• TABLE OF CONTENTS
HIDE
 Copyright
 Title Page
 Acknowledgement
 Table of Contents
 List of Tables
 List of Figures
 Abstract
 Introduction
 Materials and methods
 Results and discussion
 Summary and conclusions
 Bibliography
 Biographical sketch
 Signature page






Title: The incidence of Salmonella in four fish and shellfish species harvested in Florida
CITATION PAGE IMAGE ZOOMABLE PAGE TEXT
Full Citation
STANDARD VIEW MARC VIEW
Permanent Link: http://ufdc.ufl.edu/UF00074944/00001
 Material Information
Title: The incidence of Salmonella in four fish and shellfish species harvested in Florida
Physical Description: viii, 57 leaves : ill. ; 28 cm.
Language: English
Creator: Fraiser, Margaret Bury, 1959-
Publication Date: 1982
 Subjects
Subject: Salmonella   ( lcsh )
Seafood -- Microbiology   ( lcsh )
Fishes -- Microbiology -- Florida   ( lcsh )
Shellfish -- Microbiology -- Florida   ( lcsh )
Food Science and Human Nutrition thesis M.S
Dissertations, Academic -- Food Science and Human Nutrition -- UF
Genre: bibliography   ( marcgt )
non-fiction   ( marcgt )
 Notes
Thesis: Thesis (M.S.)--University of Florida, 1982.
Bibliography: Bibliography: leaves 51-56.
Statement of Responsibility: by Margaret Bury Fraiser.
General Note: Typescript.
General Note: Vita.
Funding: Electronic resources created as part of a prototype UF Institutional Repository and Faculty Papers project by the University of Florida.
 Record Information
Bibliographic ID: UF00074944
Volume ID: VID00001
Source Institution: University of Florida
Holding Location: University of Florida
Rights Management: All rights reserved, Board of Trustees of the University of Florida
Resource Identifier: aleph - 000319030
oclc - 09263082
notis - ABU5880

Table of Contents
    Copyright
        Copyright
    Title Page
        Page i
    Acknowledgement
        Page ii
    Table of Contents
        Page iii
        Page iv
    List of Tables
        Page v
    List of Figures
        Page vi
    Abstract
        Page vii
        Page viii
    Introduction
        Page 1
        Page 2
        The genus salmonella
            Page 3
            Page 4
            Page 5
            Page 6
            Page 7
            Page 8
            Page 9
            Page 10
            Page 11
            Page 12
        Microflora of seafoods
            Page 13
            Page 14
        Relationship of salmonella to indicator organisms
            Page 15
        Survival of salmonella during storage
            Page 16
            Page 17
    Materials and methods
        Page 18
        Materials
            Page 18
        Sampling plan
            Page 18
        Samples
            Page 19
        Salmonella analysis
            Page 19
        MPN studies
            Page 20
            Page 21
            Page 22
        Storage studies
            Page 23
        Sediment samples
            Page 23
        Aerobic plate count
            Page 23
        Coliform analysis
            Page 24
        Statistical analysis
            Page 24
    Results and discussion
        Page 25
        Salmonella analysis results
            Page 25
            Page 26
            Page 27
            Page 28
            Page 29
            Page 30
            Page 31
            Page 32
            Page 33
            Page 34
            Page 35
            Page 36
            Page 37
            Page 38
        Relationship to total coliform, fecal coliform, and aerobic plate count
            Page 39
            Page 40
            Page 41
        Salmonella as a contaminant or an autochthon
            Page 42
            Page 43
            Page 44
        Significance of the findings
            Page 45
            Page 46
            Page 47
    Summary and conclusions
        Page 48
        Page 49
        Page 50
    Bibliography
        Page 51
        Page 52
        Page 53
        Page 54
        Page 55
        Page 56
    Biographical sketch
        Page 57
    Signature page
        Page 58
Full Text


Print Form





Internet Distribution Consent Agreement

In reference to the following dissertation:

Author: Margaret Bury Fraiser


Title: The incidence of salmonella in four fish and shellfish species harvested in Florida


Publication Date: 1982


I, Margaret B. Fraiser as copyright holder for the
aforementioned thesis or dissertation, hereby grant specific and limited archive and
distribution rights to the Board of Trustees of the University of Florida (hereinafter, the
"UF") and its agents.

