per parameter are not significantly different (P > 0.05).
Treatment
time (min)
Dose
(mJ/cm2)
Population (log10 CFU/g) by organism b
E. coli O157:H7 S. Typhimurium L. monocytogenes
0 0 6.21±0.15 A 6.11±0.10 A 5.75±0.34 A
0.5 0.17 4.58±0.10 B 4.45±0.33 B 5.36±0.43 AB
1 0.34 2.70±0.25 C 3.46±0.40 C 4.82±0.38 B
3 1.00 0.00±0.00 D 0.00±0.00 D 2.16±0.59 C
5 1.67 0.00±0.00 D 0.00±0.00 D 0.00±0.00 D
29
3.2.2. Effect of UV irradiation temperature
Table 2 shows the bactericidal effect of 1 min treatment of UV irradiation
against food-borne bacteria such as E. coli O157:H7, S. Typhimurium and L.
monocytogenes on different temperatures at 0, 4, 15, 25 or 37 °C. Survival
population of all three food-borne pathogens was decreased with increasing
temperatures. For E. coli O157:H7, the significant reduction (P < 0.05) of
4.22 log was observed at 0°C. As treatment temperature increases from 0 to
37 °C, reduction level of E. coli O157:H7 was gradually increased, in
particular at more than 25 °C, it reduced by >5 log. Populations of 3.61, 3.39,
3.20, 2.94, 2.22 log CFU/ml were observed in S. Typhimurium after 1 min of
UV treatment at 0, 4, 15, 25 or 37 °C, respectively. Also, treatment at 37 °C
significantly reduced (P < 0.05) levels of S. Typhimurium by > 4 log,
compared from the control. The surviving population of UV treated L.
monocytogenes was significantly (P < 0.05) different from the control level,
but among temperature conditions, irradiated samples were not significantly
different (P > 0.05).
30
Table 2. Surviving populations a of E. coli O157:H7, S. Typhimurium, and L. monocytogenes on media following UV-
C irradiation for 1 min at 0°C, 4 °C, 15 °C, 25 °C, or 37°C. 4 cm distance between petri dish and LED
a Data represent means ± standard deviations from three replications.
b Values followed by the same letters within the column per parameter are not significantly different (P > 0.05).
Treatment
temperature (℃)
Population (log10 CFU/g) by organism b
E. coli O157:H7 S. Typhimurium L. monocytogenes
Control 6.42±0.17 A 6.26±0.02 A 5.35±0.13 A
0 2.20±0.64 B 3.61±0.16 B 4.33±0.22 B
4 1.98±0.19 BC 3.39±0.31 B 4.35±0.09 B
15 1.47±0.25 CD 3.20±0.10 BC 4.20±0.14 B
25 1.16±0.28 DE 2.94±0.43 C 4.35±0.09 B
37 0.53±0.40 E 2.22±0.17 D 4.31±0.09 B
31
3.2.3. Effect of UV irradiation humidity
Surviving populations of E. coli O157:H7, S. Typhimurium and L.
monocytogenes on media following UV treatment at the different humidity
of 30, 60, and 90 % is presented in Table 3. Only for E. coli O157:H7, the
significant reduction (P < 0.05) was observed at 90% relative humidity
condition compared with other conditions such as 30 and 60 %, about 0.5 log
of more reduction at 90% humidity. In case of S. Typhimurium and L.
monocytogenes, there were no significant (P > 0.05) differences in various
humidity conditions.
32
Table 3. Surviving populations a of E. coli O157:H7, S. Typhimurium, and L. monocytogenes on media following UV-
C irradiation for 1 min at the humidity of 30%, 60% and 90%, 25℃, 12.5 cm distance between petri dish and LED
a Data represent means ± standard deviations from three replications.
b Values followed by the same letters within the column are not significantly different (P > 0.05).
