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USE OF ULTRAVIOLET LIGHT FOR THE INACTIVATION OF LISTERIA MONOCYTOGENES AND LACTIC ACID BACTERIA SPECIES IN RECYCLED CHILL BRINES Karol Marie Gailunas Thesis submitted to the Faculty of the Virginia Polytechnic Institute and State University In partial fulfillment of the requirements for the degree of Master of Science in Food Science and Technology Susan S. Sumner, Chair Christine Z. Alvarado Robert C. Williams June 30, 2003 Blacksburg, VA Key words: Listeria monocytogenes, lactic acid bacteria, ultraviolet light, brines Copyright 2003, Karol M. Gailunas
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USE OF ULTRAVIOLET LIGHT FOR THE INACTIVATION OF LISTERIA MONOCYTOGENES AND LACTIC ACID BACTERIA

SPECIES IN RECYCLED CHILL BRINES

Karol Marie Gailunas

Thesis submitted to the Faculty of the Virginia Polytechnic Institute and State University

In partial fulfillment of the requirements for the degree of

Master of Science in

Food Science and Technology

Susan S. Sumner, Chair Christine Z. Alvarado Robert C. Williams

June 30, 2003 Blacksburg, VA

Key words: Listeria monocytogenes, lactic acid bacteria, ultraviolet light, brines

Copyright 2003, Karol M. Gailunas

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USE OF ULTRAVIOLET LIGHT FOR THE INACTIVATION OF LISTERIA MONOCYTOGENES AND LACTIC ACID BACTERIA SPECIES IN

RECYCLED CHILL BRINES

Karol M. Gailunas

(ABSTRACT)

Ready-to-eat meat products have been implicated in several foodborne listeriosis

outbreaks. Microbial contamination of these products can occur after the product has

been thermally processed and is being rapidly chilled using salt brines. The objective of

this study was to determine the effect of ultraviolet irradiation on the inactivation of

Listeria monocytogenes and lactic acid bacteria in a model brine chiller system. Two

concentrations of brines (7.9%w/w or 13.2%w/w) were inoculated with a ~6.0 log10

CFU/ml cocktail of L. monocytogenes or lactic acid bacteria and passed through the

ultraviolet (UV) treatment system for 60 minutes. Three replications of each bacteria and

brine combination were performed and resulted in at least a 4.5 log reduction in microbial

numbers in all treated brines after exposure to ultraviolet light. Bacterial populations

were significantly reduced after five minutes exposure to UV light in the model brine

chiller as compared to the control, which received no UV light exposure (P<0.05). The

maximum rate of inactivation for both microorganisms in treated brines occurred

between minute 1 and 15 of ultraviolet exposure. Overall, results indicate that inline

treatment of chill brines with ultraviolet light (UVC) shows promise in inactivating L.

monocytogenes and lactic acid bacteria. Due to the low capital involved in initiating a

continuous inline UV system, the use of ultraviolet energy may prove to be beneficial for

effectively controlling pathogens in recycled chill brines without interrupting the chilling

operation. An inline ultraviolet system could be used in a hazard analysis and critical

control points plan.

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ACKNOWLEDGEMENTS I would first like to thank my graduate advisor Dr. Susan Sumner for all of the guidance

and direction she has given me throughout these past two years. She has been a mentor,

teacher and a friend and she believed in me even when I didn�t believe in myself. I feel

honored to have had this opportunity to work with her. I would also like to thank my

committee members, Dr. Christine Alvarado and Dr. Robert Williams, for always having

an open door for answering my questions and offering ideas. Additionally, I�d like to

thank Dave Jones and Wafa Birbari at the Sara Lee Corporation for an endless amount of

input and thoughts that helped give life to this project.

I would also like to thank my fiancé and best friend, Brent Quinn for being a hand to hold

and a source of never-ending encouragement. He has been a foundation of strength for

me during two difficult years apart from each other. I am very grateful for his sense of

humor in which he has always been able to make me laugh, even when I thought I�d

never be done with school. Thank you for always being there for me.

I�d like to offer a very special thank you to my family for their love and support including

my parents Charles and Barbara Gailunas and siblings, Kate, Lynn, Sarah, Ali and

Charlie. You have each helped and guided me through this in your own way. I am so

lucky to have such amazing people in my life. Thank you to the one friend who�s known

me the longest, Liz Flaherty. Thank you for being such a beautiful person, always

lending an ear when I needed to talk, a shoulder when I needed to cry, and a smile when I

needed a friend.

I’d also like to thank Daniel Schu and Bridget Meadows for the many hours spent helping

me in the cooler and in the lab. I would also like to thank the very knowledgeable and

cooperative departmental staff that is always available. Specifically I�d like to thank Wes

Shilling, Brian Yaun, Walter Hartman, and Brian Smith.

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Finally I would like to thank all the graduate students in the department for creating a fun

environment to work in. I would especially like to thank Emily Hodson, for the good

times, always taking a break with me, and the great friendship that we have built. These

two years in school have developed into a lifelong friendship. Also, thanks to Renee

Raiden, Valerie Gorsuch, Christine Piotrowski, Angie Hartman, Gabe Sanglay, Lindsay

Millard, Michael Bazaco, and Megan Hereford for being friends as well as officemates.

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TABLE OF CONTENTS

ACKNOWLEDGEMENTS iii

TABLE OF CONTENTS v

LIST OF TABLES vii

LIST OF FIGURES viii

INTRODUCTION 1

REVIEW OF LITERATURE 4 A. Listeria monocytogenes 4

1. Characteristics 4 2. Illness 4 3. Foodborne outbreaks 5 4. Factors affecting growth and survival 6

a. Temperature 6 b. Salt Concentration 7 c. Water Activity 8 d. pH 9 e. Microbial competition 10

B. Lactic Acid Bacteria 12 1. Characteristics 12 2. Shelf-life and spoilage 13 3. Carnobacterium gallinarum 14 4. Enterococcus faecalis 15 5. Lactobacillus plantarum 16

C. Recycled Chill Brines 17 1. General 17 2. Survival of L. monocytogenes in brine 18

D. Ultraviolet radiation 19 1. General 19 2. Susceptibility of microorganisms 19 3. Efficacy and application of UV 20 4. Applications 20 5. Ultraviolet inactivation of L. monocytogenes 21

E. Conclusions 22

REFERENCES 24

USE OF ULTRAVIOLET LIGHT FOR THE INACTIVATION OF LISTERIA MONOCYTOGENES AND LACTIC ACID BACTERIA SPECIES IN RECYCLED CHILL BRINES 33

INTRODUCTION 34

MATERIALS AND METHODS 36 A. Brine preparation 36

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B. Inoculum preparation 36 1. Listeria monocytogenes 36 2. Lactic Acid Bacteria 37

C. Survival Studies 38 D. Ultraviolet Treatment System 38 E. Microbial analysis 39

1. Listeria monocytogenes 40 2. Lactic Acid Bacteria 40

F. Statistical analysis 41

RESULTS AND DISSCUSSION 42

CONCLUSIONS 47

REFERENCES 57

AREAS FOR FURTHER RESEARCH 59

APPENDIX I 60

APPENDIX II 61

APPENDIX III 62

VITAE 63

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LIST OF TABLES REVIEW OF LITERATURE

Table 1: USDA regulations for recycled chill brines, pg. 18

RESULTS AND DISCUSSION

Table 1: Bacterial populations of L. monocytogenes (LM) plated on Modified Oxford Agar (MOX), pg. 48

Table 2: Bacterial populations of L. monocytogenes (LM) plated

on Tryptic Soy Agar supplemented with 0.6% Yeast Extract (TSAYE), pg. 49

Table 3: Bacterial populations of lactic acid bacteria (LAB) plated

on All Purpose Tween Agar supplemented with 0.0032%w/v bromcresol purple dye (APT+BCP), pg. 50

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LIST OF FIGURES Figure 1: Mean microbial populations of brine inoculated with a six-strain

mixture of Listeria monocytogenes plated on Modified Oxford Agar (MOX) after 1 hour in UV Treatment System, pg. 51

Figure 2: Mean microbial populations of brine inoculated with a six-strain

mixture of Listeria monocytogenes plated on Tryptic Soy Agar (TSA) supplemented with 0.6% Yeast Extract (YE) after 1 hour in UV Treatment System, pg. 52

Figure 3: Mean microbial populations of brine inoculated with a three-strain

mixture of lactic acid bacteria plated on All Purpose Tween (APT) Agar supplemented with 0.0032% (w/v) bromcresol purple dye (BCP) after 1 hour in UV Treatment System, pg. 53

Figure 4: Mean microbial populations of brine and tap water inoculated with a six-

strain mixture of Listeria monocytogenes stored at 4°C over a 6 day period, pg. 54

Figure 5: Mean microbial populations of brine and tap water inoculated with a six-

strain mixture of Listeria monocytogenes stored at 25°C over a 6 day period, pg. 55

Figure 6: Mean microbial populations of brine and tap water inoculated with a six-

strain mixture of Listeria monocytogenes stored at 32°C over a 6 day period, pg. 56

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INTRODUCTION

Listeria monocytogenes is a pathogen that poses a serious threat to public health.

A major cause of human listeriosis is due to consumer exposure to L. monocytogenes

from ready-to-eat meat products such as frankfurters and foods purchased at a deli

counter. The food industry in the United Sates is currently under a �zero tolerance�

policy for L. monocytogenes in ready-to-eat foods by both United States Department of

Agriculture (USDA) Food Safety Inspection Service (FSIS) and the Food and Drug

Administration (FDA) Center for Food Safety and Applied Nutrition (CFSAN), because

the infective dose is unknown. Reduction in illness has eluded industry�s food safety

efforts because L. monocytogenes is commonly found in the environment and is more

resistant then most bacteria to conditions and treatments used to control foodborne

pathogens. The organism�s optimum growth temperature is 30-37°C; however, it is

known to grow at temperatures as low as 1°C and as high as 45°C (49). The ability of L.

monocytogenes to grow at refrigeration temperatures, while competing organisms cannot,

offers a competitive advantage for the microorganism. The growth of the organism on

refrigerated, ready-to-eat food products causes a serious potential food safety hazard.

Although L. monocytogenes can be destroyed if heated to a high enough temperature,

there may be contamination of the food product after it has been thermally processed

(93). Ready-to-eat meat products that have received heat treatment followed by cooling

in brine before packaging may supply a more favorable environment for multiplication of

L. monocytogenes because of the decrease in competitive microflora and the high salt

tolerance of the organism (85). Due to the risk of cross-contamination, post-processing

treatments are needed to inhibit growth of L. monocytogenes on ready-to-eat food

products, such as frankfurters.

Frankfurters have been linked recently to several outbreaks, and sometimes

frankfurters are eaten without reheating to a sufficient temperature (20). Additionally,

due to the ubiquitous nature of L. monocytogenes, there are many possible modes of entry

in processing facilities. Entry of L. monocytogenes into food processing plants occurs

through soil on worker�s shoes and clothing and on transport equipment, animals which

excrete the bacterium, raw foods or animal origin, and possibly healthy human carriers.