This is a non-exclusive grant of permissions for specific off-line and on-line uses for an
indefinite term. Off-line uses shall be limited to those specifically allowed by "Fair Use"
as proscribed by the terms of United States copyright legislation (cf, Title 17, U.S. Code)
as well as to the maintenance and preservation of a digital archive copy. Digitization
allows the University of Florida to generate image- and text-based versions as appropriate
and to provide and enhance access using search software, acting on behalf of the
University of Florida, to digitize and distribute the thesis or dissertation described, above
for nonprofit, educational purposes via the Internet or successive technologies.



This grant of permissions prohibits use of the digitized versions for commercial use or
profit.


Signature of Copyright Holder

Margaret Bury Fraiser
Printed or Typed Name of Copyright Holder/Licensee

2640 NW 39th Ave Gainesville, FL 32605
Printed or Typed Address of Copyright Holder/Licensee

352-378-1800 Doug-Meg_Fraiser@sil.org
Printed or Typed phone number and email address of Copyright Holder/Licensee

27 March 2007
Date of Signature
















THE INCIDENCE OF SALMONELLA IN FOUR FISH
AND SHELLFISH SPECIES HARVESTED IN FLORIDA










BY
MARGARET BURY FRAISER






















A THESIS PRESENTED TO THE GRADUATE COUNCIL
OF THE UNIVERSITY OF FLORIDA IN
PARTIAL FULFILLMENT OF THE REQUIREMENTS
FOR THE DEGREE OF MASTER OF SCIENCE


UNIVERSITY OF FLORIDA


1982














KKNCWLEDXGWENTS

The author wishes to thank Dr. John A. Koburger, her advisor, for

his guidance and encouragement in this project. She is thankful for his

knowledge of the subject and patience in teaching her. Appreciation is

also extended to Dr. James L. Oblinger and Dr. Samuel R. Farrah for

their advice and assistance during the research and thesis preparation.

Appreciation is expressed to the National Fisheries Institute for

financial support during this and other related projects. Thanks are

also given to Mary Miller for her willingness to listen and to share

materials.

Finally, the author thanks her parents for their encouragement and

financial support throughout her education and her husband for his

love, support, meal preparation, and word processor knowledge.














TABLE CF CONTENTS

PAGE

A KNO< C LEDGBENTS ..................................................... ii

LIST CF TABLES....................................................... v

LIST CF FIGURES .....................................................vi

ABSTRCT. ...................................................... vii

INTRODUCTION ....................... .................................
The Genus Salmonella............................................. 3
Disease ............. .......................... ............4
Prevention ................................... ..........4
Infective Dose ................................. .. ...... 5
Incidence........ ........ ................................. 6
Ecology ..................... ................ .10
Microflora of Seafoods............................. ...... 13
Relationship of Salmonella to Indicator Organisms................15
Survival of Salmonella During Storage.......................... 16

MTERIALS AND nETHDDS............................................... 18
Materials.............. ..... ......... ....... .. .. ............ 18
Sampling Plan.......................... ... ......................18
Samples....o. ........ ....... ......... ... ........... ...... ......19
Salmonella Analysis.................. ......................... 19
VPN Studies .................................................... 20
Storage Studies............ ............................ ........ 23
Sediment Samples..................................................23
Aerobic Plate Count............................................. 23
Coliform Analysis .......... ...... .... .................. ...........24
Statistical Analysis ......... ... ... .... ............. ..... .......24

