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Applied and Environmental Microbiology, January 2001, p. 198-205, Vol. 67, No. 1
0099-2240/01/$04.00+0 DOI: 10.1128/AEM.67.1.198-205.2001
Copyright © 2001, American Society for Microbiology. All rights reserved.
Molecular Studies on the Ecology of Listeria
monocytogenes in the Smoked Fish Processing Industry
Dawn M.
Norton,1
Meghan A.
McCamey,1
Kenneth L.
Gall,2
Janet M.
Scarlett,3
Kathryn J.
Boor,1 and
Martin
Wiedmann4,*
Food Safety Laboratory, Department of Food
Science,1 Department of Population
Medicine and Diagnostic Sciences,3 and
Department of Food Science,4 Cornell
University, Ithaca, New York 14853, and Cornell University
Cooperative Extension, New York Sea Grant, State University of New
York, Stony Brook, New York 11794-50022
Received 18 April 2000/Accepted 14 September 2000
 |
ABSTRACT |
We have applied molecular approaches, including PCR-based detection
strategies and DNA fingerprinting methods, to study the ecology of
Listeria monocytogenes in food processing environments. A
total of 531 samples, including raw fish, fish during the cold-smoking process, finished product, and environmental samples, were collected from three smoked fish processing facilities during five visits to each
facility. A total of 95 (17.9%) of the samples tested positive for
L. monocytogenes using a commercial PCR system (BAX for
Screening/Listeria monocytogenes), including 57 (27.7%)
environmental samples (n = 206), 8 (7.8%) raw
material samples (n = 102), 23 (18.1%) samples
from fish in various stages of processing(n = 127), and 7 (7.3%) finished product samples (n = 96). L. monocytogenes was isolated from 85 samples
(16.0%) using culture methods. Used in conjunction with a 48-h
enrichment in Listeria Enrichment Broth, the PCR system had
a sensitivity of 91.8% and a specificity of 96.2%. To track
the origin and spread of L. monocytogenes, isolates were
fingerprinted by automated ribotyping. Fifteen different ribotypes were identified among 85 isolates tested. Ribotyping data
established possible contamination patterns, implicating raw
materials and the processing environment as potential sources of
finished product contamination. Analysis of the distribution of
ribotypes revealed that each processing facility had a unique contamination pattern and that specific ribotypes persisted in the environments of two facilities over time (P
0.0006). We conclude that application of molecular approaches can
provide critical information on the ecology of different L. monocytogenes strains in food processing environments. This
information can be used to develop practical recommendations for
improved control of this important food-borne pathogen in the food industry.
 |
INTRODUCTION |
The advent of molecular methodology
has revolutionized our ability to investigate and understand microbial
ecology, offering new and unique opportunities to explore the ecology
of food-borne pathogens, including Listeria monocytogenes,
throughout the food chain and in the food processing environment.
Highly discriminatory molecular typing methods, including multilocus
enzyme electrophoresis, pulsed-field gel electrophoresis (PFGE), random
amplification of polymorphic DNA, ribotyping, and phage typing, have
been successfully applied to investigations of contamination patterns
in foods and in the food processing environment and are increasingly
used for surveillance of human disease cases and for tracking of
outbreak sources (2-4, 7, 12, 26, 34, 36, 37, 39). While each method provides discriminatory differentiation of L. monocytogenes subtypes, highly automated and standardized methods
provide a simplified approach to molecular subtyping and data analysis. The RiboPrinter Microbial Characterization System (Qualicon,
Inc., Wilmington, Del.) is one example of such an approach. This system is based on ribotyping, a subtyping method based upon scoring restriction polymorphisms in the rRNA operons of
prokaryotes (8, 9, 25).