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Once on frankfurters, the frankfurters provide an adequate pH, water activity (aw), and

nutrients for growth of the organism. A study by Samelis and Metaxopoulos (76)

determined the major sources and routes of contamination of Listeria spp. in a meat

processing plant. Listeria monocytogenes and other Listeria spp. were isolated from 51%

and 49% of samples of frozen raw meat taken from several incoming lots. As a

consequence, listeriae colonized certain processing sites where raw materials were

handled and hygienic conditions were not strictly followed. Tumbled meats were

contaminated heavily during tumbling as the need to operate tumblers continuously did

not enable their proper cleaning and disinfection. Also the use of mechanically deboned

turkey-neck meat in cooked sausages raised contamination at a pre-cooking stage (76).

Another source of contamination on frankfurters by L. monocytogenes occurs through

post process contamination during the cooling step when the frankfurters are sprayed

with salt brines before packaging (62).

Recycled brine is frequently used in food processing plants to cool thermally

processed products. The rapid cooling of the product minimizes the chance that the

product will be exposed to temperatures that permit bacterial growth. This offers some

microbiological safety by decreasing the growth of pathogenic organisms that may

endure the thermal processing. Also, this helps assure adequate shelf life of the product

by preventing the growth of spoilage microorganisms. However, heat and nutrients from

the product often infuse the brine allowing bacteria such as L. monocytogenes and lactic

acid bacteria to survive, grow and spread in these recycled chilling brines. Consequently,

it is also critical to maintain the microbial safety of the cooling brines, especially when

the brine is recycled. Bacterial contamination of these brines has been directly linked to

the outbreaks of listeriosis from commercial ready-to-eat foods. The addition of one or

several steps prior to packaging could help to minimize growth of L. monocytogenes in

ready-to-eat food products.

Ultraviolet (UV) light has been utilized for the control of microbial contamination

in some areas of the food industry because of its bacteriocidal effects. Ultraviolet

radiation emitted between wavelengths of 220-300 nanometers is considered to have a

germicidal effect on bacteria, molds, yeasts and viruses (65). The most microbiologically

damaging wavelength range of ultraviolet radiation is between 240 and 280 nanometers.

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Gram-negative bacteria are most easily killed by UV, while Gram-positive bacteria,

spores and molds are much more resistant. The germicidal properties of UV radiation are

mainly due to DNA mutations induced through absorption of UV light by the nucleic

acids on the DNA strand of the microorganism. The cross-linking of thymine dimers on

the DNA strand prevents repair and reproduction (35).

The Food and Drug Administration has approved UV treatments for pathogen

reduction in water. The use of UV is a promising bactericidal alternative for other

applications because it does not undesirably affect the color, flavor, odor, or taste of the

product (92). Also, UV radiation does not produce undesirable by-products and is

effective against a wide variety of microorganisms (27). The objective of this research

was to use ultraviolet irradiation within a model brine chiller system to inactivate L.

monocytogenes and lactic acid bacteria species. In using UV irradiation to reduce the

bacterial load in recycled chilling brines, the safety of these ready-to-eat meat products

will be improved due to the decreased risk of foodborne listeriosis. Also, the shelf life of

the product will be increased by the reduction of spoilage lactic acid bacteria.

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REVIEW OF LITERATURE A. Listeria monocytogenes

1. Characteristics

Listeria monocytogenes is a well-known foodborne pathogen that is

ubiquitous in nature. It is commonly found in water and soil, but has also been

isolated from a number of domestic and wild animals. Listeria monocytogenes

has been found in raw foods, such as uncooked meats, vegetables, fruits, and

dairy products made from unpasteurized milk (25). More importantly, L.

monocytogenes has been associated with processed foods, most commonly ready-

to-eat (RTE) meat products, such as frankfurters or deli meats. Listeria

monocytogenes is a short (0.5µm in diameter by 1 to 2µm long) Gram-positive,

non-sporeforming rod that is a part of the lactobacilli family. It has tumbling end-

over-end motility at room temperature (13). It is catalase positive, oxidase

negative, and has slight β-hemolysis on blood agar. Although it has optimum

growth at ~32°C, it can survive and multiply at refrigeration temperature. Listeria

monocytogenes has also been known to survive freezing and drying, which

provides difficulties for the food industry (25).

2. Illness

In the United States, approximately 2,500 individuals become seriously ill

with listeriosis each year, and approximately 500 of those people die (21).

Although L. monocytogenes is generally known to cause severe illness, there have

been outbreaks in which the majority of the patients only developed mild

symptoms, as the bacteria generally do not affect healthy adults or children (25).

The infective dose of L. monocytogenes is unknown. However it is assumed that

less than 1,000 total organisms could cause infection depending on susceptibility

of the victim (36). Listeria monocytogenes is of major concern for several high-

risk subpopulations, such as the elderly, the perinatal, and those who are

immunocompromised (25). Approximately 12 hours after ingestion of the

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contaminated food, those inflicted exhibit mild influenza-like symptoms including

fever, headache, nausea, vomiting, and diarrhea (36). Healthy adults and children

rarely become seriously ill. However, in the high-risk subpopulations, the mild

symptoms are often followed a few days to a few weeks later by more serious

complications. These can include meningitis, encephalitis, septicemia, and

intrauterine/cervical infections that may result in stillbirth or miscarriage in

pregnant women (25).

3. Foodborne Outbreaks

Pasteurization and heating methods used during the preparation of ready-

to-eat food products will kill L. monocytogenes. However, post-process

contamination occurs because the microorganism can readily adapt to and live in

food processing environments. Most cases of listeriosis occur as sporadic

incidents; however there have been many significant outbreaks of the illness.

Most recently, in October of 2002 an outbreak involving eight Northeastern states

brought about the largest meat recall in history. Pilgrim�s Pride Foods recalled

27.4 million pounds of cooked deli products produced in a Pennsylvania factory

over a five-month period. This multistate outbreak of L. monocytogenes

infections included 46 culture-confirmed cases, seven deaths and three stillbirths

or miscarriages (23). In November 2000, homemade Mexican Style soft cheese

was reported as the contaminated food source in a listeriosis outbreak involving

12 individuals in North Carolina. In this outbreak, ten of the cases involved

pregnant women and resulted in five stillbirths, three premature deliveries, and

two infected newborns (22). Also that same year, deli turkey and chicken meat

was associated with 29 illnesses due to this organism in 10 states between May

and November (21). In August of 1998, 40 illnesses caused by a single strain of

L. monocytogenes were identified in ten states. This outbreak was linked to high

environmental levels of L. monocytogenes in the production facility where the

contaminated deli meats and frankfurters were processed (20). Mexican style soft

cheese was responsible for at least 86 cases and 29 deaths due to foodborne

listeriosis in Los Angeles and Orange counties in California in 1985 (19).

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4. Factors Affecting Growth and Survival in ready-to-eat meat products

a. Temperature

There are many factors that will affect the growth and survival of

L. monocytogenes in ready-to-eat meat products. Listeria monocytogenes

can survive longer then many other non-spore forming bacteria under

adverse environmental conditions (49). Temperature is one factor that

may help support the growth of L. monocytogenes in meat products.

Listeria monocytogenes is able to grow over a broad temperature range.

Lower and upper limits for growth are approximately 1°C and 45°C,

respectively. The optimum growth temperature for L. monocytogenes is

30�37°C (79). The ability of L. monocytogenes to grow at low

temperatures allows for the possibility of proliferation in refrigerated food

products. This is why it is necessary for strict temperature control to

minimize L. monocytogenes growth. Glass and Doyle (40) found that L.

monocytogenes could survive on several types of processed meat products

that were stored at 4.4°C, including ham, bologna, wieners, sliced chicken

and turkey, and sausages. The growth rate depended largely on the type of

product and proliferation was greatest on processed poultry products.

Another study found that 65.6% of wieners inoculated with L.

monocytogenes supported growth of the pathogen while stored under

vacuum at 5°C for up to 28 days (59).

Temperature will often affect the generation time of bacteria by

slowing down replication. Papageorgiou et al. (70) reported generation

times of L. monocytogenes in whey cheeses at 5°C ranged between 16.2

and 20.2 h and were significantly longer then those observed at 12°C,

which ranged between 5.1 and 5.8 h. Generation times at 22°C ranged

between 1.7 and 2.7 h. Andrews and Grodner (1) reported a similar

generation time of 1.2 h in tryptic soy broth at 20°C.

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Temperatures may fluctuate wildly during storage of a food

product and this can lead to an increased risk of proliferation of

pathogenic bacteria. A study by Bovill et al. (11) examined the growth of

L. monocytogenes during various rates of increase and decrease in

temperature. The group found that growth was not affected by even the

most rapid changes and injury or lag was not observed. However, another

study found that L. monocytogenes that was heat shocked in ground beef

at 46°C for 60 min had elevated D10-values as compared to nonheat-

shocked controls. Refrigeration and frozen storage did not influence the

observed effects (67).

In addition to the ability to grow at refrigeration temperature in

many foods, L. monocytogenes can tolerate and grow in foods with high

salt concentration, as well as in foods with low moisture content, and in

comparatively acidic foods (49).

b. Salt Concentration

Sodium chloride is an important microbial inhibitor that has been

reported as preventing the recovery of stressed L. monocytogenes on solid

agar media at concentrations of 2% (58), 4% (60), 4.5% (28) and 6% (17).

Hudson (46) examined the effectiveness of high sodium chloride

concentrations for the destruction of L. monocytogenes. It was found that

at relatively low NaCl concentrations (6%), L. monocytogenes would grow

at refrigeration temperature. Numbers could be reduced in the presence of

26% NaCl, but not under practical time periods for use in the food

industry. In another study, Peterson et al. (71) used sodium chloride and

packaging methods to control L. monocytogenes in smoked fishery

products. The group found that inhibition related to NaCl concentration

was most apparent at 5°C and the L. monocytogenes populations were held

below 102 CFU/g by 6% NaCl.

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Many studies have been conducted to determine the growth and

survival of L. monocytogenes under multiple constraints. In one such

study, Buchanan et al. (16) studied the effects and interactions of several

factors on the growth of L. monocytogenes including temperature, pH,

atmosphere, sodium nitrite and salt concentration. It was found that

although refrigeration was the primary factor in controlling the rate of

growth, NaCl also had an effect on growth. The combined bacteriostatic

effects that were most effective proved to be a combination of pH 6.0,

4.5% NaCl, 5ºC incubation, and anaerobic conditions (cultures flushed

with sterile N2 for 10 minutes and sealed with screw caps). It has also

been found that the combined effect of salt concentration (2 to 3.5%) and

low temperature (10°C) seem to play a protective role, allowing L.

monocytogenes to better survive exposure to nisin, a bacteriocin (33).

Bal�a and Marshall (3) found that L. monocytogenes tolerance to NaCl was

greatest (>78 g/liter) at neutral pH (6.8 to 7.2) and increased in the pH

range 7.0 to 5.4 as the incubation temperature was lowered to 5°C.

c. Water Activity

Another factor allowing for the growth and survival of L.

monocytogenes is the ability of the organism to multiply at an unusually

low water activity (aw). It is reported that the type of solute as well as the

osmotic conditions created by the solute effect the ability of L.

monocytogenes to grow. Tapia de Daza et al. (86) observed aw minima for

strains Scott A and Brie 1. Both strains grew well at 30°C in glycerol-

supplemented TSB, but not in NaCl- and sucrose-supplemented TSB at aw

0.90. The effects of all three solutes were magnified at 4°C. In a separate

study, Petran and Zottolla (72) were able to grow L. monocytogenes in a

39.4% sucrose solution with a water activity of 0.92. A few years later

these findings were duplicated by Farber et al. (34) reporting that the

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minimum aw that permitted growth of the L. monocytogenes was 0.92 in a

TSB base with sucrose as the humectant.