RESULTS AND DISCUSSION..............................................25
Salmonella Analysis Results......o............................25
Isolation of Salmonellae from Various Seafoods ...........25
MPN Studies....................o...........................30
Storage Studies ...................... ........... .... 32
Serotypes........... .................. ........ ...........32
Isolation Methodology.....................................38
Relationship to Total Coliform, Fecal Coliform, and
Aerobic Plate Count.................. .......................39
Salmonella as a Contaminant or an Autochthon....................42
Significance of the Findings....................................45

SULMRY AND 3NCLLU6IONS ............................................. 48

iii








PAGE
BIBLIOGRAPHY ........................................................51

BIOGRAPHICAL S












LIST OF TABLES


TABLE PAGE

1. MIDFLCR RA CF CYSTERS AND BLLE CRABS............................. 14

2. BIOCHYMIICAL TESTS PERFCRED FTR ISCLATICN CF SALMONELLA .......... 21

3. BASIS FCR DISCARDING ISOLATES....................................22

4. SALM3NELLAE RECOVERED FRCM FOLR SEAFIODS.. .....................26

5. NMST ROBABLE NULBER F SAILNNELLAE PRESENT IN OfSTERS...........31

6. M3ST PROBABLE NUMBER CF SALIDNELLAE
PRESENT IN FRESH--WATER CLAMS ................................. 33

7. SALM NELLA SEROTYPES PREVIOUSLY REPORTED FICM SEAFODS........... 34

8. SERCLOGICAL IDENTIFICATION CF ISCLATES
FRCM FKR SEAICODS AND SEDINENT................................36

9. THE TEN M3ST FREQUENTLY REPORTED SALM3NELLAE
SERDTYPES FRCM HVMAN AND NONHLMAN SOXCES, 1979 ..................37

10. AEROBIC PLATE (DLNT, TOTAL CCLIFCRM, FECAL CCLIFCRM, AND
SAMIDNELLAE RECOVERED FCM IFOLR SEAFOODS......................... 40














LIST OF FIGURES


FIGURE PAGE

1. REPORTED SALWVNELLA ISOLATIONS FRCM HLMNS
BY WEEK IN THE LNITED STATES, 1974-1980..........................7

2. REF RTED SALMNELLAISCLATIONS HiCM HUINS
BY PE IN THE UNITED STATES, 1980..............................9

3. MODE OF TRANSMISSION CF SAIMDNELLOSIS ...........................11

4. ANIMML-TO-MAN TRANSMISSION OF SALM3NELLOSIS.....................12













Abstract of Thesis Presented to the Graduate Council
of the University of Florida in Partial Fulfillment of the
Requirements for the Degree of Master of Science


THE INCIDENCE OF SALMONELLA IN FOR FISH
AND SHELLFISH SPECIES HARVESTED IN FLCRIDA

By

Margaret Bury Fraiser

December 1982

Chairman: John A. Koburger
Major Department: Food Science and Human Nutrition

Members of the genus Salmonella are important etiological agents in

foodborne disease outbreaks in the United States and have often been

recovered from seafoods. In order to gain information on the distribu-

tion of these organisms in seafoods harvested in Florida, the incidence

of Salmonella was studied in four seafoods: clams (Mercenaria mercenar-

ia), oysters (Crassostrea virginica), mullet (Mugil cephalus), and blue

crabs (Callinectes sapidus). These were harvested from two locations in

Florida; the west coast location was at the mouth of the Suwannee River

and the east coast location was in the Intracoastal Waterway at Crescent

Beach. In addition, fresh-water clams (Polymesoda caroliniana) and sedi-

ment obtained at the west coast location were analyzed for Salmonella.

Determination of salmonellae was performed using the standard pro-

cedures of the United States Food and Drug Administration for the analy-

sis of salmonellae in food products. To determine the degree of contami-

nation, a quantitative study of Salmonella in west coast oysters and

fresh-water clams was performed. In addition, a storage study to







investigate the survivability of Salmonella under commercial storage

conditions was also conducted.