L. monocytogenes, an invasive food-borne pathogen capable of
causing serious disease in immunocompromised individuals and pregnant
women, is common to many natural and man-made environments (16). As this organism is ubiquitous and capable of growth
at refrigeration temperatures, the zero-tolerance ruling issued by the
U.S. Food and Drug Administration for L. monocytogenes in ready-to-eat foods presents a serious challenge to the food industry. Cold-smoked fish products, which are typically consumed without cooking, are among the ready-to-eat foods of particular concern due to
the lack of a heat inactivation step during processing. The prevalence
of L. monocytogenes in cold-smoked fish and cooked seafood
products has been reported to range from 6 to 36% (6) up
to 78% (15, 27). Many studies have also demonstrated a high prevalence of L. monocytogenes in a variety of food
processing environments (3, 4, 29, 33, 34, 37) and in
ready-to-eat foods that had been subjected to microbial destruction
steps sufficient to eliminate L. monocytogenes present in
raw materials (for a recent survey, see
http://www.fsis.usda.gov/oa/topics/lm_action.htm), strongly
suggesting that the processing environment represents a significant
source of this organism in finished products.
We hypothesize that molecular studies on the ecology of L. monocytogenes strains present in food processing environments will provide information crucial for the development of better control and
prevention strategies for this important food-borne pathogen. The
smoked fish industry provides an ideal model for the development and
evaluation of molecular detection and tracking systems, as L. monocytogenes is frequently isolated from cold-smoked
fish and hazard analysis critical control point (HACCP) programs are mandatory for seafood processors (1). The primary
objective of this study was to investigate the prevalence, ecology, and transmission of L. monocytogenes in different seafood
processing facilities using molecular detection and subtyping
methods. The application of a commercially available
PCR-based screening system for L. monocytogenes (BAX
for Screening/Listeria monocytogenes; Qualicon, Inc.)
allowed us to evaluate its performance using a culture-based detection
method as a standard of comparison.
 |
MATERIALS AND METHODS |
Samples.
A total of 531 samples were collected from three
New York State smoked fish processing facilities over five visits (30 April, 10 August, 26 August, 13 October, and 26 October) to each
facility in 1998. Processors C and D were located 2 miles apart.
Processor B was located approximately 42 miles from the other two
facilities. Samples collected from the processing environment
(n = 206) were taken from floor drains, sink drains,
cooler floors, and equipment surfaces. Sterile swabs were moistened
with 1.0% peptone water containing 0.85% NaCl prior to sampling dry
surfaces. Samples of raw fish (n = 102), belonging
predominantly to the family Salmonidae, were taken from the
collar and belly flap area of fresh, frozen, or thawed whole gutted
fish or fish fillets. In-process samples (n = 127) were
taken from fish during the wet or dry brine step and from brine
solutions. Finished product samples (n = 96) included paper-wrapped and vacuum-packaged cold-smoked fish. Environmental swabs
were transported in 2.0 ml of 1.0% peptone water containing 0.85%
NaCl. All other samples were transported in sterile Stomacher 400 closure bags (Seward Ltd., London, United Kingdom). Samples were
transported to the laboratory and held on ice. Sample analysis was
initiated within 24 h of collection.
Bacteriological analysis.
The method for isolation of
L. monocytogenes used in this study was a modification of
the protocol recommended by the Food and Drug Administration for the
isolation of L. monocytogenes from food (24).
Twenty-five-gram portions of raw, in-process, and smoked fish, prepared
using sterilized instruments, were homogenized in 225 ml of
Listeria Enrichment Broth (LEB) (Difco Laboratories, Detroit, Mich.) using a Stomacher 400 laboratory blender (Seward Ltd.).
Brine solutions, in 25-ml aliquots, were inoculated into 225 ml of LEB.
Swabs and transport media were transferred aseptically to 8 ml of LEB.