Miller (61) reported that survival of L. monocytogenes is related to

the aw level, as well as the solute employed. He used brain heart infusion

(BHI) broth adjusted to water activity levels of 0.99-0.80 with glycerol,

NaCl, or propylene glycol and found minimum aw levels for growth

occurred at 0.90, 0.92, and 0.97, respectively. The use of NaCl in this

study was examined in greater detail then the other solutes because of its

common use in foods. It was found that when using NaCl as the solute,

growth of L. monocytogenes occurred at water activities of 0.99, 0.97,

0.93, and 0.92. It was also reported that below aw levels of 0.92 the death

rate of L. monocytogenes Scott A was proportional to water activity.

Survival of the organism in NaCl at 28ûC was estimated to range from

200-700 hours, depending on the water activity. Nolan et al. (66) obtained

similar aw minima using tryptic soy broth with 0.6% yeast extract (TSB-

YE) containing glycerol and NaCl; in addition the group obtained an aw

minimum of 0.92 using sucrose.

Chen and Shelef (29) used a model meat system to show the

relationship of several factors including water activity on the growth of L.

monocytogenes. The pair reported inhibition of strain Scott A in cooked

strained beef having an aw of 0.93, a moisture content of 25%, and no

added solutes. As mentioned earlier, L. monocytogenes is known for its

ability to survive in many environments in which other pathogens cannot.

As shown by the finding in these studies, it can be concluded that L.

monocytogenes is a serious threat as a foodborne pathogen because is it

able to grow at aw values <0.93 (49).

d. pH

In addition to salt concentration and water activity, pH also affects

the growth and survival of L. monocytogenes. The organism has been

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shown to grow over a wide pH range. The optimum pH range for L.

monocytogenes growth is 6.0�8.0. However, growth of L. monocytogenes

is possible in pH ranges from 4.1-9.6 (49). Parish and Higgins (69)

examined the survival of several L. monocytogenes strains in pH adjusted

TSB with yeast extract (TSB+YE). Growth was observed in the TSB+YE

at pH 4.5 and higher for all strains during incubation at 30ºC and growth

did not occur at pH 4.0 or lower. It has been found that the minimum pH

supporting the growth of L. monocytogenes is dependent upon the

temperature of incubation, nutrients available, moisture content, and the

composition of the food product (49). Bal�a and Marshall (3) studied the

combined effects of pH and salt on the survival of L. monocytogenes using

double-gradient plates. The pH gradient across the plates ranged from 5.4

to 7.8 and the salt gradient ranged from 25 to 78 g/liter. The plates were

incubated at 5, 15, 25, or 35ºC. The largest area of growth inhibition was

observed on the salt-pH gradient plates incubated at 25ºC. At all

incubation temperatures, peak salt tolerance occurred around neutral pH.

It was found that L. monocytogenes was able to tolerate higher salt

concentrations and a lower pH as the incubation temperature was lowered.

The pH range for meat products ranges from 5.1�6.4, depending on the

animal of origin and how the meat is processed (49). Since the pH range

of meat products falls within the range of growth for L. monocytogenes,

contamination of ready-to-eat meat products is a concern.

e. Microbial Competition

As a psychrotrophic pathogen, L. monocytogenes can often be

isolated at low levels from a range of foods, but is rarely present at

elevated numbers. The growth and survival of L. monocytogenes is also

impacted by the growth of competing microorganisms (15). These

organisms compete for available nutrients and consequently have an effect

on product safety and stability through storage (55). The Pseudomonas

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spp. are an example of psychrotrophic, Gram-negative spoilage organisms

that are likely to be found in contaminated meat products stored

aerobically. Buchanan and Bagi (15) found the suppression of L.

monocytogenes by P. fluorescens was generally associated with low

incubation temperatures (4°C) and sodium chloride levels (5 and 25 g/l)

while slight increases of the maximum population density (<1.0 log

cfu/ml) were observed when L. monocytogenes was grown in the presence

of P. fluroescens at higher temperatures (12 and 19°C) and sodium

chloride levels (25 and 45 g/l).

However, when the growth of these Gram-negative organisms is

suppressed, there may be an increase in the proliferation of lactic acid

bacteria such as the lactobacilli, pediococci, leuconostocs, and

streptococci (12). These lactic acid bacteria also compete with L.

monocytogenes in refrigerated, ready-to-eat meat products, often hindering

listerial growth through the production of both lactic acid and bacteriocins.

The antimicrobial activity of lactic acid is related to pH, and the

undissociated form of the acid. In the undissociated form, the lactic acid

can penetrate the cell membrane more easily. Once inside the cell, the

acid dissociates because the cell interior has a higher pH then the exterior.

Protons generated from intracellular dissociation of the lactic acid must be

removed from the cell, using energy in the form of ATP. The constant

entry of these protons will eventually deplete cellular energy and lead to

cellular death (32). Bacteriocins are agents (commonly proteins) encoded

in the genetic material carried on plasmids, produced for the purpose of

inhibiting or killing closely related species, or even different strains of the

same species (64).

In a separate study, Buchanan and Bagi (14) found that the growth

of L. monocytogenes was suppressed when grown in the presence of two

strains of Carnobacterium piscicola. Juven et al. (50) reported inhibition

of L. monocytogenes in vacuum-packaged ground beef stored at 4°C using

a lactic acid producing strain (FloraCarn L-2) of Lactobacillus

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alimentarius. Berry et al. (7) observed a 2 log10 CFU/g reduction of L

.monocytogenes by a bacteriocin-producing Pediococcus in fermented

semidry sausage.

B. Lactic Acid Bacteria

1. Characteristics

The lactic acid bacteria (LAB) consist of a number of genera including

Carnobacterium, Enterococcus, Lactococcus, Lactobacillus, Lactosphaera,

Leuconostoc, Oenococcus, Pediococcus, Streptococcus, Tetragenococcus,

Vagococcus, and Weissella (47). Carr et al. (18) defined the LAB as �Gram-

positive, aerobic to facultatively anaerobic, asporogenous rods and cocci which

are oxidase, catalase, and benzidine negative, lack cytochromes, do not reduce

nitrates to nitrite, are gelatinase negative, and are unable to utilize lactate.�

Although the lactic acid bacteria group is composed of a number of separate

genera, they are classified as either homofermenters or heterofermenters. The

differences between these two groups are the major end products after the bacteria

ferment glucose. The homofermenters produce lactic acid as a major product of

the fermentation, where the heterofermenters produce several other products

besides lactic acid, including carbon dioxide, acetic acid, and ethanol (74).

The LAB are often used beneficially in food products. The LAB are hardy

microorganisms and are often able to survive the stressors provided by the

environment of the food product. They can be used as starter cultures in

fermented foods or as preservatives by exploiting their ability to product

bacteriocins (74). In a study sampling retail food products, Garver and Muriana

(39) found by direct plating, bacteriocin-positive LAB were detected at levels up

to 2.4 × 105 CFU/g in ready-to-eat meats. Of those identified the homofermentive

Lactobacillus curvatus (four strains) and Lactococcus lactis (nine strains) were

the only isolates inhibitory to foodborne pathogens including L. monocytogenes.

However, because LAB are able to grow anaerobically, at low

temperatures, and high salt concentrations these organisms can also survive and

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grow on food products and lead to spoilage and decreased shelf life. Some LAB

have been found to be responsible for souring, slime formation, and off-color and

off-flavor production in meat products (41). Samelis et al. (77) found that both

the growth rate and the composition of spoilage LAB during refrigerated (4°C)

storage of cooked, cured meats, sharing their processing plant environment, day

of production and film packaging conditions were dependent on the product type

and manufacturing method. Apart from the effect of pH, moisture, salt (brine) or

sugar content, the cooking method strongly affected the LAB, as their growth was

more delayed in smoked meats than in steam-cooked meats.

2. Shelf life and spoilage

The shelf life of meat and meat products is determined by the amount

of time the product can be stored until spoilage occurs. The meat is

considered spoiled when a maximum acceptable bacterial level is reached or

an unacceptable off-odor or off-flavor and/or undesirable appearance occurs

(10). However, even if high bacterial numbers are reached there may not be

apparent spoilage of the product. For example, in a study by Susiluoto et al.

(84) found that the average CFU/g of 32 packages of marinated broiler meat

products at the end of the producer-defined shelf life was found to be 2.3x108

on Plate Count Agar (PCA). Despite high bacterial counts, radical spoilage

changes such as unpleasant odor, slime production and formation of gas were

not seen.

The various forms of microbiological spoilage are preventable to a

large degree by a wide range of preservation techniques, most of which act by

preventing or inhibiting microbial growth, such as chilling, freezing, drying,

curing, packaging, and adding preservatives (42). Since ready-to-eat meat

products are heat processed to high temperatures, most vegetative cells are

destroyed and it is post-process contamination that strongly influences the

shelf life of the product (10).

Throughout storage, environmental aspects such as temperature,

atmosphere, pH and salt content will select for specific microorganisms, and

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influence their growth rate and activity. Thus allowing for a varied shelf life

for refrigerated meat and meat products, lasting from only a few days to

several months (10). The shelf life of some meat products is also determined

by intrinsic factors of the meat. Blixt et al. (9) found high correlations

between initial values of pH, fat and L-lactate, respectively, and the rate of

spoilage. However, no relationship was found between spoilage and the

origin of the meat (pork or beef).

3. Carnobacterium gallinarum

Previously known as �atypical meat lactics� several lactic acid bacteria

have been installed in a new genus, Carnobacterium. This reclassification

was due to DNA homology and physiological studies and includes organisms

such as Lactobacillus divergens, Lactobacillus piscicola, and a few other rod-

shaped psychrophilic microorganisms (31). Carnobacterium gallinarum is a

Gram-positive, nonsporeforming, short, stubby rod often found in pairs or

short chains. It has no motility at 25°C, is catalase negative and shows no

hemolysis on blood agar (55). The organism has the ability to grow at 0°C,

but not at 45°C and is inhibited by acetate and by pH <6.0 with an optimal pH

in the range of 8.0 to 9.0 (18).

The Carnobacteria have been largely associated with meat spoilage,

predominantly poultry. Researchers have also isolated these microorganisms

from chilled, vacuum-packaged, unprocessed beef, lamb, and pork (18). In a

study by Hansen and Huss (43) three Carnobacterium spp. produced spoilage

off-odors in spoiled cold-smoked salmon, resulting in 9% of the LAB isolates

being identified as Carnobacterium spp. This is in contrast to other

screenings of cold-smoked salmon in which the Carnobacteria played a much

more dominate role in the spoilage of those products. Paludan-Müller et al.