Treatment
humidity (%)
Population (log10 CFU/g) by organism b
E. coli O157:H7 S. Typhimurium L. monocytogenes
Control 5.58±0.03 A 5.00±0.08 A 4.41±0.08 A
30 1.55±0.20 B 2.82±0.35 B 2.81±0.04 B
60 1.61±0.16 B 2.72±0.09 B 2.83±0.05 B
90 1.11±0.09 C 2.76±0.06 B 2.82±0.10 B
33
3.3. UV treatment for water decontamination
3.3.1. Bactericidal effect by UV treatment at batch water system
Populations (log CFU/g) of E. coli O157:H7, S. Typhimurium and L.
monocytogenes in 10 ml of water during UV treatment are depicted in Table
4. The levels of surviving cells of all pathogens were reduced to below the
detection limit (1.0 log CFU/g) after UV treatment at the dose of 3 mJ/cm2.
The initial population of E. coli O157:H7 was 6.72 log CFU/g and the
number of surviving cells was 5.18, 2.87, 1.69 and 1.07 log CFU/g after
irradiation of 0.2 to 2 mJ/cm2. For S. Typhimurium the overall inactivation
pattern is similar to that of E. coli O157:H7. Populations of 5.09. 3.75, 2.14
and 1.30 log CFU/g were observed in S. Typhimurium after UV dose of 0.2,
0.5, 1 and 2 mJ/cm2 respectively. In case of L. monocytogenes, the level of
surviving population was decreased as 4.84, 3.76 and 1.97 log CFU/g after
irradiation of 0.2 to 1 mJ/cm2. At the dosage of 2 mJ/cm2, treatment
significantly reduced (P < 0.05) below the detection limit
34
Table 4. Surviving populations a of E. coli O157:H7, S. Typhimurium, and L. monocytogenes in batch water system
following UV-C irradiation. Treated at room temp, 4.5 cm distance between sample and LED
a Data represent means ± standard deviations from three replications.
b Values followed by the same letters within the column per parameter are not significantly different (P < 0.05).
Dose (mJ/cm2) Population (log10 CFU/g) by organism b
E. coli O157:H7 S. Typhimurium L. monocytogenes
0 6.72±0.28 A 6.71±0.17 A 5.29±0.11 A
0.2 5.18±0.42 B 5.09±0.15 B 4.84±0.22 B
0.5 2.87±0.23 C 3.75±0.32 C 3.76±0.28 C
1 1.69±0.27 D 2.14±0.60 D 1.97±0.20 D
2 1.07±0.12 E 1.30±0.30 E <1.00 E
3 <1.00 E <1.00 E <1.00 E
35
3.3.2. Bactericidal effect by UV treatment at scale-up system
The survival of E. coli O157:H7, S. aureus and general bacteria in scale-
up water decontamination system following UV treatment is shown in Fig. 8.
In general, the reduction of E. coli O157:H7, S. aureus and general bacteria
decreased with increasing the amount of treating water 1 L to 3 L. Fig 8 (A)
shows the inactivation effect of UV irradiation against E. coli O157:H7 in
scaled-up water. At the UV dosage of 1.5 mJ/cm2, populations were reduced
below the detection limit (1.0 log CFU/ml) for the scale at 1 L and 2 L of
water. For the scale of 3 L, population was reduced below the detection limit
after treatment of 2.0 mJ/cm2. The inactivation of S. aureus in scale-up
system is shown in Fig. 8 (B), and the trend of reduction was similar to that
of E. coli O157:H7. At the UV dosage of 2.0 mJ/cm2, populations were
reduced below the detection limit (1.0 log CFU/ml) for the scale at 1 L and
reduced by 6.09 and 4.87 log CFU/ml at 2 L and 3 L of water. For the scale
of 3 L, population was reduced below the detection limit after treatment of
3.0 mJ/cm2. Fig. 8 (C) shows the bactericidal effect of UV treatment against
general bacteria. At the UV dosage of 3.0 mJ/cm2, surviving populations
were reduced by 5.38 and 4.37 log CFU/ml for 2 L and 3 L of water,
respectively, and was lowered to below detection limit for 1 L of water.