Following 24 and 48 h of incubation at 30°C, 0.1 ml of each
enrichment culture was plated on Oxford medium containing the Oxford
Antimicrobic Supplement (Difco Laboratories) and incubated at 30°C
for 48 h. Esculin hydrolysis-positive colonies with morphology typical for Listeria spp. were streaked for isolation on
brain heart infusion (Difco Laboratories) agar and incubated at 37°C for 24 h. Colonies were isolated preferentially from the Oxford plate inoculated after 24 h of sample enrichment to facilitate recovery of L. monocytogenes as opposed to other
Listeria species (30, 35). Pure culture
isolates used for hlyA PCR or BAX system analysis (for
confirmation that this system correctly identified isolates from
culture-positive, BAX system-negative samples) were grown in brain
heart infusion broth at 37°C with shaking for 12 to 15 h.
Identification of L. monocytogenes.
Four
Listeria-like isolates obtained from each sample on Oxford
plates were tested with a PCR assay targeting the
listeriolysin O gene, hlyA, to specifically identify
L. monocytogenes isolates. Primers
-1 (CCT AAG ACG CCA
ATC GAA AAG AAA) and
-1 (TAG TTC TAC ATC ACC TGA GAC AGA) define an
858-bp fragment of the hlyA gene (10). Assays
were performed using GeneAmp PCR core reagents (Perkin-Elmer Applied
Biosystems, Foster City, Calif.). Each 25-µl reaction mixture
contained 1× PCR buffer II, 1.5 mM MgCl2, 125 µM each
dATP, dCTP, dGTP, and dTTP, 0.5 µM each primer, 1 U of Amplitaq DNA
polymerase, and 2 µl of a 1:10 dilution of a crude cell lysate
prepared as described by Furrer et al. (18). Cycling was
performed in the GeneAmp PCR system 2400 (Perkin-Elmer Applied Biosystems). Amplification cycling began with 2 min at 95°C, followed by 40 cycles of 95°C for 10 s, 60°C for 30 s, and 72°C
for 30 s. A final extension step of 72°C for 10 min was followed
by a hold at 4°C. The PCR products were electrophoresed on 1.5%
agarose gels at 120 V, stained with ethidium bromide, and
photodocumented (41). A positive result was indicated by
the presence of an approximately 858-bp band.
BAX for Screening/Listeria monocytogenes.
Following 48 h of sample enrichment, 250 µl of the enrichment
culture was removed and centrifuged at maximum speed in a bench-top microcentrifuge for 2 min. The supernatant was discarded and the pellet
was resuspended in 250 µl of sterile deionized water. This prelysis
wash step was incorporated to minimize the possibility of PCR
inhibition by components of the enrichment culture (personal communication from Technical Assistance, Qualicon, Inc.). The lysate
was prepared as outlined in the manufacturer's protocol. Temperature
cycling for the DNA amplification step was performed in either the
GeneAmp PCR system 2400 or PCR system 9600 (Perkin-Elmer Applied
Biosystems). PCR products were loaded onto 1.5% agarose gels as
outlined in the BAX for Screening protocol, electrophoresed at 120 V,
stained with ethidium bromide, and photodocumented (41). A
positive result was indicated by the presence of an approximately 400-bp band in the sample lane and an 800-bp band in the corresponding control lane. Aliquots of the resuspended enrichment culture pellets, stored at
80°C, were used to retest samples for which PCR-based screening and culture methods yielded discrepant results.
Ribotyping.
One L. monocytogenes isolate from
each culture-positive sample was subtyped. Automated ribotyping with
normalized data was performed using the RiboPrinter (Qualicon, Inc.),
as previously described (9, 25), in the Laboratory for
Molecular Typing at Cornell University. This automated typing method
involves EcoRI digestion of L. monocytogenes
chromosomal DNA followed by Southern hybridization with an
Escherichia coli rrnB rRNA operon probe. Images are
acquired with a charge-coupled device and analyzed using custom
software that normalizes fragment pattern data for band intensity and
relative band size compared to a molecular size marker.
Statistical analyses.