(68) found the LAB microflora was dominated by Carnobacterium piscicola,

which was found to account for 87% of the 255 LAB isolates from cold-

smoked salmon stored at 5°C. Similarly, Leroi et al. (56) found

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Carnobacterium piscicola to be widely represented (97/155 LAB isolates) on

cold-smoked salmon stored at 8°C.

In addition to causing spoilage problems in cold stored seafood,

Carnobacterium spp. are often associated with the spoilage of refrigerated

meat products. Barakat et al. (4) found the Carnobacteria to be one of the

most prevailing isolates (71/203 LAB isolates) from cooked, modified

atmosphere packaged, refrigerated, poultry meat.

4. Enterococcus faecalis

Bacteria in the genus Enterococcus have been recognized since the late

1800�s, when they were describes as the �entérocoque� to give emphasis to

their intestinal origin (81). Carr et al. (18) defined the enterococci as �Gram-

positive, facultative anaerobic cocci with growth at 10°C and 45°C, growth in

broth with 6.5% NaCl, growth at pH 9.6 and reduction of 0.1% Methylene

Blue Milk Medium.� The Enterococci generate lactic acid

homofermentatively from glucose and also gain energy from the break down

of amino acids. As a normal inhabitant of the human intestinal tract, the

Enterococci, usually Enterococcus faecalis, have been associated with urinary

tract infections, bacteremia, bacterial endocarditis, and nosocomial infections

(81).

There is an elevated likelihood for contamination of meat at the point

of slaughter due to the existence of enterococci in the gastrointestinal tract of

animals. Stiles et al. (80) completed a study of enterococci from raw meat

products and found E. faecalis was the major isolate from both beef and pork

cuts. The group also found another enterococci, E. faecium, was frequently

isolated from bologna. In a study of three hog slaughtering plants, Knudtson

and Hartman (52) found mean populations of 4 log10 and 8 log10 enterococci

per 100 cm2 of carcass surface at various stages in the slaughtering process,

indicating that microbial contamination of meat products can occur at any

point between slaughter and processing. Enterococcus faecalis (79%) was the

most abundant Enterococcus spp isolated.

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Enterococci are among the most thermotolerant of the non-sporulating

bacteria and this often leads to spoilage problems in cooked, processed meats.

Processed meats are usually salted or cured and can be either raw or cooked

(38). After surviving heat treatment, both E. faecalis and E. faecium have

been implicated in spoilage of cured meat products (5, 6).

5. Lactobacillus plantarum

In the genus Lactobacillus, there is a classic division based on

fermentative characteristics: (1) obligately homofermentative; (2) facultatively

heterofermentative; and (3) obligately heterofermentative. Several species of

groups 1 and 2 and some from group 3 are used in fermented foods. But the

lactobacilli in group 3 are also commonly associated with food spoilage.

Lactobacillus plantarum falls into group 2 because of its use as a starter

culture for some fermented sausages and cereal products. However, it has

been known to cause spoilage problems in some food products (81).

Lactobacillus plantarum is a Gram-positive, non-sporulating short rod.

It is often found singly or in pairs, but can also form small chains with short

round ends (55). Lactobacillus plantarum is considered a psychrophilic

microorganism because it can grow at temperatures of 2°C to 8°C, although

they grow very slowly at these temperatures (18). This organism is a member

of a large group of organisms known as the Streptobacteria. The

Streptobacteria are found in nature connected with a variety of plants and

dairy products. Lactobacillus plantarum has been associated with both types

of products, including cabbage and cheese. Typical Streptobacteria, such as

L. plantarum, ferment both lactose and maltose, but differ from Atypical

Streptobacteria by also fermenting mannitol (18).

Although Lactobacillus spp. are naturally occurring in some food

products, they are also an important cause of spoilage in the meat industry. In

one study, Samelis et al. (78) determined that Lactobacillus sakei was the

most prevalent species in the spoilage microflora of sliced, vacuum-packed,

smoked, oven-cooked turkey breast fillets which developed slight, sour

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spoilage flavors after 4 weeks storage at 4°C. In an experiment to determine

the influence of packing atmosphere on the microbial spoilage pattern of

ground beef, it was found that of the Gram-positive isolates, the lactobacilli

predominated at 45% of isolates. The researchers found significant numbers

of lactobacilli from samples in all treatment groups, including the aerobically

packed categories (88).

The Lactobacillus spp. are fairly heat sensitive organisms. Franz and

von Holy (37) found a one-log reduction in numbers on vienna sausages was

achieved at 57°C in less then 60 seconds. In their experiment, the researchers

determined D-values at 57, 60 and 63°C for Lactobacillus sake were 52.9,

39.3 and 32.5 seconds, respectively, and for Lactobacillus curvatus D-values

were 22.5, 15.6, and 14.4 seconds, respectively, in vacuum packaged vienna

sausages.

C. Recycled Chill Brines

1. General

Thermally processed foods are often cooled using recycled brine in

order to rapidly remove heat that could expose the product to temperatures

that allow for bacterial growth. This cooling is done in order to increase shelf

life by decreasing growth of spoilage microorganisms and it also aids in food

safety by decreasing the growth of pathogenic organisms that may have

contaminated the product. However, the heat and nutrients from the product

often infuse the brine, leaving the brine as a potential habitat for these

microorganisms. In addition to this, these brines are often recycled, which

could lead to contamination of the thermally processed food while it is being

cooled (62).

USDA regulations state that brine may be reused to chill cooked

product for various lengths of time based on salinity and temperature. The

solution maintenance requirements for recycling the brines are shown below.

The provisions range from recycling the brines for one production shift with

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no temperature or sodium chloride controls, to reuse up to 4 weeks, requiring

maintaining 20% NaCl and a maximum temperature of �12.2°C (87).

Table 1: USDA regulations for recycled chill brines (USDA, 2000) Solution maintenance conditions

Duration of use Minimum salt Maximum Concentration (%) temperature

One production shift None Undefined

Up to 24 hours 5 40°F (4.4°C)

Up to 1 week 9 28°F (-2.2°C)

Up to 4 weeks 20 10°F (-12.2°C)

2. Survival of L. monocytogenes in Recycled Chill Brines

Contamination of L. monocytogenes in recycled chill brines is of great

concern to the food industry. Many studies have been completed investigating the

survival of L. monocytogenes in brines. Larson et al. (54) obtained commercial

cheese brines from factories and inoculated them with L. monocytogenes.

Survival of the pathogen ranged from <7 days to over 259 days and showed no

proliferation. In addition to just evaluating the survival of L. monocytogenes in

brines, several processes have been explored for their applications for the

inactivation of the organism, such as microfiltration (44), organic acids (73), and

electrochemical treatment (91). In one study, Miller et al. (62) used a model brine

system to evaluate the growth, injury, and survival of L. monocytogenes. The

organism grew at 5ºC in 5% NaCl and at 12ºC in 9% NaCl and there was no

significant injury observed. Bacteriostatic conditions were maintained for the

pathogen at -2ºC and 9% NaCl. However, L. monocytogenes survived for 30 days

at -12ºC in 20% NaCl. In another study using a model brine system, Ye et al. (91)

examined using electrochemical treatment system consisting of a pulsed electrical

power supply and an electrical treatment chamber to inactivate L. monocytogenes

in recirculated brine for chilling processed bacon. The team used both fresh

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brines and used brines (after 20 hours of operation in the plant) at several different

temperatures. The average D-value was 1.61 min for the fresh brines at 7mA/cm3

and 2.5 min at 35 mA/cm3 for the used brines.

D. Ultraviolet (UV) radiation

1. General

One physical method of sterilization of surfaces, equipment, and food

products is the use of ultraviolet energy. This is done by using radiation from the

ultraviolet region of the electromagnetic spectrum for the purpose of disinfection.

Although the UV spectrum includes wavelengths between 100 nm and 400 nm, it

can be subdivided into 4 sections: UVA, UVB, UVC, and the vacuum UV range.

The section of interest is the UVC (200 to 280 nm) due to its antimicrobial

activity. Within this UVC range, the wavelengths around 260 nm are the most

effective in inactivating bacteria and viruses, since at this wavelength DNA

mutations are induced through UVC absorption by the nucleic acids (26).

DNA absorption of the UVC light causes crosslinking between

neighboring pyrimidine bases on the same DNA strand, and thus formation of

hydrogen bonds with the purine bases on the other strand is impaired and DNA

transcription and translation is blocked, leading to cell death (63).

UV inactivation of microoorganisms is mainly dependant on the UV

dosage and not the intensity of the light. The actual dosage in µW·s·cm-2 required

to attain a specific level of microbial inactivation can be expressed as the product

of applied intensity (µW/cm2) and irradiation time (s). It is thus implied that for a

given UV dose at low radiation intensity and long exposure time, the same effect

is achieved with high intensity for a short time (65).

2. Susceptibility of Microorganisms

Generally, the UV dose required to inactivate viruses and molds is much

higher then for bacteria (27, 65). However, resistance of bacteria differs between

the species and also depends on age of the organisms and the presence of spores.

In general, Gram-positive bacteria tend to be more resistant to UV radiation than

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Gram-negative organisms and spore formers are more resistant then non-spore

formers. Vegetative bacteria tend to be most resistant to UV radiation just prior

to active cell division, during the lag phase. It has also been found that a given

dose will become less effective the higher the number of cells. The absence of

oxygen will also increase microbial resistance to UV irradiation (48).

3. Efficiency and Application of UV Radiation

The use of UV for its germicidal properties in food is restricted due to the

fact that UV acts only on the surface, except when the food product is transparent.

Also, the only organisms to be killed will be those that are in the direct radiation

beam. Food products are often not uniform in shape, which could cause shadows

or holes and pores in which the UV light cannot penetrate (2).

UV rays are not capable of penetrating solid foods and have only a limited

ability to penetrate liquids. There are several factors affecting the use of UV

irradiation on liquids. The most critical factor is the transmissivity of the material

being sterilized, as even small amounts of solutes or particulates will attenuate

and scatter UV light, resulting in a lower measure of microbial inactivation. Also

of importance is the thickness of the radiation path through the liquid because

attenuation of the UV light is increased with the length of passage (26).

4. Applications

UV radiation has been used to disinfect drinking water and has shown

effectiveness against a variety of microorganisms (2, 27). It has also been used to

treat air and surfaces in hospitals and laboratories where aseptic facilities are

required (30). UV radiation has also been used for the treatment of packaging

materials for aseptic packaging (35).

A good deal of research has been completed on using direct application of

UV light to food products. Kissinger and Willits (51) were able to reduce

microorganisms in maple sap by 99% using UV energy. It has also been used

effectively on shell eggs (53). Treatment with high intensity UV extended the

shelf life of fresh mackerel fish by 7 days over the untreated fish (45).

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Since UV light cannot penetrate into foods, only microbes on exposed

surfaces are susceptible to its effects. Bacteria on a smooth surface absorb more

UV light than bacteria on a rough surface (82, 89, 90). Consequently, the UV

exposure necessary for destruction of bacteria on meat will most likely exceed

that required for killing cells on laboratory media. Studies have shown that UV

exposure does not have a deleterious effect on the color of meat nor does it cause

oxidative rancidity (82, 89).