Results indicated that salmonellae were present in oysters, clams,

and blue crabs in percentages of 8.3%, 28.3%, and 33.3% of the samples

analyzed, respectively. Salmonellae were not recovered from any mullet

samples. Sediment samples taken in the vicinity of the west coast har-

vest location also contained salmonellae. The serotypes recovered were

those which are less frequently reported to the Centers for Disease Con-

trol as agents in human salmonellosis, which may reflect their lesser

virulence. Quantitation of salmonellae in oysters and fresh-water clams

using the most probable number technique yielded low numbers, ranging

from 2.2 to 16.0 salmonellae per 100 grams sample. Storage tests showed

that Salmonella were capable of surviving in oysters and fresh-water

clams at refrigerated temperatures for ten days. Aerobic plate counts,

total coliform estimates and fecal coliform estimates showed no apparent

correlation with the incidence of salmonellae.

This study indicates that salmonellae may be autochthonous members

of the microflora of these seafoods based on the wide distribution, the

low numbers recovered, the variety of the serotypes recovered and the

lack of correlation with fecal coliform analyses. Under normal handling,

processing, and storage conditions, consumption of these seafood prod-

ucts may not cause salmonellosis in the majority of the human United

States population due to the low numbers of salmonellae isolated, the

destruction of salmonellae during the cooking process, the unfavorable

pH of the stomach, and/or the presence of less virulent serotypes.




Chai


viii













INTRODUCTION

Seafoods accounted for 8.7% of the reported foodborne disease

outbreaks in the United States in 1979 (10). With the dockside value of

seafoods landed in Florida at approximately 173 million dollars (48),

there is both an economic and an etiological need to study the presence

of pathogens within these products. Historically, Salmonella typhi was

the major pathogen isolated from seafoods. For instance, in 1925, 150

deaths and thousands of cases of typhoid fever were due to the presence

of salmonellae in oysters (25). Other pathogens are now commonly found

in seafoods (e.g., nonagglutinating Vibrio cholerae and Clostridiun

botulinum), in addition to opportunistic pathogens ( e.g., Vibrio

parahaemolyticus, enteroviruses, Pseudomonas aeroginosa, and Aeromonas

hydrophila) which are being recognized with greater frequency. Because

of the increase in reporting of foodbone disease associated with

seafood, stricter microbiological guidelines are being considered for

harvesting areas and seafood products, placing pressure on both the

seafood industry and the federal government. In an attempt to better

understand this problem, additional data concerning the presence and

distribution of pathogens in seafoods would be helpful in dealing with

this problem.

Members of the genus Salmonella are the primary etiological agents

in foodborne disease outbreaks in the United States (10). In 1979 the

genus Salmonella produced 40% of all confirmed foodborne cases and 29%

of all confirmed outbreaks. The prevalence of the disease can only be






2

estimated because the reported infections are estimated to be only a

fraction of the total number. It is postulated that about 1% of the

salmonellosis cases are reported (13); in 1980 there were 33,715 cases

reported, making the total estimated cases in the United States well

over 3 million. This low rate of reporting is probably a result of a

low fatality rate and an illness which is frequently mild and

self-limiting. In addition, salmonellosis can not be accurately

diagnosed on clinical grounds alone, leaving many cases unreported,

particularly those which are not associated with a recognized

food-poisoning outbreak. Although salmonellosis may appear to be a

relatively harmless disease, it is responsible for substantial costs in

the form of medical care, hospitalization, and lost income due to

absence from work. The total cost of salmonellosis in 1969 was

estimated to be at least $300 million (49). Salmonellosis is also

potentially fatal to the old, the very young, and the infirm. Because

of the ease of transmission between both humans and animals, the

control of salmonellosis is complex.