Culture- and PCR-based detection
system results were compared by defining the culture-based system
results as the standard of comparison ("gold standard") and then
calculating the sensitivity (true positive rate), specificity (true
negative rate), and accuracy (method agreement) of the PCR-based system
using standard formulas (11). BAX system-negative,
culture-positive results were interpreted as BAX system false-negative
results. As characterization of as few as five Listeria-like
isolates in a culture-based screen can result in an overall
sample-negative result (24), BAX system-positive results
were interpreted as false positive if hlyA screening of four
Listeria-like isolates from the corresponding sample yielded negative results. If the presence of L. monocytogenes was
subsequently confirmed by hlyA PCR screening of up to 16 additional isolates from a sample, the BAX results were interpreted as
true positive for calculation of the revised specificity estimate.
The rates of recovery of specific ribotypes of L. monocytogenes among the three processing plants and among the
sample sources (environment, raw materials, in-process product, and
finished product) were compared using Pearson's chi-square test. Exact P values were calculated since expected cell values in some
cells were less than five. No analyses were attempted for ribotypes isolated fewer than four times overall due to the small sample size and
infrequency of those observations. P values of
0.05 were
considered significant. All analyses were performed using the
statistical software program StatXact-4 for Windows (CYTEL Software
Corporation, Cambridge, Mass.).
 |
RESULTS |
Detection of L. monocytogenes in cold-smoked fish and
in the smoked fish processing environment.
A total of 531 environmental, raw material, in-process, and smoked fish samples were
screened for the presence of L. monocytogenes using both the
culture-based method and the BAX for Screening/Listeria monocytogenes system. The BAX PCR system detected L. monocytogenes in 17.8% of the 531 samples, compared to 16.0%
positive-culture results. Sensitivity, specificity, and overall
accuracy estimates for the PCR system are shown in Table
1. Thirteen samples that gave initial BAX
system false-negative results were retested using the resuspended
frozen enrichment culture pellets. Six samples gave positive results
upon retesting, improving the sensitivity of the PCR system (Table 1).
Twenty-nine samples gave BAX system false-positive results compared to
the initial culture-based screening results. Subsequent hlyA
PCR screening of up to 16 additional isolates per sample confirmed
the presence of L. monocytogenes in 12 of these samples,
thus improving the specificity of the PCR system (Table 1). While there
was no apparent correlation between sample type and BAX system
false-positive results, four of the seven BAX system false-negative
samples were taken from finished products. The corrected BAX system
sensitivity and specificity values reported in this study should be
regarded as rough estimates, as only the discrepant results were
further analyzed. Estimation of true corrected values would have
required retesting of all samples.
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TABLE 1.
Sensitivity and specificity estimates for the BAX
for Screening/Listeria monocytogenes system using
culture-based detection results as the standard of comparison
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The BAX system detected L. monocytogenes in 27.7% of the
206 environmental samples taken throughout the processing areas (Table 2) (the data reflect prevalence following
reexamination of discrepant results). Positive samples included those
from floors and floor drains in raw material preparation areas,
brining rooms, cold smokers, finished product processing
areas, and food contact surfaces, including cutting tables
and automated finished product slicer blades. L. monocytogenes was isolated from environmental samples with a lower
frequency (21.4%) than was detected by the PCR-based system. Nine raw
material samples (8.8%), including salmon, whitefish, and chub, were
L. monocytogenes culture positive, compared to a slightly
lower frequency using the PCR-based system. L. monocytogenes was detected in in-process samples with a slightly higher frequency (18.1%) by the PCR-based system. The prevalence of L. monocytogenes in finished products, including smoked sea bass,
sablefish and cold-smoked salmon, was similar to that observed in raw
materials. Additional Listeria species (L. monocytogenes hlyA PCR negative) were isolated from 54.1%
of the 85 culture-positive samples.
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TABLE 2.