The use of ultraviolet radiation to control the growth of pathogens and

spoilage microorganisms while avoiding unfavorable effects on the quality of the

meat has been documented. Stermer et al. (82) reported that UV radiation dose of

150 µW·s·cm-2 reduced bacteria on a smooth surface of fresh meat by 2 log

cycles. In another study, Wong et al. (90) reported the greatest logarithmic

reductions of bacteria on fresh pork muscle was achieved at doses of 100

µW·s·cm-2 for E. coli and 80 µW·s·cm-2 for S. senftenberg where a 1.5- and 2-log

reduction was observed, respectively. Sumner et al. (83) were successful in

almost completely eliminating bacteria on agar plates, with a 99.9% reduction of

S. typhimurium at 2,000 µW·s·cm-2. Reduction of bacteria was less successful on

the surface of poultry skin with an 80.5% reduction of S. typhimurium obtained at

2,000 µW·s·cm-2. Wallner-Pendleton et al. (89) found similar results on broiler

chicken carcasses, with a 61% reduction in viable S. typhimurium observed in

UV-treated chicken halves as compared with untreated halves. The UV dose in

this study ranged from 82,560 to 86,400 µWs/cm2.

5. Ultraviolet inactivation of Listeria monocytogenes

Very little research exists studying the inactivation of L. monocytogenes

by ultraviolet energy. In one study, Yousef and Marth (92) exposed L.

monocytogenes grown on tryptose agar to short-wave UV energy (100 µW/cm2)

for a period of time ranging from 0.5 and 10 minutes. It was shown that the

highest rate of inactivation occurred in the second minute and the rate of death

diminished and essentially leveled off after 4 minutes. Inactivation of 90% of L.

monocytogenes on the plate occurred with the average dose of 3.4 µW·s·cm-2. In

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another study, Bintsis et al. (8) exposed L. innocua (chosen to mimic the behavior

of L. monocytogenes) to long-wave UV energy (~365 nm) in conjunction with

photosensitizing compounds. It was found that in the presence of psoralen at a

concentration of 5 mg1-1, reduction of 99.8% of L. innocua was obtained over 60

seconds.

MacGregor et al. (57) studied the light inactivation of food-related

pathogenic bacteria using a pulsed power source. The group reported that as few

as 64 light pulses of 1 µs duration were required to reduce L. monocytogenes

populations by 99%. Cell populations of Listeria were reduced by 7 log10 orders

at the upper exposure level of 512 µs. In a similar study, Rowan et al. (75) also

examined the effects of high-intensity pulsed-light emissions on the survival of

several bacterial types. The group used both high and low UV content to

inactivate Listeria monocytogenes on the surface of tryptone soya-yeast extract

agar. The results showed that with 200 light pulses of high-UV content, the

microbial populations were reduced by 6 log10 CFU/plate. The levels of

resistance of the different bacteria varied, in which the Gram-positive bacteria

were shown to be more resistant to the effects of UV than the Gram-negative

bacteria.

E. Conclusions

Recent research in food microbiology has focused on non-thermal processing

alternatives for ready-to-eat (RTE) foods. Ultraviolet light treatment is widely

recognized and proven method for pathogen reduction in water. The use of UV is a

promising bactericidal alternative for some other fluid applications in the food industry

because it does not undesirably affect color, flavor, odor or taste, depending on the

product. UV disinfestations are efficient, effective, and economical.

Concentrated brine (salt/water) solutions are commonly used to chill RTE

products. The brine solutions are recirculated and sprayed over warm product until a

certain product temperature is attained, normally ~4°C. It is critical to maintain low

bacterial levels in the brine systems for food safety and food preservation reasons.

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In line treatment of brine with UV to provide the necessary level of disinfection

would be a low cost alternative for decreasing brine bacterial counts. Validation of UV

for brine systems would be beneficial for meat processing and provide a critical control

point for HACCP plans to address pathogen reduction of post thermally processed

product.

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3. Bal�a, M.F.A., and D.L. Marshall. 1996. Use of double-gradient plates to study combined effect of salt, pH, monolaurin, and temperature on Listeria monocytogenes. J. Food Prot. 59(6): 601�607.

4. Barakat, R.K., M.W. Griffiths, and L.J. Harris. 2000. Isolation and

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Use of Ultraviolet Light for the Inactivation of Listeria monocytogenes and

Lactic Acid Bacteria Species in Recycled Chill Brines

Karol M. Gailunas, Susan S. Sumner*, Christine Z. Alvarado, and Robert C. Williams

Department of Food Science and Technology Virginia Polytechnic Institute and State University

Blacksburg, VA

KEYWORDS: Ultraviolet light, Listeria monocytogenes, lactic acid bacteria, brines *Corresponding Author: Mailing address: Department of Food Science and Technology, Virginia Tech, Blacksburg, VA 24061-0418. Phone 540-231-5280 Fax 540-231-9293. Electronic mail address: [email protected]

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INTRODUCTION

The growth of Listeria monocytogenes on refrigerated, ready-to-eat food products

causes a serious potential food safety hazard. Although the organism can be destroyed if

heated to a high enough temperature, there may be contamination of the food product

after it has been thermally processed (23). Ready-to-eat meat products that have received

heat treatment followed by cooling in brine before packaging may supply a favorable

environment for multiplication of L. monocytogenes because of the decrease in

competitive microflora and the high salt tolerance of the organism (17). Due to the risk of

cross-contamination, postprocessing treatments are needed to inactivate L.

monocytogenes on ready-to-eat food products.

Recycled brine is frequently used in food processing plants to cool thermally

processed products. The rapid cooling of the product minimizes the chance that the

product will be exposed to temperatures that permit bacterial growth. This offers

microbiological safety by averting the growth of pathogenic organisms that may endure

the thermal processing. Also, this assures adequate shelf life of the product by

preventing the growth of spoilage microorganisms. However, heat and nutrients from the

product often infuse the brine allowing bacteria such as L. monocytogenes and lactic acid

bacteria to survive, grow and spread in these recycled chilling brines. Consequently, it is

critical to maintain the microbial safety of the cooling brines, especially when the brine is

recycled. Bacterial contamination of these brines has been directly linked to the

outbreaks of listeriosis from commercial ready-to-eat foods. The USDA�s Food Safety

and Inspection Service (FSIS) issued MPI Bulletin 83-16, stating that brine may be

reused to chill cooked product for various lengths of time based on salinity and

temperature. They range from recycling the brines for one production shift to up to four

weeks (19).

Ultraviolet (UV) light has been utilized for the control of microbial contamination

in some areas of the food industry because of its bacteriocidal effects. The Food and

Drug Administration has approved UV treatments for pathogen reduction in water. The

use of UV is a promising bactericidal alternative for other applications because it does

not undesirably affect the color, flavor, odor, or taste of the product (22). Also, UV

radiation does not produce undesirable by-products and is effective against a wide variety

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of microorganisms (5). The use of ultraviolet radiation to control the growth of

pathogens and spoilage microorganisms while avoiding unfavorable effects on the quality

of the meat has been documented. Stermer et al. (15) reported that UV radiation dose of

150 µW·s·cm-2 reduced bacteria on a smooth surface of fresh meat by 2 log cycles. In

another study, Wong et al. (20) reported the greatest logarithmic reductions of bacteria on

fresh pork muscle was achieved at doses of 100 µW·s·cm-2 for E. coli and 80 µW·s·cm-2

for S. senftenberg where a 1.5- and 2-log reduction was observed, respectively. Sumner

et al. (16) were successful in almost completely eliminating bacteria on agar plates, with

a 99.9% reduction of S. typhimurium at 2,000 µW·s·cm-2. Reduction of bacteria was less

successful on the surface of poultry skin with an 80.5% reduction of S. typhimurium was

obtained at 2,000 µW·s·cm-2. During more recent times, high intensity UV-C lamps have

become available and have enhanced the potential of destroying bacteria on foods.

The objective of this research was to use ultraviolet irradiation within a model

brine chiller system to inactivate L. monocytogenes and lactic acid bacteria species. In

using UV irradiation to reduce the bacterial load in recycled chilling brines, the safety of

these ready-to-eat meat products will be improved due to the decreased risk of foodborne

listeriosis. Also, the shelf life of the product will be increased by the reduction of

spoilage lactic acid bacteria.

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MATERIALS AND METHODS

A. Brine Preparation

The brine solutions were prepared in the laboratory facilities 24 hours before

treatment with ultraviolet light. All equipment and containers used for brine

manufacturing were cleaned using hot water and HC-10 Chlorinated Kleer-Mor

(EcoLab, St. Paul, MN) high foaming caustic cleaner and sanitized with hot water and

Ster-Bac Quaternary Ammonium Sanitizer (EcoLab, St. Paul, MN) at 200 ppm prior

to use. The brines were prepared by dissolving Cargill Top-Flo Evaporated Salt

(99.8% purity) (Cargill Inc., Minneapolis, MN) into domestic water until a 7.9%w/w

or a 13.2%w/w solution was attained.

Top-Flo Evaporated Salt is of food grade quality, complying fully with the

standards for sodium chloride as set forth in the Food Chemicals Codex. The U.S.

Department of Agriculture Food Safety and Inspection Service approved this salt for

direct use in meat and poultry products. The salt contains water-soluble yellow

prussiate of soda, which is added to improve caking resistance in accord with 21CFR

172.490. A chemical analysis of the salt can be found in Appendix I.

The 7.9%w/w brine was prepared by dissolving 4.74 kg of salt into 60 kg of tap

water in a 30 gallon Nalgene© bucket. The 13.2%w/w brine was prepared by

dissolving 7.92 kg of salt into 60 kg of tap water. The salt and water was hand-mixed

until dissolved and placed in a 4°C cooler for 24 hours to yield a final brine

temperature of ~10°C.

B. Inoculum preparation

1. Listeria monocytogenes

Six strains of Listeria monocytogenes (LM) were used in this study.

Listeria monocytogenes Scott A, V7, LCDC, D43, Brie, and ATCC 19115 were

obtained from the Department of Food Science and Technology (FST), Virginia

Polytechnic Institute and State University (VPI&SU), Blacksburg, Virginia. The

cultures were prepared by inoculating 100 ml of trypic soy broth (TSB; Difco

Laboratories, Detroit, MI) supplemented with 0.6% yeast extract (YE; Difco)

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(TSBYE) with one strain of L. monocytogenes, and incubating at 32°C for 48

hours. This procedure was done for each of the six strains being used. One loop

of this culture was streaked onto Modified Oxford (MOX) agar (Oxford Medium

Base plus Modified Antimicrobic Supplement; Difco) to ensure isolation and

incubated at 32°C for 48 hours. A confirmed colony of L. monocytogenes from

the MOX plate was transferred back into 100 ml of sterile TSBYE and incubated

at 32°C for 48 hours and then streaked onto slants of tryptic soy agar (TSA;

Difco) supplemented with 0.6% yeast extract (TSAYE). The L. monocytogenes

stock cultures were maintained on slants of (TSAYE). All culture slants were

stored at 4°C. Before use, one loopful of culture from the slants was grown in 10

ml TSBYE and was incubated at 32ºC for 24 hours. Each of these strains was

centrifuged at 10,000 x G for 5 minutes and the pellet was washed with 10 ml of

either 7.9%w/w or 13.2%w/w sterile brine (Top-Flo Evaporated Salt, Cargill Inc.,

Minneapolis, MN and tap water). The washed cells were also centrifuged at

10,000 x G for 5 minutes and the pellet was suspended in 10 ml sterile brine. A

cocktail of L. monocytogenes was prepared by combining equal proportions of

each of the six strains suspended in brine into a sterile container and stored at 4°C

for 24 hours.