The purpose of this study was to investigate the incidence of Sal-

monella in four fresh seafoods commercially harvested in Florida: oys-

ters (Crassostrea virginica), clams (Mercenaria mercenaria), striped

mullet (Mugil cephalus), and blue crabs (Callinectes sapidus). Salmo-

nella was chosen as a representative of the pathogenic microflora be-

cause it is an established overt pathogen, it is associated with the

estuarine environment, and standarized methodology for its detection is

available. In an attempt to obtain a more representative sampling of

the seafoods harvested in Florida, the seafoods were harvested from two

approved areas in Florida; the west coast location was at the mouth of






.3

the Suwannee River and the east coast location was in the Intracoastal

Waterway at Crescent Beach.

The Genus Salmonella

The genus Salmonella, a member of the family Enterobacteriaceae,

now contains over 1800 serotypes with the rrst prominent member of the

genus being Salmonella typhi, the causal agent of typhoid fever. The

genus can be divided into three classifications, based on their patho-

genicity for various animals:

1. Salmonellae pathogenic to man only

e.g. S. typhi and S. paratyphi

2. Salmonellae pathogenic to animals only

e.g. S. pullorum and S. abortus equi

3. Salmonellae pathogenic to man and animals

It is this last classification which contains the vast majority of ser-

otypes. In man, these species are the major cause of food infections

(6). The genus is further classified into groups A through I based on

their O (somatic) antigens. The serotypes (or species) within each of

these groups are based on the H (flagellar) antigens.

Salmonellae (50) are gram negative, generally motile, generally

produce abundant amounts of hydrogen sulfide, and generally do not

ferment lactose or sucrose. They are capable of growth between 7 and

45 C with optimal growth at 35 to 37 C. The pH range for growth is 4.1

to 9.0 with an optimum of pH 6.5 to 7.5. The lowest water activity at

which growth occurs is 0.94, which is equivalent to a 9% NaCI solution.

The D value, which is the amount of time at a particular temperature

needed to reduce the number of organisms by one log10 cycle, is given

as 0.4 minutes at 140 F for egg products. The D values can vary greatly






4.

among strains and can.be influenced strongly by pH, sugar or salt

content, and the physiological state of the cells. The genus has shown

an ability to survive for relatively long periods of time in chilled,

frozen, or dried foods and feeds. Salmonellae have also been found to

persist for prolonged periods at ambient temperatures in dried nonfat

milk, egg products, and rendered animal byproducts (50).

Disease

There are four typical disease syndromes associated with the genus

Salmonella, which are enteric fever, septicemia, gastroenteritis, and a

carrier state. Only one of these, gastroenteritis, is commonly caused

by ingestion of contaminated foods, although gastroenteritis can occa-

sionally progress into the other syndromes. The gastroenteritis, called

salmonellosis, will begin to occur 8 to 48 hours after ingestion of the

salmonellae. The symptoms usually include fever, cramps, diarrhea, and

vomiting, which are caused by invasion of the muscosal layer of both

the small and large intestines. The gastroenteritis is self-limiting

with a duration of three to four days and the degree of severity of the

disease is variable, depending on the infecting dose, serotype, and the

health of the individual. Treatment includes administration of fluids

and electrolytes. Occasionally septicemia will develop, resulting in a

localized infection of the gall bladder, spleen, lungs, or urinary

tract (50). In 0.5 to 2% of the salmonellosis patients a carrier state

develops which may last for years (24). This is often characterized by

a chronic infection of the gall bladder.

Prevention

Prevention of salmonellosis is mainly accomplished by the adher-

ence to public health standards. Proper sewage disposal, pasteurization






5

of milk, maintenance .of unpolluted water supplies, and exclusion of

carriers as food handlers are common measures exercised in the

developed world. On an individual level, personal hygiene is helpful in

prevention of salmonellosis.