Detection of L. monocytogenes in samples from
the processing environment, raw materials, fish during the
cold-smoking process, and cold-smoked fish
|
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Tracking L. monocytogenes in cold-smoked fish and in
the smoked fish processing environment.
L.
monocytogenes strain characterization by ribotyping identified 15 ribotypes among 85 isolates analyzed. The
distribution of ribotypes among processing facilities, grouped by
sampling visit, is shown in Fig. 1 to 3.

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FIG. 1.
Ribotypes of L. monocytogenes isolates from
processor B environmental, raw material, in-process, and finished
product samples grouped by sampling visit. (E), environmental sample;
(R), raw materials; (IP), in-process sample; (F), finished product.
*, ribotype isolated most frequently from processor B samples.
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FIG. 2.
Ribotypes of L. monocytogenes isolates from
processor C environmental, raw material, in-process, and finished
product samples grouped by sampling visit. (E), environmental sample;
(R), raw materials, (IP), in-process sample, (F), finished product. * and **, ribotypes isolated most frequently from processor C
samples.
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Seven different ribotypes were isolated
from samples collected at processor B (Fig. 1). L. monocytogenes DUP-1042C, isolated from 36.4% of positive samples,
predominated in the samples collected from this facility. This strain
persisted in environmental samples collected over a period of 5 months
and was also isolated from raw materials and in-process samples.
L. monocytogenes DUP-1045 was isolated from 31.8% of
positive processor B samples and persisted in environmental samples
collected over 2.5 months. This ribotype was isolated only from the
environment of processor B, was not isolated from processor C samples,
and was isolated from only two in-process samples collected from
processor D (Fig. 3). As shown in Table
3, the distribution of ribotypes
DUP-1042C and DUP-1045 varied significantly by processing facility
(P = 0.0003 and P = 0.0006, respectively).

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FIG. 3.
Ribotypes of L. monocytogenes isolates from
processor D environmental, raw material, in-process, and finished
product samples grouped by sampling visit. (E), environmental sample;
(R), raw materials; (IP), in-process sample; (F), finished product.
*, ribotype isolated most frequently from processor D samples.
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Eight different L. monocytogenes ribotypes were
isolated from 16 of the samples collected at processor C (Fig.
2). L. monocytogenes DUP-1044A and DUP-1046B were
isolated with the highest frequency (25.0% each) from positive
samples. L. monocytogenes DUP-1044A persisted
in samples collected from this facility over 4 months and was not
isolated from processor B samples. The distribution of ribotype
DUP-1044A, however, was not shown to vary significantly by processor
(Table 3). The distribution of ribotype DUP-1046B, isolated only from
samples collected at processor C, was shown to vary significantly among
processing facilities (P = 0.0144) (Table 3).
Nine L. monocytogenes ribotypes were isolated from 47 of the
samples collected at processor D (Fig. 3). L. monocytogenes
DUP-1039C, isolated from 48.9% of positive processor D samples,
persisted in the processing environment over all sampling visits (6 months). This strain was not isolated from raw material samples
collected at processor D or from any samples collected from processor B or C. The distribution of L. monocytogenes DUP-1039C was
shown to vary significantly by processing facility (P = 0.0000) (Table 3). While L. monocytogenes ribotypes
DUP-1044A and DUP-1062 also persisted in samples collected from
processor D over a 3-month period, the distribution of these ribotypes
did not vary significantly by processing facility (Table 3).
As preliminary analyses indicated that the type of sample collected
varied significantly (P = 0.0001) according to
processing facility, we suspected that the apparent difference in
ribotype distribution among processors could be attributed to the
prevalence of a given ribotype in a specific sample type. The
distribution of each ribotype, however, was not shown to vary
significantly by sample type (P > 0.05).
 |
DISCUSSION |
L. monocytogenes is a food-borne bacterial pathogen
that is ubiquitous in nature and shows the ability to persist in the
food processing environment for prolonged time periods. Control of this
organism is thus extremely challenging for the food industry. Development of a better understanding of the ecology of L. monocytogenes in food processing plants in combination with rapid,
standardized detection and typing systems will provide critical tools
and knowledge for the development and verification of improved control strategies.