2. Lactic Acid Bacteria

Three strains of lactic acid-producing bacteria (Carnobacterium

gallinarum (ATCC 49517) isolated from ice slush from chicken carcasses,

Lactobacillus plantarum (ATCC 49445) isolated from ground pork, and

Enterococcus faecalis (ATCC 29212; a human isolate) were used in this study.

All were obtained from the American Type Culture Collection (Manassas, VA).

Carnobacterium gallinarum and L. plantarum were chosen to represent typical

post-processing contaminants, while E. faecalis was chosen to represent potential

thermoduric nonsporeformers that may survive thermal processing.

Carnobacterium gallinarum and E. faecalis stock cultures were maintained on

slants of All-Purpose Tween agar (APT; Difco). Lactobacillus plantarum stock

cultures were maintained on slants of deMan, Rogosa, and Sharpe agar (MRS;

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Remel Inc., Lenexa, KS). All culture slants were stored at 4°C. Before use, one

loopful of culture from each slant was grown in 10 ml APT broth (for C.

gallinarum and E. faecalis) or MRS broth (for L. plantarum) and was incubated at

30ºC for 24 hours. Each of these strains was centrifuged at 10,000 x G for 5

minutes and the pellet was washed with 10 ml of sterile brine (Top-Flo

Evaporated Salt, Cargill Inc., and tap water). The washed cells were also

centrifuged at 10,000 x G for 5 minutes and the pellet was suspended in 10 ml

sterile brine. A cocktail of Lactic Acid Bacteria (LAB) was prepared by

combining two equal proportions of each of the three strains suspended in brine

into a sterile container and stored at 4°C for 24 hours.

C. Survival Studies

In order to determine how L. monocytogenes would respond to environmental

stressors such as temperature and brine concentration, several growth studies were

performed. In duplicate sterile bottles, 100 ml of tap water, 7.9%w/w brine, or

13.2%w brine were inoculated with ~5 log10 CFU/ml of the six strain L.

monocytogenes cocktail and incubated at 4°C, 25°C, or 32°C. The brines were then

plated in duplicate on tryptic soy agar supplemented with 0.6% yeast extract

(TSAYE) at 0, 4, 8, 24, 48, 72, 96, 120, and 144 hours. The TSAYE plates were

incubated at 32°C for 48 hours. After incubation, the colonies were counted and

recorded as CFU/ml brine.

D. Ultraviolet Treatment System

The Ultraviolet treatment system used was an Ultra-Violet Water Treatment Unit

(Aquionics Inc., Erlanger, KY) model number AMD 150B/1/2T D. The treatment

was achieved by passing the brine through a stainless steel chamber containing one

UV emitting arc-tube. The arc-tube is mounted in a quartz sleeve and fitted within

the chamber allowing the brine to pass the sleeve on all sides. After treatment, the

brine was returned to a reservoir and was continually pumped through the treatment

system. A diagram of the UV treatment system is available in Appendix II. The

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entire system was kept in a 4°C laboratory in order to allow the brine to remain

chilled.

After the brine had been chilled for 24 hours, it was placed into the reservoir of

the UV treatment system. The pump was started and the uninoculated brine was

allowed to circulate within the system with exposure to UV light for 10 minutes in

order to decompose free chlorine in the brines. The light was then turned off and the

prepared cocktail was added to the brine, giving an approximate inoculum of 1.0x106

CFU/ml (6.0 log CFU/ml). As a control, the inoculated brine was allowed to

circulate through the system with no exposure to ultraviolet light for 1 hour.

Duplicate 50 ml samples were taken at 0, 1, 5, 15, 30, and 60 minutes. After 1 hour

treatment, this brine was emptied from the UV treatment system and discarded. A

new 60 liters of uninoculated brine was added to the reservoir. Prior to addition of the

inoculum, uninoculated brine was allowed to circulate within the system with

exposure to UV light for 10 minutes in order to decompose free chlorine in the brines.

The brine was then inoculated as previously described with the inoculum. The

inoculated brine was recirculated and pumped through the treatment chamber to be

exposed to ultraviolet light at a flow rate of ~47 liters per minute. Samples were

taken in duplicate at 0, 1, 5, 15, 30, and 60 minutes.

In the UV treatment system the brine temperature was taken at each sampling to

monitor any changes. All samples were obtained by aseptically collecting 50ml

samples of the brine out of the brine reservoir and placed into sterile 4 oz. Whirl-

Pak® bags (VWR, Bridgeport, NJ).

E. Microbial Analysis

The experiment was performed as stated above with the 7.9% brine and LM

cocktail, the 13.2% brine and LM cocktail, the 7.9% brine and the LAB cocktail, and

the 13.2% brine and the LAB cocktail. Each brine and cocktail combination was

analyzed in triplicate. The UV Treatment system was cleaned and sanitized between

each repetition. The system was cleaned with fresh hot water (~15 gallons) and low

foaming caustic cleaner, Klenzade FastPac 110: Mechanical and CIP cleaner

(EcoLab, St. Paul, MN), at approximately 2%w/w according to manufacturers

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directions. It was then sanitized with fresh hot water and Ster-Bac Quaternary

Ammonium Sanitizer (EcoLab, St. Paul, MN) at 200 ppm. Cleaning and sanitizing

procedures are found in Appendix III.

1. Listeria monocytogenes

At the appropriate time during recirculation (0, 1, 5, 15, 30, and 60 min),

two 50 ml samples were collected. There was a total of 12 samples taken during

each repetition, two 50 ml samples at each time interval. From each 50 ml

sample, an aliquot was removed and serially diluted with 0.1% peptone (Difco)

water and pour plated in duplicate on Modified Oxford (MOX) agar (Oxford

Medium Base plus Modified Antimicrobic Supplement; Difco) plates in order to

enumerate only the L. monocytogenes (LM) present in the brine. The MOX plates

were incubated at 32°C for 48. After incubation, the colonies were counted and

recorded as CFU/ml brine in a database for later comparison.

Using an aerobic plate count (APC) method, the remainder of the 50 ml

samples were analyzed to determine if any significant injury was caused to the L.

monocytogenes while in the UV treatment system. Another aliquot was removed

from the original 12 samples and was serially diluted with 0.1% peptone (Difco)

water and pour plated onto duplicate trypticase soy agar (TSA; Difco)

supplemented with 0.6% yeast extract (YE; Difco) (TSAYE) in order to

enumerate any microorganisms present in the brine. The TSAYE plates incubated

at 32°C for 48 hours. After incubation, the colonies were counted and recorded as

CFU/ml brine in a database for later comparison.

2. Lactic Acid Bacteria

At the appropriate time during recirculation (0, 1, 5, 15, 30, and 60 min),

two 50 ml samples were collected. There was a total of 12 samples taken during

each repetition, two 50 ml samples at each time interval. From each 50 ml

sample, an aliquot was removed and serially diluted with 0.1% peptone (Difco)

water and pour plated in onto duplicate All-Purpose Tween (APT) Agar (Difco)

containing 0.0032% (w/v) bromcresol purple (BCP) dye (Fisher Scientific,

Pittsburgh, PA) (APT+BCP) plates in order to enumerate only the Lactic Acid

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Bacteria (LAB) present in the brine. The APT+BCP plates were then incubated at

30°C for 48 hours to allow for sufficient growth of any organisms present. After

incubation, the colonies were counted and recorded as CFU/ml brine in a database

for later comparison.

F. Statistical analysis

At the end of the study, the effect of ultraviolet light exposure on the inactivation

of L. monocytogenes and lactic acid bacteria species at different brine concentrations

(7.9%w/w and 13.2%w/w) and its effect on microbial population (log CFU/ml) was

statistically analyzed. The data gathered was compared to the control (no exposure to

UV) to establish any significant change in inhibitory performance that may have

occurred in the brines with regards to each cocktail. Reported values are averages

from three independent trials converted to logarithmic units. Each replicate was

preformed on different days. The different brine and cocktail combinations were

analyzed separately by the general linear model procedure using SAS statistical

software (SAS Institute Inc., Cary, N.C.). Tukey’s HSD was performed to determine

significant differences ( = 0.05) between the mean (log CFU/ml) of the control

brines and the brines exposed to UV light.

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RESULTS AND DISCUSSION

Ultraviolet light (UV) was effective at reducing microbial populations of both L.

monocytogenes and lactic acid bacteria (LAB) in recycled chill brines. Listeria

monocytogenes inoculum concentrations averaged 6.10 log10 CFU/ml for studies in

7.9%w/w brine and 6.01 log10 CFU/ml for studies in 13.2%w/w brines. As seen in Tables

1 and 2, mean L. monocytogenes populations were significantly reduced after five

minutes exposure to UV light in the model brine chiller as compared to the control, which

received no UV light exposure (P<0.05). There was no significant statistical difference

in log reductions of L. monocytogenes plated on the two different media MOX and

TSAYE (P<0.05). Lactic acid bacteria inoculum concentrations averaged 5.94 log10

CFU/ml for studies in 7.9%w/w brines and 5.81 log10 CFU/ml for studies in 13.2%w/w

brines. The lactic acid bacteria inactivation followed a similar trend as the L.

monocytogenes. As seen in Table 3 mean lactic acid bacteria populations were also

significantly reduced after five minutes exposure to UV light in the model brine chiller as

compared to the control (P<0.05). There was at least a 4.5 log CFU/ml reduction in

microbial populations seen in all treated brines after exposure to ultraviolet light for 60

minutes.

The graphs shown in Figures 1, 2, and 3 all depict similar inactivation curves for

L. monocytogenes and lactic acid bacteria in brines as compared to their controls over a

60 minute period. The average microbial populations for controls remained relatively

constant during the entire 60 minutes in the model brine chiller. The maximum rate of

inactivation for treated brines occurred between one and fifteen minutes of ultraviolet

exposure.

Survival studies were performed to determine how L. monocytogenes would

respond to environmental stressors such as temperature and salt concentration. The

brines and tap water were inoculated at ~5 log10 CFU/ml. Figure 4 displays the pathogens

response to salt concentration at refrigeration temperatures (4°C) over a six-day period.