36
Dose (mJ/cm2)
0.0 0.5 1.0 1.5 2.0 2.5 3.0 3.5
Lo
g C
FU
/ml
0
1
2
3
4
5
6
7
Dose (mJ/cm2)
0.0 0.5 1.0 1.5 2.0 2.5 3.0 3.5
Log C
FU
/ml
0
1
2
3
4
5
6
7
(A)
(B)
37
Dose (mJ/cm2)
0.0 0.5 1.0 1.5 2.0 2.5 3.0 3.5
Lo
g C
FU
/ml
0
1
2
3
4
5
6
7
(C)
Fig. 8. Survival curves for Escherichia coli O157:H7 (A), Staphylococcus
aureus (B) and General bacteria (C) by UV-C irradiation from DUV-LED
with water volume of �, 1L; ¡, 2L; q, 3L.
38
3.3.3. Bactericidal effect by UV treatment at continuous water system
The reduction of E. coli O157:H7, S. Typhimurium and L. monocytogenes
at continuous water system during UV irradiation is presented in Tables 5, 6
and 7, respectively. In general, the reduction level of E. coli O157:H7, S.
Typhimurium and L. monocytogenes increased with decreasing flow rate and
increasing intensity. Table 5 shows the inactivation effect of UV irradiation
against E. coli O157:H7 in continuous system. UV treatment for 100 mW
with lower than at the flow rate of 1.0 LPM, 150 mW with lower than at the
flow rate of 1.5 LPM and 200mW with lower than at the condition of 2.0
LPM accomplished more than 99.9% reduction. Table 6 shows the
inactivation effect of UV irradiation against S. Typhimurium in continuous
water system. UV treatment for 100 mW showed 1.20, 1.40, 1.87 and 2.87
log reductions at 2.0, 1.5, 1.0 and 0.5 LPM, respectively. For intensity of 150
mW at the flow rate of 0.5 LPM and 200mW with lower than at the
condition of 1.0 LPM accomplished more than 99.9% reduction. The
inactivation of L. monocytogenes in continuous water system is shown in
Table 7, and the trend of reduction was similar to those of E. coli O157:H7
and S. Typhimurium. But just at the condition as intensity of 200 mW with
the flow rate of 0.5 LPM showed 99.9% reduction level of L. monocytogenes.
39
Fig. 9 shows the reduction curves for E. coli O157:H7, S. Typhimurium
and L. monocytogenes in continuous water decontamination system
according to the dose of UV irradiation. As the dose increases, the amount of
reduction was increased for all three pathogens, and the graph presented the
greater resistance in order by L. monocytogenes, S. Typhimurium and E. coli
O157:H7.
40
Table 5. Reduction levels a of Escherichia coli O157:H7 in continuous water system following UV-C irradiation at
various flow rates and intensities
Flow rate (LPM) Log reduction [log10 (N0/N)] by treatment type b
100mW 150mW 200mW
2.0 1.97±0.32 Aa
(98.93%)
2.82±0.28 Ab
(99.85%)
3.36±0.30 Ab
(99.97%)
1.5 2.36±0.12 Aa
(99.56%)
3.81±0.31 Bb
(99.98%)
4.06±0.19 Bb
(>99.99%)
1.0 3.24±0.32 Ba
(99.94%)
4.20±0.11 Bb
(>99.99%)
4.90±0.10 Cc
(>99.99%)
0.5 4.69±0.40 Ca
(>99.99%)
5.02±0.57 Ca
(>99.99%)
6.38±0.06 Db
(>99.99%)
a Data represent means ± standard deviations from three replications.
b Means with the same uppercase letter in the same column are not significantly different (P > 0.05). Means with the
same lowercase letter in the same row are not significantly different (P > 0.05).