In-plant L. monocytogenes contamination patterns.
L. monocytogenes was detected in a variety of environmental,
raw material, in-process, and cold-smoked fish samples (Table 2)
collected from three smoked fish processing plants. We isolated L. monocytogenes from 11.5% of finished product samples,
consistent with the prevalence range reported by previous surveys
(6, 21, 27). As L. monocytogenes is a common
contaminant of the food processing environment (6, 16), we
were not surprised that this organism was isolated from over 20% of
our environmental samples.
To specifically investigate L. monocytogenes contamination
patterns and strain progressions in these plants, all isolates were
characterized by molecular subtyping. Our subtyping data, in
combination with statistical analysis, revealed a unique L. monocytogenes contamination pattern for each processing plant. Different ribotypes predominated in the samples collected from each
processor, and specific ribotypes persisted in samples collected over
time (Fig. 1 to 3). In support of a unique contamination pattern for
each processor, the distributions of L. monocytogenes ribotypes DUP-1039C, DUP-1042C, DUP-1045, and DUP-1046B were shown to
vary significantly by processing facility (Table 3) but not according
to sample type. The results for processor D provide the most striking
illustration, as L. monocytogenes DUP-1039C persisted in the
processing environment over the 6-month sampling period and was
isolated from nearly half of the culture-positive samples collected at
this facility (Fig. 3). This ribotype was not isolated from any samples
collected from processors B and C. In contrast, a different subtype
(DUP-1042C) persisted in the environment of processor B over a period
of 5 months (Fig. 1).
The persistence of L. monocytogenes DUP-1042C and DUP-1039C
in the environments of processors B and D, respectively, for at least 5 months suggests that these strains are a part of the resident microflora and are not eliminated by current cleaning and sanitation programs. Previous reports have shown that L. monocytogenes
has the ability to adhere to surfaces and colonize the food processing environment (22, 28, 29, 31). Once these populations are established, they appear to become more resistant to cleaning and
sanitation measures (17, 28, 32). The affected processing areas, therefore, can serve as primary sources of finished product contamination. Our results show that ribotyping provides an effective means for monitoring the persistence of resident populations of L. monocytogenes in the processing environment and
facilitates a better understanding of the ecology of this organism in
food processing facilities. With this information available, the
processor can develop and implement specific programs to eliminate
resident populations and minimize the potential for L. monocytogenes colonization.
The predominance of specific L. monocytogenes subtypes over
time is consistent with findings of previous investigations of contamination patterns in a variety of food processing environments, including those for smoked fish, poultry, meat, and dairy foods (3, 29, 33, 37). The persistence of specific strains in a
variety of processing environments, along with the isolation of
genetically diverse sporadic contaminants, suggests that some strains
might have unique genetic characteristics conferring an enhanced
ability to survive environmental stresses and colonize the food
processing environment. In support of this hypothesis, a recent study
indicated that L. monocytogenes strains differ in
their ability to form biofilms (M. Chae and M. Schraft, Abstr. 99th Gen. Meet. Am. Soc. Microbiol., abstr. P-104, p. 531, 1999). In a
previous study evaluating the relationship between the resistance of
specific strains to commercial sanitizers and their ability to persist
in the processing environment, Earnshaw and Lawrence observed that
while the sensitivity to sanitizers varied significantly among strains
in suspension, there was not a significant difference between strains
which persisted in the poultry processing environment over a 6-month
period and sporadic isolates (14). Further studies will
likely elucidate characteristics that contribute to the apparent enhanced ability of specific subtypes to colonize processing
environments and resist cleaning and sanitation measures.
Potential sources of finished product contamination.