Refrigeration allowed for better survival of L. monocytogenes in the brines (7.9%w/w

and 13.2%w/w) than in the tap water. This may be due to homeoviscous adaptation,

which enables the cells to maintain membrane fluidity at a decreased temperature. As the

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temperature decreases, the cell begins to synthesize and increased amount of mono- and

diunsaturated fatty acids. This increase in the degree of unsaturation leads to a decrease

in lipid melting point, suggesting this adaptation occurs to maintain the lipids in a liquid

and mobile state, thereby allowing membrane proteins to continue to function. As long

as the membrane proteins are functioning, the cell can tolerate the higher salt

concentrations by intracellular accumulation of compatible solutes (7). Compatible

solutes stabilize intracellular enzymes and other proteins and enable them to continue

functioning when the water activity decreases. The solutes Listeria monocytogenes

accumulates are glycinebetaine and carnitine (12). Also, the membrane’s physical state

can influence and/or control expression of genes, particularly those that respond to

temperature. The production of cold shock proteins (CSPs) also contributes to an

organism’s ability to grow at low temperatures. Listeria monocytogenes that has been

cold-shocked from 37°C to 5°C have been found to produce 12 CSPs (3). As shown in

Figure 5, both the brines and the tap water showed similar inactivation rates of the

pathogen when stored at 25°C. At 25°C, all three concentrations showed complete

inactivation of L. monocytogenes after 48 hours. This is consistent with results reported

by Bal’a and Marshall (2) who found that the largest inhibition of L. monocytogenes

occurred on salt-pH gradient plates incubated at 25°C and the smallest area of growth

inhibition occurred on plates incubated at 5°C. As the temperature increased to 32°C

(Figure 6), the L. monocytogenes survived the longest in the tap water, followed by the

7.9%w/w brine and survival was the shortest in the 13.2%w/w brine. This may be

explained by the lower water activity in the 13.2%w/w brines and/or the expression of

salt stress proteins by L. monocytogenes. Miller reported that growth of L.

monocytogenes Scott A occurred at water activities of 0.99, 0.97, 0.93, and 0.92. He also

reported that below aw levels of 0.92 the death rate of L. monocytogenes Scott A was

proportional to water activity (9). The water activity (aw) of the brines was measured

during each replication. It was found that the average aw for the 7.9%w/w brines was

0.94 and the average aw for the 13.2% w/w brines was 0.89. Duché and colleagues

reported that when under osmotic stress at 3.5%w/v NaCl, L. monocytogenes produces

12 salt stress-induced proteins. The identified proteins belong in two groups: the salt

shock proteins (Ssp), which are rapidly but briefly overexpressed, and the stress

acclimation proteins (Sap), which are also rapidly induced but still overexpressed several

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hours later (6). It can be concluded that at colder temperatures L. monocytogenes is more

adaptable to environmental stressors, such as salt concentration. This adaptability is why

L. monocytogenes contamination of recycled chill brines is important. Because of this

adaptability, it is important that recycled brines receive some form of sterilization in

order to avoid contamination of the product.

Other researchers have indicated that UV-energy inactivates bacteria

exponentially and thus the typical death curve for microorganisms treated with UV is

often described as sigmoidal (1, 13, 22). In this study, the use of UV to reduce microbial

populations in brines led to the formation of a sigmoidal curve. The tail of inactivation

curves has been explained in several different ways. The first explanation is the multiple

hit phenomena described by Yousef and Marth (22), which states that the sigmoidal

survival curve was accounted for on the basis of multiple UV hits on a single cell or

single UV hits on multiple cells. The tailing has also been explained by the lack of

homogeneous population (4). This occurs when the bacteria are not uniform in structure

or composition throughout the cocktail due to the fact they are composed of several

different strains. These strains all have distinctive characteristics that make them

different and these differences may cause one strain to be more resistant to ultraviolet

energy then another. Finally, the tail on the sigmoidal shaped inactivation curve may also

be caused by the presence of suspended solids that may block the UV irradiation (13).

Some such solids include food particles from the product being chilled with the brines

and other environmental contaminants such as dust or dirt.

The tailing effect often seen in other death curves was not as prominent in this

study. This may be due to the fact that other UV inactivation studies were performed on

flat surfaces, where the bacteria would have direct contact with the UV energy. As

shown in Figures 1, 2, and 3 microbial numbers in the brines do level slightly after 15

minutes of UV treatment, but the tail is not as pronounced as in other studies. This may

be due to turbidity in the brines caused by air bubbles during recirculation, causing the

UV light to be scattered and have less contact with the microbial cells leading to a slower

rate of death. Perhaps if the length of time the brine was exposed to ultraviolet light was

increased, this tailing effect would have been more prominent.

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The brines inoculated with L. monocytogenes were plated on two types of media,

MOX and TSAYE. This was done to determine the amount of injury that could be

caused to the cells during UV treatment. The early exposure of bacteria to UV is

believed to injure cells. As the dose of UV is increased, mutations occur in the bacterial

DNA that obstructs cellular replication. When the DNA transcription and replication is

blocked, the cellular functions are compromised and this eventually leads to death (13).

Injured cells would be harder to grow on the MOX plates due to its selective nature.

Therefore if a high number of cells were being injured instead of killed in the treatment

system; the counts would be higher on the TSAYE plates. Statistical analysis of the

microbial counts on both types of media indicated no difference; therefore there was no

cellular injury.

As seen in Figures 2 and 3, both 7.9%w/w brine and 13.2%w/w brine show

similar logarithmic reductions in L. monocytogenes when treated for the same amount of

time in the UV treatment system. Figure 4 depicts similar log reductions of both brine

concentrations inoculated with lactic acid bacteria. From the data presented, there is no

statistical difference exhibited in the log reduction between 7.9%w/w brine and

13.2%w/w brine (P<0.05) with both types of microorganisms. However, the lactic acid

bacteria seemed to be slightly more susceptible to salt concentrations then the L.

monocytogenes. As shown on Table 3, in the control brines that had no exposure to UV,

the mean lactic acid bacteria populations decreased by twice as much in the 13.2% brine

after 60 minutes than in the 7.9% brines. This is consistent with previous studies, in

which low levels of NaCl stimulated lactic acid bacteria growth but higher levels

decreased lactic acid bacteria growth drastically (11, 14, 18).

In the UV treatment system the brine temperature was taken at each sampling to

monitor any changes. The control brines averaged 11.3°C at the beginning of the one-

hour treatment. During the hour of treatment the brine temperature increased an average

of 4.0°C. The UV treated brines averaged 10.3°C at the beginning of the one hour

treatment. During the one-hour treatment with UV light, the brine temperature increased

an average of 15.5°C.

The pH of the brines was also monitored during each repetition of the study. It

was found that all brines averaged a pH of 7.2. Sodium chloride is a neutral chemical

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salt, and exhibits neither alkalinity nor acidity. Sodium chloride brines are highly

ionized, and possess no buffering action. Because of this, the pH of sodium chloride

brines depends, not on the concentration of the salt in the brine, but on the presence of

minute quantities of foreign alkaline or acidic materials in the brine. These usually

appear in the form of dissolved gases in the dissolving water. For example, the presence

of CO2 in the dissolving water can lower the pH of the salt brine from the neutral point of

7.0 to a value of 4.0�6.0. Similarly, ammonia in the water can raise the pH of the brine to

the range of 8.0�10.0. The brines in this study were all made with tap water in the

laboratory facility. Depending on where the brines in a processing facility are made, as

well as how the product is processed, the pH of brines in industry usually ranges from 6.0

to 8.0.

Other researchers have obtained comparable results to this study using other

methods of disinfecting recycled chiller brines. Ye et al. (21) used an electrochemical

treatment system to treat brines over a 60 minute time period. The group found and

average D-value of 2.5 min at all three temperatures (4, 0, and -8°C). Hart et al. (8) used

microfiltration and were able to see ~3 log10 CFU/ml reduction in microorganisms after

80 minutes of treatment.

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CONCLUSIONS Overall results indicate that inline treatment of chill brines with ultraviolet light

(UVC) shows promise as a processing intervention to inactivate L. monocytogenes and

lactic acid bacteria. This design of the lab-scale ultraviolet treatment system allows for a

continuous inline treatment of the brine and L. monocytogenes and lactic acid bacteria

may be effectively controlled without interrupting the chilling operation. When

compared with an offline alternative, this form of treatment system could be easily

implemented, and would not require extra brine, storage tanks, or pumping equipment.

Validation for the use of ultraviolet light in processing systems can provide

documentation for a critical control point within Hazard Analysis and Critical Control

Point (HACCP) plans to address pathogen reduction of post thermally processed

products.

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TABLE 1. Bacterial populations of L. monocytogenes (LM) plated on Modified Oxford Agar (MOX) LM populations (mean log CFU/ml ± SD; n=6)

7.9% w/w brine 13.2%w/w brine Time (minutes) Control UV Control UV

0 6.10±0.07a* 6.05±0.01a 5.93±0.17a 6.06±0.16a 1 6.09±0.04a 5.65±0.07a 5.97±0.05a 5.61±0.48a

5 6.06±0.06a 4.11±0.57b 5.96±0.12a 3.84±0.64b

15 6.04±0.06a 2.37±0.37c 5.88±0.16a 2.45±0.36c 30 6.02±0.03a 2.16±0.53cd 5.89±0.15a 1.82±0.07c

60 6.00±0.03a 1.36±0.63d 5.76±0.26a 1.49±0.01c

* Within each brine concentration, mean values followed by different letters are significantly different (P<0.05)

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TABLE 2. Bacterial populations of L. monocytogenes (LM) plated on Tryptic Soy Agar supplemented with 0.6% Yeast Extract (TSAYE) LM populations (mean log CFU/ml ± SD; n=6)

7.9% w/w brine 13.2%w/w brine Time (minutes) Control UV Control UV

0 6.14±0.04a* 6.12±0.03a 5.97±0.20a 6.09±0.20a 1 6.14±0.04a 5.79±0.09a 6.04±0.05a 5.61±0.47a

5 6.09±0.05a 4.20±0.52b 6.01±0.06a 3.94±0.74b

15 6.08±0.07a 2.41±0.37c 5.95±0.13a 2.52±0.40c 30 6.08±0.03a 2.20±0.49cd 5.95±0.12a 1.82±0.16c

60 6.04±0.05a 1.51±0.49d 5.87±0.13a 1.61±0.03c

* Within each brine concentration, mean values followed by different letters are significantly different (P<0.05)

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TABLE 3. Bacterial populations of lactic acid bacteria (LAB) plated on All Purpose Tween Agar supplemented with 0.0032%w/v bromcresol purple dye (APT+BCP) LAB populations (mean log CFU/ml ± SD; n=6)

7.9% w/w brine 13.2%w/w brine Time (minutes) Control UV Control UV

0 6.04±0.25a* 5.84±0.27a 5.84±0.07a 5.78±0.04ab 1 6.05±0.23a 5.64±0.17a 5.78±0.13ab 5.20±0.05b

5 6.05±0.21a 3.90±0.53b 5.79±0.12ab 3.52±0.31c

15 6.00±0.18a 2.80±0.65c 5.71±0.12ab 1.97±0.49d 30 5.98±0.18a 2.10±0.31cd 5.65±0.11ab 1.38±0.06e

60 5.89±0.28a 1.49±0.10d 5.54±0.06ab 0.75±0.01f

* Within each brine concentration, mean values followed by different letters are significantly different (P<0.05)

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0.00

1.00

2.00

3.00

4.00

5.00

6.00

7.00

0 1 5 15 30 60time (min)

log

CFU

/ml

Figure 1. Mean microbial populations of brine inoculated with a six-strain mixture of Listeria monocytogenes plated on Modified Oxford Agar (MOX) during 1 hour of UV exposure. Solid lines represent 7.9%w/w brine solutions; dashed lines represent 13.2%w/w brine solutions. 7.9% brine � no UV exposure (▲); 7.9% brine � with UV exposure (■); 13.2% brine � no UV exposure (●); 13.2% brine � with UV exposure (♦).