41
Table 6. Reduction levels a of Salmonella Typhimurium in continuous water system following UV-C irradiation at
various flow rates and intensities
Flow rate (LPM) Log reduction [log10 (N0/N)] by treatment type b
100mW 150mW 200mW
2.0 1.20±0.17 Aa
(93.74%)
1.38±0.39 Aa
(95.83%)
1.85±0.39 Aa
(98.59%)
1.5 1.40±0.19 Aa
(96.05%)
1.81±0.37 ABab
(98.46%)
2.27±0.38 ABb
(99.46%)
1.0 1.87±0.29 Ba
(98.66%)
2.11±0.35 Ba
(99.22%)
3.06±0.53 Bb
(99.91%)
0.5 2.87±0.25 Ca
(99.86%)
3.67±0.26 Cb
(99.98%)
5.81±0.43 Cc
(>99.99%) a Data represent means ± standard deviations from three replications.
b Means with the same uppercase letter in the same column are not significantly different (P > 0.05). Means with the
same lowercase letter in the same row are not significantly different (P > 0.05).
42
Table 7. Reduction levels a of Listeria monocytogenes in continuous water system following UV-C irradiation at
various flow rates and intensities
a Data represent means ± standard deviations from three replications.
b Means with the same uppercase letter in the same column are not significantly different (P > 0.05). Means with the
same lowercase letter in the same row are not significantly different (P > 0.05).
Flow rate (LPM) Log reduction [log10 (N0/N)] by treatment type b
100mW 150mW 200mW
2.0 0.42±0.14 Aa
(62.27%)
0.44±0.28 Aa
(63.97%)
0.93±0.27 Ab
(88.16%)
1.5 0.58±0.23 Aa
(73.56%)
0.60±0.27 Aa
(75.07%)
1.19±0.38 Aa
(93.49%)
1.0 0.63±0.15 Aa
(76.56%)
0.89±0.09 Aa
(87.02%)
1.49±0.41 Ab
(96.79%)
0.5 1.48±0.17 Ba
(96.69%)
2.31±0.42 Bb
(99.51%)
3.47±0.41 Bc
(99.97%)
43
Dose (mJ/cm2)
0 1 2 3 4 5 6 7 8
log
red
uction
(C
FU
/ml)
0
1
2
3
4
5
6
7
Dose (mJ/cm2)
0 1 2 3 4 5 6 7 8
log
re
du
ctio
n (
CF
U/m
l)
0
1
2
3
4
5
6
7
(A)
(B)
44
Dose (mJ/cm2)
0 1 2 3 4 5 6 7 8
log r
educt
ion (
CF
U/m
l)
0
1
2
3
4
5
6
7
(C)
Fig. 9. Survival curves for Escherichia coli O157:H7 (A), Salmonella
Typhimurium (B) Listeria monocytogenes (C) by UV-C irradiation from
DUV-LED with power of �, 100mW; ¡, 150mW; q, 200mW.
45
IV. DISCUSSION
Traditionally, UV irradiation has been used for disinfecting surface, air
and water for a long time. Also the decontamination effect of UV irradiation
has been widely verified by many studies until now. As one of the non-
thermal methods for reducing a broad range of microorganisms, including
some pathogens, it has been considered to be a safety assurable treatment. LP
lamp which had been commonly used has some side effects such as low
efficiency and potential of mercury leakage so it is really necessary to
replace this technology. Therefore in this study, I confirmed that the basic
spectral characteristics which associated with bactericidal power compared
to LP lamp. Also the real pasteurization effect of UV irradiation by DUV-
LED technology was investigated.
For this research the DUV-LED which has the wavelength of 275 ± 3 nm
was selected because of its cost and the germicidal range. Globally, the
technology of DUV-LED still in development stage and a few companies
such as Sensor Electronic Technology (SET) and LG innotek is now
producing the prototype of LED for lower UV-C range lower than 280nm.