Molecular
subtyping data also provided useful information regarding potential
sources of specific L. monocytogenes strains isolated from
finished product samples. Our subtyping data, in conjunction with our
prevalence results, indicate that both raw materials and the processing
environment serve as potential sources of finished product
contamination. For example, DUP-1039A was isolated from processor B raw
and cold-smoked Chilean salmon but not from the processing environment
(Fig. 1, visit 1), indicating that raw materials likely served as the
source of finished product contamination at the time of sampling. While
results from a study by Eklund et al. also implicated raw fish as an
important source of L. monocytogenes in the smoked fish
processing environment and in finished products (15),
other studies employing molecular typing methods concluded that raw
materials may not serve as a significant source of finished product
contamination (4, 37). Additional comprehensive studies
monitoring contamination of raw fish and finished products using
molecular subtyping methods are needed to clarify the importance of raw
materials as a source of L. monocytogenes in finished products.
Analysis of ribotyping data also provided strong evidence in support of
the processing environment as a significant source of finished
product contamination. L. monocytogenes DUP-1046B, for
example, was isolated from cold-smoked Nova salmon, cold-smoked sablefish, and two floor drain samples collected during the second visit to processor C (Fig. 2). As DUP-1046B was not isolated from any
raw material samples collected from this facility over the 6-month
sampling period, the processing environment most likely served as the
source of this subtype in finished product samples. L. monocytogenes DUP-1039C, which persisted in the processing environment of processor D over the 6-month sampling period, was also
isolated from in-process samples and from five of seven positive cold-smoked fish samples. DUP-1039C was not isolated from raw material
samples (Fig. 3), strongly suggesting that the environment serves as
the primary source of finished product contamination in this processing
facility. Consistent with our results, previous studies employing
discriminatory subtyping methods have identified the processing
environment as a significant source of L. monocytogenes isolated from samples during processing and from finished products (4, 37). Rørvik et al. observed the persistence of a
single electrophoretic type in the processing environment of a smoked salmon processing plant and in finished products, strongly suggesting that the environment served as a primary source of contamination (37). Similarly, analysis of PFGE subtyping data led Autio
et al. to conclude that the contamination of cold-smoked rainbow trout
was most closely linked to sites associated with brining and slicing
(4).
Evaluation of a commercial PCR-based system for detection of
L. monocytogenes.
Conventional culture methods for the
isolation and identification of L. monocytogenes from food
and environmental samples require a minimum of 4 to 5 days to complete
(6, 13, 16). These methods may lead to false-negative
results if mixed populations of Listeria species are present
in a given sample, as most selective plating media do not allow visual
differentiation of L. monocytogenes from other
Listeria spp. (6). Rapid sample screening
methods, including immunochemical, nucleic acid probe-based, and
PCR-based assays, may overcome some of these limitations (5, 13,
23, 40). An increasing number of commercial PCR-based assays are available for the specific detection of L. monocytogenes,
including the BAX for Screening system and the Probelia PCR system
(Sanofi Diagnostics Pasteur). These assays have the potential to
provide rapid and reliable molecular methods for monitoring of L. monocytogenes in the food industry.
We used the BAX for Screening/Listeria monocytogenes system
for monitoring the presence of this organism in raw materials, in-process fish, cold-smoked fish, and environmental samples. Our
results indicate a sensitivity of 91.8% for the BAX system (Table 1).
It appears that our PCR system false-negative results were likely due
to low levels of L. monocytogenes after sample enrichment or
due to a high level of background microflora. Fewer than 3 × 102 Listeria-like colonies (<3 × 103 CFU/ml), below the system detection limit of 1 × 105 CFU/ml (40), were observed on the Oxford
plates for six of the seven BAX system false-negative samples. The
other sample appeared to contain Listeria in a high
background of a mixed bacterial population. Further, pure-culture
L. monocytogenes isolates from all false-negative samples
tested BAX system positive, suggesting that the false-negative results
were not due to the presence of nonreacting isolates. The employment of
a two-step sample enrichment, as recommended by the manufacturer of the
BAX for Screening/Listeria monocytogenes system, may
increase the sensitivity of this system by facilitating recovery and
growth of this organism. We used a single-step enrichment in LEB for
this study based upon reports of comparable or enhanced recovery of
L. monocytogenes from naturally contaminated seafood as
compared to other enrichment protocols (6).