Infective Dose

The infective dose has been disputed since 1951, when McCullough

and Eisele reported doses in the range of 105 to 109 bacteria were

needed for human infection (43, 44, 45). McCullough and Eisele also

reported differences in the infective doses between serotypes and

strains; this was thought to be due to a difference in the virulence of

various serotypes (43, 44, 45). Because this is the only research re-

ported using human subjects, these figures have been used repeatedly

and are still in use today. Epidemiologic studies from salmonellosis

outbreaks, however, have shown doses causing the disease to be much

smaller. An outbreak in 1973 involving chocolate revealed a total con-

tamination of fewer than 100 salmonellae for a primary case of

infection (17). In an outbreak involving ground beef, there were only

6-23 viable salmonellae per 100 grams upon epidemiological analysis of

the frozen sample (23). Experience shows, however, that there is a re-

duction in the number of viable organisms after freezing, which would

increase the number of viable salmonellae in the meat at the time of

ingestion as much as 100-fold (71). In the case of ground beef, it is

unlikely that a person who contracted salmonellosis from this product

would have eaten 100 grams of raw meat, although the amount may have

been larger if the contaminated meat was cooked rare, which may not

kill salmonellae. In other cases, frozen eggs were found to have an

infective dose of 0.6 salmonellae per gram, cereal products had 7 to 14







salmonellae per gram, and ice cream had an infective dose of 2

salmonellae per gram. It can be seen from the above epidemiological

studies that the tolerance to salmonellae varies with the food product

and the person involved. Because of this, regulatory agencies forbid

the sale of foods which contain any salmonellae. Exceptions to this are

red meats and poultry, which often have high percentages (30%) of

contamination (57). These products, being integral parts of the food

chain, are difficult to rid of salmonellae. Because of this and the

fact that these products will commonly be cooked, destroying the

salmonellae, the United States Department of Agriculture has made an

exception, allowing salmonellae to be present in red meats and poultry

sold in the United States if the salmonellae are considered inherent in

the product.

Incidence

The incidence of salmonellosis has been steadily increasing in the

United States since the beginning of surveillance in 1950 (11) and has

continued to increase in recent years as shown in Figure 1 (11). Some

of this increase must be attributed to more effective monitoring and

reporting of the disease, although the extent of this contribution can-

not be established. In cases per 100,000 population, however, a slight

decrease was seen in 1980, from 15.06 in 1979 to 14.88 in 1980 with

33,715 cases of salmonellosis reported in 1980. It is estimated that

approximately 1% of the total salmonellosis cases are reported (13),

indicating the total cases in 1980 to be well over 3 million. In Figure

1, the seasonal fluctuation in the incidence is apparent, with the sum-

mer months having higher incidences. This may be the result of the in-

crease in thermally mishandling of foods which occurs more readily in


































2 -

4 700
.-
0
'L 600


w soo
CO 500

400
>J

300


200


< 100


rA ; lU J 4's 0111O r sono rur 77".Tnl=" .-'. "O'J' IT-C "s oJ rUnMAM oJ J SCN AJJ
1974 1975- 1976 1977 1978 1979 1980
SEach po'nt r.prespt ts the w~vpklv averaqr number)* r.l ,olatps for tho month








FIGURE 1
REPORTED SALMONELLA ISOLATIONS FROM HUMANS
BY WEEK IN THE UNITED STATES, 1974-1980






8

the sumner months. Salmonella is now the most cormnon etiological agent

of foodborne disease in the United States.

The reported isolations of Salmonella from humans by age in the

United States -s 1980 is shown in Figure 2 (11). The very high

incidence in children less than one year old can be attributed to sev-

eral factors, including low immunity, higher incidence of examination,

and the increased probability of transmission by the fecal/oral route.

Another increase in the incidence can be seen in the elderly; this in-

crease is due to aging which causes a decrease in resistance to such

organisms.

Another indication of the severity of salmonellae is shown in the

number of deaths attributed to the disease. Deaths due to salmonellosis

reported in the United States in the nine year period from 1970 to 1979

totaled 645 with the highest number of deaths in one year being in 1970

and 1971 with 81 deaths in each year. The lowest number of deaths was

in 1974 with 59 deaths being reported.