That is the reason of high cost is set in production. 200 to 280 nm range of
UV-C radiation has germicidal effect which depends on the wavelength. The
46
maximum DNA absorption of UV-C peaks at the wavelength of 260-265 nm
(Kowalski, 2009; US EPA, 2006). By considering both cost and germicidal
effectiveness, the LED for the wavelength of 275nm was chosen for this
study.
It is important to minimize the amount of light loss by taking optimal
LED alignment and distance adjustment while lowering overall cost. Colleen
Bowker et al. (2011) used Comsol Multiphysics method to investigate an
optimal collimated irradiation design. They reported that the simulated four
corners configuration showed highest petri factor over other type of arrays,
but it had limitation for prediction result. Therefore actual evaluation of petri
factor and intensity for DUV-LED was required. By comparing each
arrangement, more than 0.9 of petri factor is measured at 4 cm distance in
four corner array and 8 cm distance in others. Taken together with irradiance
factor, as four corners arrangement at 4 cm distance showed higher intensity
than 8 cm distance by other arrangements, so it was selected for the most
proper irradiation design.
As shown in Fig. 7 (A), the intensity of UV lamp reached to maximum
range after 5 min or more so that there should be a possibility of delaying
disinfecting effect. But in case of DUV-LED, high intensity was measured
from beginning and it consistently maintained. For these reason, LP lamp’s
warm up time could be removed by alternating to DUV-LED technology. Fig.
47
7 (B) indicates another benefit of DUV-LED for wide range of working
temperatures, especially at cold temperature around 0 to 4 °C. By comparing
each intensity at 4 °C and room temperature, 4.5% higher irradiance power
was measured at cold condition. Peak intensity of LP lamp was showed at
the room temperature and decreased about 62.5% at 4 °C. Similar result
already had been reported by Crawford et al. (2005). There are plenty of
microorganisms which can grow at refrigeration temperatures, particularly
Listeria monocytogenes is one of the major food-borne pathogens (Donnelly
and Briggs, 1986; Rosenow and Marth, 1987). For inactivating these bacteria,
DUV-LED is more meaningful method than using a LP lamp.
The populations of surviving all three pathogens showed decreasing
tendency when treated UV energy increased. L. monocytogenes of gram-
positive bacterium had more resistance to UV radiation than gram-negative
bacteria such as E. coli O157:H7 and S. Typhimurium. Because a thick
peptidoglycan wall surrounds the cytoplasmic membrane of gram-positive
bacteria, while gram-negative bacteria possess an external membrane (Virto
et al., 2005). Many research for disinfecting food-borne pathogens at various
food samples reported that L. monocytogenes is considered as one of the
most UV-resistant bacteria (Lu et al., 2011; Guerrero-Beltran and Barbosa-
Canovas, 2006; Gabriel and Nakano, 2009).
48
Most of the UV-related studies have focused on the storage temperature
which following UV treatment (Lemoine et al., 2007; Gonzalez-Aguilar et
al., 2004). Along with storage temperature, treatment temperature condition
is one of the key factors. In present research, treatment temperature had a
profound effect on inactivating E. coli O157:H7 and S. Typhimurium. When
temperature increases from 0 to 37 °C the population of surviving both
pathogens were decreased. Although DUV-LED emits higher intensity of
radiation at lower temperature, inactivation effect showed opposite results.
The enhanced inactivation at higher temperatures might be explained by
phase transition of the phospholipid molecules which is in the cell membrane
(Jayaram et al, 1992). Thayer and Boyd (1995) stated that inactivation level
of bacteria to gamma radiation was directly related to chemical reactions at
treatment temperatures. Rather than interaction of irradiation, cellular
inactivation is due to interactions with radiolytic products of water. It can be
applied to temperature-dependent UV radiation, because of photochemical
reactions which can occur as a direct result of UV radiation energy (Gayan et
al., 2013). And also, the fluidity of the cell membrane was increased by
heating, making the affected cells more sensitive to UV exposure (Gayan et
al., 2014). On the other hand, UV treatment temperature dose not effect to
the reduction rate of L. monocytogenes because of its bacterial characteristics.