Our results indicated a specificity of 96.2% for the BAX system (Table
1). We believe that the BAX system false-positive results may be due to
the specific detection of L. monocytogenes in a high
background of other Listeria species. As additional Listeria spp. were observed in over half of our
L. monocytogenes-positive samples, it is possible that
this organism was overgrown by competing species during sample
enrichment (resulting in culture-negative screening results). In
agreement with our results, several researchers have observed that
Listeria innocua can outcompete L. monocytogenes if the two species are grown together in commonly used enrichment media, including LEB (30, 35). It is unlikely that
nonspecific priming contributed to the BAX system false-positive
results, as this system has demonstrated 100% exclusivity for 60 Listeria spp. strains (non-L. monocytogenes)
and 44 non-Listeria strains (BAX for
Screening/Listeria monocytogenes package insert,
Qualicon, Inc., Wilmington, Del.). Further, a recent report
indicated that the presence of other Listeria species did
not interfere with the detection of L. monocytogenes by the
BAX system (40).
Conclusions.
Our results indicate that molecular detection and
subtyping methods facilitate a better understanding of the ecology of
food-borne pathogens in the food processing environment. This work
further demonstrates the utility of molecular subtyping, specifically ribotyping, for tracking the sources and spread of food-borne pathogens. Ribotyping was applied in our study because this subtyping method is highly discriminatory, automated, and reproducible from one
laboratory to another, thus facilitating rapid identification and data
sharing among research groups. Although a single typing method can
often elucidate contamination patterns, the use of multiple
typing methods (20), multiple enzymes for ribotyping (19), or other typing methods (e.g., PFGE)
(20) may increase discriminatory power and
provide additional information on contamination patterns. It is also
important to remember that molecular typing methods rely on
culture-based isolation of L. monocytogenes. As it has
been shown that different enrichment procedures may favor the growth of
different subtypes and that multiple subtypes may be present in a given
sample (38), the employment of more than one enrichment
method and subtyping of more than one isolate per sample may facilitate
further elucidation of contamination patterns.
A thorough understanding of strain persistence and progression will be
crucial for improved control strategies for L. monocytogenes. Based on our results, we propose that sanitation
protocols specifically targeting possible reservoirs of persistent
strains may efficiently reduce environmental contamination. Sanitation
control procedures are of particular importance for products that do
not receive a heat treatment sufficient to kill food-borne pathogens,
including L. monocytogenes. Routine environmental monitoring
programs featuring molecular detection and subtyping methods will help
to provide the necessary information regarding the origins and spread
of contaminants to facilitate targeted control and sanitation strategies.
 |
ACKNOWLEDGMENTS |
We are indebted to the smoked fish processors who participated in
this study. We thank Qualicon, Inc., Cornell Research Support Specialist Mary Bodis, and the members of the Food Safety Laboratory for their expert technical advice and assistance.
This paper is a result of research funded by the National Oceanic and
Atmospheric Administration (award NA86RG0056 to the Research Foundation
of State University of New York for New York Sea Grant).
 |
FOOTNOTES |
*
Corresponding author. Mailing address: Department of
Food Science, 412 Stocking Hall, Cornell University, Ithaca, NY 14853. Phone: (607) 254-2838. Fax: (607) 254-4868. E-mail:
mw16{at}cornell.edu.
 |
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0099-2240/01/$04.00+0 DOI: 10.1128/AEM.67.1.198-205.2001
Copyright © 2001, American Society for Microbiology. All rights reserved.
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