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0.00

1.00

2.00

3.00

4.00

5.00

6.00

7.00

0 1 5 15 30 60

time (min)

log

CFU

/ml

Figure 2. Mean microbial populations of brine inoculated with a six-strain mixture of Listeria monocytogenes plated on Tryptic Soy Agar (TSA) supplemented with 0.6% Yeast Extract (YE) during 1 hour of UV exposure. Solid lines represent 7.9%w/w brine solutions; dashed lines represent 13.2%w/w brine solutions. 7.9% brine � no UV exposure (▲); 7.9% brine � with UV exposure (■); 13.2% brine � no UV exposure (●); 13.2% brine � with UV exposure (♦).

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0.00

1.00

2.00

3.00

4.00

5.00

6.00

7.00

0 1 5 15 30 60

time (min)

log

CFU

/ml

Figure 3. Mean microbial populations of brine inoculated with a three-strain mixture of lactic acid bacteria plated on All Purpose Tween (APT) Agar supplemented with 0.0032% (w/v) bromcresol purple dye (BCP) during 1 hour of UV exposure. Solid lines represent 7.9%w/w brine solutions; dashed lines represent 13.2%w/w brine solutions. 7.9% brine � no UV exposure (▲); 7.9% brine � with UV exposure (■); 13.2% brine � no UV exposure (●); 13.2% brine � with UV exposure (♦).

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0.00

1.00

2.00

3.00

4.00

5.00

6.00

7.00

0 72 144

time (hours)

log

CFU

/ml

tap water7.9% brine13.2% brine

Figure 4. Mean microbial populations of brine and tap water inoculated with a six-strain mixture of Listeria monocytogenes stored at 4°C over a 6-day period.

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0.00

1.00

2.00

3.00

4.00

5.00

6.00

0 4 8 24 48 72 96 120 144

time (hours)

log

CFU

/ml

tap water7.9% brine13.2% brine

Figure 5. Mean microbial populations of brine and tap water inoculated with a six-strain mixture of Listeria monocytogenes stored at 25°C over a 6-day period.

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0.00

1.00

2.00

3.00

4.00

5.00

6.00

0 4 8 24 48 72 96 120 144

time (hours)

log

CFU

/ml

tap water7.9% brine13.2% brine

Figure 6. Mean microbial populations of brine and tap water inoculated with a six-strain mixture of Listeria monocytogenes stored at 32°C over a 6-day period.

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REFERENCES 1. Bachmann, R. 1975. Sterilization by intense ultraviolet radiation. Brown Boveri

Rev. 62: 206�209.

2. Bal�a, M.F.A., and D.L. Marshall. 1996. Use of double-gradient plates to study combined effect of salt, pH, monolaurin, and temperature on Listeria monocytogenes. J. Food Prot. 59(6): 601�607.

3. Bayles, D.O., B.A. Annous, and B.J. Wilkinson. 1996. Cold stress proteins

induced in Listeria monocytogenes in response to temperature downshock and growth at low temperatures. Appl. Environ. Microbiol. 62(3): 1116�1119.

4. Block, S. S. 1991. Disinfection, Sterilization and Preservation. 3rd Ed. Lea &

Febier. Philadelphia, PA.

5. Chang, J.C.H., S.F. Ossoff, D.C. Lobe, M.H. Dorfman, C.M. Dumais, R.G. Qualls, and J.D. Johnson. 1985. UV inactivation of pathogenic and indicator microorganisms. Appl. Environ. Microbiol. 49(6): 1361�1365.

6. Duché, O., F. Trémoulet, P. Glaser, and J. Labadie. 2002. Salt stress proteins

induced in Listeria monocytogenes. Appl. Environ. Microbiol. 68(4): 1491�1498.

7. Farkas, J. 2001. Physical methods of food preservation. p. 567�591. In M.P

Doyle, L.R. Beuchat, and T.J. Montville (ed). Food Microbiology: Fundamentals and Frontiers 2nd ed. ASA Press, Washington, DC.

8. Hart, M.R., C.C. Huxsoll, Tsai LS, NG KC. 1988. Preliminary studies of

microfiltration for food processing solution reuse. J. Food Prot. 51(4): 269�276.

9. Miller, A.J. 1992. Combined water activity and solute effects on growth and survival of Listeria monocytogenes Scott A. J. Food Prot. 55(6):414�418.

10. Miller, A.J., J.E Call, and B.S Eblen. 1997. Growth, injury, and survival

potential of Yersinia enterocolitica, Listeria monocytogenes, and Staphylococcus aureus in brine chiller conditions. J. Food Prot. 60(11): 1334�1340.

11. Paludan-Müller, C., M. Madsen, P, Sophanodora, L. Gram, and P.L. Møller.

2002. Fermentation and microflora of plaa-som, a Thai fermented fish product prepared with different salt concentrations. Int. J. of Food Microbiol. 73(1): 61�70.

12. Russell, N.J., R.I. Evans, P.F. ter Steeg, J. Hellemons, A. Verheul, and T. Abee.

1995. Membranes as a target for stress adaptation. Int. J. of Food Microbiol. 28: 255�261.

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13. Sastry, S.K., A.K. Datta and R.W. Worobo. 2000. Ultraviolet light in kinetics of

microbial inactivation for alternative food processing technologies. J. Food Sci. Special Supplement.

14. Simonson, L., H. Salovaara, and M. Korhola. 2003. Response of wheat

sourdough parameters to temperature, NaCl and sucrose variations. Food Microbiol. 20(2): 193�199.

15. Stermer. R.A., M. Lasater-Smith, and C.F. Brasington. 1987. Ultraviolet

radiation � An effective bactericide for fresh meat. J. Food Prot. 50(2): 108�111.

16. Sumner, S.S., E.A. Wallner-Pendleton, G.W. Froning, and L.E. Stetson. 1995.

Inhibition of Salmonella typhimurium on agar medium and poultry skin by ultraviolet energy. J. Food Prot. 59(3): 319�321.

17. Swaminathan, B. 2001. Listeria monocytogenes. p. 383-409. In M.P. Doyle,

L.R. Beuchat, and T.J. Montville (ed.), Food Microbiology: Fundamentals and Frontiers, 2nd ed. ASM Press, Washington, DC.

18. Tassou, C.C., E.Z. Panagou, and K.Z. Katsaboxakis. 2002. Microbiological and

physiochemical changes of naturally black olives fermented at different temperatures and NaCl levels in the brines. Food Microbiol. 19(6): 605�615.

19. USDA. Food Safety and Inspection Service. 1983. Reuse of water or brine

cooling solutions on product following a heat treatment. MPI Bulletin 83-16. USDA, FSIS, Washington, DC.

20. Wong, E., R.H. Linton, and D.E. Gerrard. 1998. Reduction of Escherichia coli

and Salmonella senftenberg on pork skin and pork muscle using ultraviolet light. Food Microbiol. 15(4): 415�423.

21. Ye, J., H. Yang, H-K. Kim, and Y. Li. 2001. Inactivation of Listeria

monocytogenes in recirculated brine for chilling thermally processed bacon using an electrochemical treatment system. J. Food Sci. 66(5): 729�733.

22. Yousef, A.E., and E.H. Marth. 1988. Inactivation of Listeria monocytogenes by

ultraviolet energy. J. Food Sci. 53(2): 571�573.

23. Zaika, L.L., S.A. Palumbo, J.L. Smith, F.D. Corral, S. Bhaduri, C.O. Jones, and A.H. Kim. 1990. Destruction of Listeria monocytogenes during frankfurter processing. J. Food Prot. 53(1): 18�21.

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AREAS FOR FURTHER RESEARCH In summary, brines contaminated with L. monocytogenes and lactic acid bacteria

may be disinfected using ultraviolet energy. One further area for investigation may

include exposing the brines to ultraviolet light for periods of time longer then 60 minutes.

In this study, there was never a decrease in microbial numbers below detectable levels

and it is essential to know how much exposure to UV light is necessary for all

microorganisms in the brines to be inactivated. Another area for further study may consist

of obtaining used brines from a processing facility producing ready-to-eat meat products

and subjecting those brines to an investigation similar to this one. The used brines are

likely to contain a number of dissolved and suspended solids due to the particles from

product permeating into the brine during processing. These solids are likely to scatter

ultraviolet light rays and slow down the inactivation rate. Finally, a study in which L.

monocytogenes and lactic acid bacteria are both inoculated into the same brine should be

tested. The lactic acid bacteria may aid in the inactivation of L. monocytogenes in the

brine through the production of bacterocins.

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APPENDIX I Chemical Analysis of Top-Flo Evaporated Salt (99.8% purity). Supplied by Cargill Inc., Minneapolis, MN:

Component Units Typical Specification

Sodium Chloride (dry)1 % 99.86 99.80 min. Calcium & Magnesium (as Ca) % 0.04 - Sulfate (as SO4) % 0.06 - Surface moisture2 % 0.03 0.1 max Copper (as Cu) ppm 0.01 0.5 max. Iron (as free Fe) ppm 0.2 2.0 max. Heavy Metals (as Pb) ppm <1.0 2.0 max. Water Insolubles ppm 165 200 max. Yellow Prussiate of Soda3 ppm 5 13 max.

1By difference of impurities 2110°C for 2 hours 3Anticaking agent (sodium ferrocyanide decahydrate)

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APPENDIX II Diagram of the Ultraviolet Treatment System:

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APPENDIX III Methods for cleaning the UV Treatment System:

Prior to cleaning, the UV lamp system was allowed to de-energize and cool down

for at least 30 minutes. For safety, wearing chemical resistant rain suit, boots, gloves and

eye/face protection is advised. The test solution (inoculated brines) was drained and the

reservoir was rinsed with hot fresh water (~15 gallons). The fresh water was circulated

for 2 minutes and drained. The reservoir was then filled again with fresh hot water (~15

gallons) and low foaming caustic cleaner, Klenzade FastPac 110: Mechanical and CIP

cleaner (EcoLab, St. Paul, MN), at approximately 2%w/w. The pump was started and the

solution was circulated for 8 minutes and then the cleaning solution was drained. The

reservoir was again filled with fresh hot water, circulated and then drained. Once rinsed

and drained, the reservoir was filled again with fresh hot water and Ster-Bac Quaternary

Ammonium Sanitizer (EcoLab, St. Paul, MN) at 200 ppm. Sanitizer was circulated for 2

minutes and then drained. The entire unit was then rinsed again with fresh water. A 50

ml sample was obtained from the rinse water and pour plated on trypticase soy agar

(TSA, Difco) to ensure the system is free from microbial contamination.

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VITAE Karol Gailunas, the daughter of Charles and Barbara Gailunas, was born and raised in

Catonsville, MD where she attended the Magnet School for Pre-Engineering and Student

Conducted Research at Woodlawn High School, graduating in 1997. Following high

school, she attended Virginia Polytechnic Institute and State University and received her

Bachelor�s degree in Biology and a Minor in Chemistry in 2001.

After graduation, she decided to stay at Virginia Tech to pursue a Master�s degree in

Food Science and Technology. She began the program in the summer of 2001. While in

graduate school, she was a member of the Institute of Food Technologists and the

International Association for Food Protection.


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