49
To adopt LED technology commercially, scale-up system of UV treatment
is necessary for evaluating at the actual effectiveness. For that reason, 10 ml
capacity of initial treatment was scaled–up by 1 L to 3L. As shown in Fig. 8,
overall inactivation tendency was similar to each amount of treated water but
when the volume of water is increased, slight more resistance to the same
dosage of UV radiation was investigated. The sensitivity to ultraviolet
irradiation was different between kinds of bacteria, it was hard to inactivate
in the order of E. coli O157:H7, S. aureus and general bacteria. The
preference of batch or continuous type of water treatment system would be
determined by the purpose and process of use. But in consideration of all
cases, continuous type of decontamination system deserves careful
examination. In Tables 5, 6 and 7, reduction population were determined by
the condition of each level of flow rate and intensity. As the flow rate
increased, reduction level of each pathogen was decreased because of the
shorter UV treatment time. By combination of both factors, flow rate and
intensity, the inactivation effect should be explained at continuous system as
a consequential in the sole of UV dosage factor. As a result, continuous
system conditions reduced the disinfection ability but the inactivation rate
showed dependently on the calculated dosage of UV irradiation. Therefore,
UV treatment system in order to inactivate pathogen should be determined
by the degree of UV dose eventually.
50
In conclusion, these overall results suggest that conventional UV lamp for
the inactivation of food-borne pathogens can be fully substituted by DUV-
LED technology. Spectral characteristics of DUV-LED such as fast
stabilizing intensity and a property of insensitive to temperature should be
well appreciated for a strong point. DUV-LED leads to effective inactivation
of E. coli O157:H7, S. Typhimurium and L. monocytogenes both on the
surface of medium and in the water system at various conditions.
Furthermore, from our knowledge, this is the first report applying DUV-LED
technology directly to inactivating food-borne pathogens. In addition, DUV-
LED treatment for these large-capacity and high flow speed have never been
reported previously. DUV-LED could be a very promising alternative
technology for UV lamp in the field of controlling food-borne pathogens.
Moreover, applying to the real food sample and comparing disinfection
effectiveness of UV lamp must be studied in the future.
51
V. REFERENCES
Baird-Parker, A.C., 1990. Foodborne salmonellosis. Lancet 336, 1231–1235.
Bettles, T., Schujman, S., Smart, J. A., Liu, W., Schowalter, L., 2007. UV
Light Emitting Diodes; Their Applications and Benefits.
International Ultraviolet Association Conference. Los Angeles, CA.
Bintsis, T., Tzanetaki, E.L., Robinson, R.K., 2000. Existing and potential
applications of ultraviolet light in the food industry — A critical
review. Journal of the Science of Food and Agriculture. 80, 637–
645.
Bolton, J.R., Linden, K.G., 2003. Standardization of methods for fluence
(UV dose) determination in bench-scale UV experiments. Journal of
Environmental Engineering 129 (3), 2009-2215.
52
Bowker C., Sain A., Shatalov M., Ducoste J., 2011. Microbial UV fluence-
response assessment using a novel UV-LED collimated beam
system. Water Research 45 (5), 2011-2019
Crawford, M.H., Banas, M.A., Ross, M.P., Ruby, D.S., Nelson, J.S., boucher,
R., Allerman, A.A., 2005. Final report: Ultraviolet Water
Datta, A.R., 2003. Listeria monocytogenes, International handbook of
foodborne pathogens. Marcel Dekker, Inc., New York, NY 105-121
Donnelly, C.W., Briggse, H., 1986. Psychrotrophic growth and thermal
inactivation of Listeria monocytogenes as as function of milk
composition. Journal of Food Protection 49, 994-998.
Doyle, M.P., 1991. Escherichia coli O157:H7 and its significance in foods.
International Journal of Food Microbiology 12, 289–302.
Farber, J.M., Peterkin, P.I., 1991. Listeria monocytogenes, a food-borne
pathogen. Microbiological Reviews. 55(3):476–511.
53
Franz, C.M.A.P., Specht, I., Cho, G., Graef, V., Stah, M.R., 2009. UV-C
inactivation of microorganisms in naturally cloudy apple juice using
novel inactivation equipment based on Dean Vortex technology.
Food Control 20, 1103–1107.
Gabriel, A.A., Nakano, H., 2009. Inactivation of Salmonella, E. coli and
Listeria monocytogenes in phosphate-buffered saline and apple juice
by ultraviolet and heat treatments. Food Control, 20(4), 443-446.
Gayán, E., Mañas, P., Álvarez, I., Condón, S., 2013. Mechanism of the
synergistic inactivation of Escherichia coli by UV-C light at mild
temperatures. Applied and Environmental Microbiology 79(14),
4465-4473.
Gayán, E., Condón, S., & Álvarez, I., 2014. Biological aspects in food
preservation by ultraviolet light: a review. Food and Bioprocess
Technology 7(1), 1-20.
Gonzalez-Aguilar, G., Wang, C.Y., Buta, G.J., 2004. UV-C irradiation
reduces breakdown and chilling injury of peaches during cold
storage. Journal of the Science of Food and Agriculture 84, 415–422.
54
Guerrero–Beltrán, J.A., Barbosa–Cánovas, G.V., 2004. Review: advantages
and limitations on processing foods by UV light. Food Science and
Technology International 10, 137–148.
Guerrero-Beltran, J.A., Barbosa-Canovas, G.V., 2005. Reduction of
Saccharomyces cerevisiae, Escherichia coli and Listeria innocua in
apple juice by ultraviolet light. Journal of Food Process Engineering,
28(5), 437-452.
Hamamoto, A., Mori, M., Takahashi, A., Nakano, M., Wakikawa, N.,
Akutagawa, M., Kinouchi, Y., 2007. New water disinfection system
using UVA light‐emitting diodes. Journal of applied microbiology
103(6), 2291-2298.
Jayaram, S., Castle, G.S.P., Margaritis, A., 1992. Kinetics of sterilization of
Lactobacillus brevis cells by the application of high voltage pulses.
Biotechnology and Bioengineering 40(11), 1412-1420.
Kowalski, W., 2009. Ultraviolet germicidal irradiation handbook. UVGI for
air and surface disinfection. New York: Springer.
55
Lemoine, M.L., Civello, P.M., Martinez, G.A., Chaves, A.R., 2007.
Influence of postharvest UV-C treatment on refrigerated storage of
minimally processed broccoli (Brassica oleracea var. Italica).
Journal of the Science of Food and Agriculture 87, 1132-1139.
Lopez-Malo, A., Palou, E., Barbosa-Cánovas, G.V., Tapia, M.S., Cano, M.P.,
2005. Ultraviolet light and food preservation. Novel food processing
technologies 405-421.
Lu, G., Li, C., Liu, P., 2011. UV inactivation of milk-related microorganisms
with a novel electrodeless lamp apparatus. European Food Research
and Technology 233(1), 79-87
Purification systems for rural environments and mobile applications. Sandia
Report SAND 2005-7245.
Rosenow, E.W., Marth, E.H., 1987. Growth of Listeria monocytogenes in
skim, whole and chocolate milk, and in whipping cream during
incubation at 4, 8, 13, 21 and 35 °C. Journal of Food Protection 50,
452-459.
56
Scharff, R.L., 2012. Economic burden from health losses due to foodborne
illness in the United States. Journal of Food Protection 75(1), 123-
131.
Sodha, S.V., Heiman, K., Gould, L.H., Bishop, R., Iwamoto, M., Swerdlow,
D.L., Griffin, P.M., 2014. National patterns of Escherichia coli
O157 infections, USA, 1996–2011. Epidemiology and Infection 1-7.
Thayer, D.W., Boyd, G., 1995. Radiation sensitivity of Listeria
monocytogenes on beef as affected by temperature. Journal of Food
Science 60, 237-240.
U.S. Environmental Protection Agency (U.S. EPA), 2006. Ultraviolet
disinfection guidance manual. EPA 815-R-06-007, Office of Water,
Washington, D.C.
US-FDA, United States Food and Drug Administration, 2000. Ultraviolet
radiation for the processing and treatment of food. Code of Federal
Regulations 21 (Part 179.39).
57
Virto, R., Manas, P., Alvarez, I., Condon, S., Raso, J., 2005. Membrane
damage and microbial inactivation by chlorine in the absence and
presence of a chlorine-demanding substrate. Applied and
environmental microbiology, 71(9), 5022-5028.
Würtele, M.A., Kolbe, T., Lipsz, M., Külberg, A., Weyers, M., Kneissl, M.,
Jekel, M., 2011. Application of GaN-based ultraviolet-c light
emitting diodes–UV LEDs–for water disinfection. Water research
45(3), 1481-1489.
Zansky, S., Wallace, B., Schoonmaker-Bopp, D., Smith, P., Ramsey, F.,
Painter, J., 2002. Outbreak of multidrug-resistant Salmonella
Newport — United States, January–April 2002 (Reprinted from
MMWR, vol 51, pg 545–548, 2002). Jama–Journal of the American
Medical Association 288 (8), 951–953.
58
VI. 문초록
식품 살균 한 UV 사는 2000 미 FDA 에 해 승
았다. 지 지 UV 처리에는 253.7 nm
지닌 압 UV 램프가 사 고 다. 하지만 러한 램프 타
수 누 가능 , 짧 수 과 낮 에 지 효 문 를 갖고
UV 수 램프에 한 안 , DUV-LED 는 살균
야에 큰 심 고 다. 본 연 에 는 DUV-LED
본 특 악하고 고체 지에 뿐만 아니라 물에
UV-C 사 식 독 병원균 감화 효과를 확 하 다.
Escherichia coli O157:H7, Salmonella Typhimurium 과 Listeria
monocytogenes 균 혼합한 cocktail 각각 택 지에
도말하거나 처리 는 수 처리 샘플에 하 다. 연 결과,
도가 가함에 라 LED 는 큰 변화가 없는 , LP
램프는 약 30 °C 지 가 가한 후 다시 감 하는 경향
보 다. UV 사량 1.67 mJ/cm2 지 가할수 , 균
5 log CFU/ml 수 감 를 보 다. 처리 도가 가할
경우 Escherichia coli O157: H7 Salmonella Typhimurium
감화는 가 (P < 0.05) 하 나 Listeria
59
monocytogenes 는 감화 양상 보 지 않았다 (P >
0.05). 90% 상 습도 건에 E. coli O157: H7 만 30%,
60% 처리 환경과 비 하여 (P < 0.05) 감화 효과를
보 다. 3 mJ/cm2 UV 처리량 경우 10ml 수 처리에 는 든
병원균 검 한계 (1.0log CFU/g) 하 감화하 ,
스케 업 스트에 는 2, 3L 각각 처리 량에 균
5.38, 4.37 log CFU/ml 감 었고, 1L 처리량에 만 검
한계 하 감 하 다. 연 식 수 처리 시스 에 는
사량과 감화 효과 형 상 계를 나타내었다. 러한
결과를 통해 현재 개 단계에 는 DUV-LED 가 다양한
지니고 병원 균 감화하는 효과를
지니고 므 LP 램프를 체할 차 안 술
확 었 보여 다.
주 어: DUV-LED, 사, 식 독 균, 표 살균 수 처리,
친환경 술
학 : 2013-21176