In Canada, it is of interest to note that in 1977 the foodborne

illnesses due to Salmonella species exceeded those caused by all other

microbiological genera. This is in contrast to the 1976 figures, which

show Staphylococcus aureus responsible for more outbreaks and cases

(9). In 1976, there were 356 salmonellosis cases reported involving 23

outbreaks. In that same year, there were 520 cases involving 25

outbreaks reported due to Staphylococcus aureus. In 1977, however,

there were 763 cases of salmonellosis reported involving 32 outbreaks

with 305 cases involving 22 outbreaks pertaining to Staphylocuccus

aureus reported (9). These figures illustrate the importance of Salmo-

nella as a foodborne pathogen in another area of the developed world.





















70-


300
60-
--- MALE 200-
S-- .- FEMALE 2

50- 100-


<1' 2 4 5 6 7 8 9 10 11
. 40- AGE (MONTHS)
I- I
0

30-




20-




10





0-4 5-9 10-19 20-29 30-39 40-49 50-59 60-69 70-79 80
AGE GROUP (YEARS)

'PER 100,000 POPULATION





FIGURE 2
REPORTED SALMONELLA ISOLATIONS FROM HUMANS
BY AGE IN THE UNITED STATES, 1980







Ecology

Salmonella is ubiquitous in the environment, being one of the. most

widely distributed overt pathogens in the world. The main reason for

this ubiquity is the easy transmissibility of the organism. Transmis-

sion of salmonellae can be through a variety of means (5): animal to

animal, animal to man, man to man, man to animal, or a common source to

both animals and man. The mode of transmission in 500 salmonellosis

outbreaks from 1966 to 1975 is given in Figure 3 (57). The most common

of these transmissions was the animal to man, in which red meats and

poultry play a large part as illustrated in Figure 4 (5). A circular

pattern can be seen by noting that the byproducts of processing plants,

which are often contaminated with salmonellae, are the main ingredients

of animal feeds. Another reason for the ubiquity of Salmonella is the

apparent capacity of the genus to survive for prolonged periods in the

estuarine environment. For example, Salmonella in oysters have been

reported to have survived in artificial brackish water for forty-nine

days (33).

The Centers for Disease Control (CDC) now believes that much of

the human salmonellosis is directly or indirectly related to Salmon-

ella-contaminated animal feeds (56). Epidemiolgical evidence that

supports this position is growing, as seen particularly by the rise in

the recovery of two serotypes, S. agona and S. hadar. Before 1970, S.

agona had been reported in man only twice. One of the first isolations

of the serotype in the United States was due to contaminated Peruvian

fishmeal. After this, S. agona was isolated more frequently from

non-human sources, followed by an increase in isolations from human

sources. In 1976 it ranked third among the most frequently isolated













































INCLUDES OVER 50 VEHICLES WHICH INDIVIDUALLY
CAUSED LESS THAN 3% OF OUTBREAKS







FIGURE 3
MODE OF TRANSMISSION OF SALMONELLOSIS













CONTAMINATED AI

AND CFRTILIZER





ILTRY INI CTPD ON
FEW INFECTED ON


NV/AL FEED


FARM


MANY INFECTED IN LAIRAGE,POULTRY
PROCESSING PLANTS AND ABATTOIRS

V


BULK EGG PRODUCTSl


IFOWL AND MEATI


CO sJ 5J mED

MAN AND WIS 4


4r f
LOCAL
UNPASTEURPJZED
MIK PRODUCTS
<


DOMESTIC ANIMALS


FIMGRE 4
ANIMAL-TO-MAN TRANSMISSION OF SALMONELLOSIS


I


B





13

serotypes from human sources. S. hadar has been accidentally imported

by a turkey breeder from the United Kingdom. A rapid increase in.the

early 1970s was seen in the LK much like that of S. agona in this

country due to recycling of waste products from processing plants. The

increase in the LK has lead to an increase in the United States,

although the numbers of isolates have been smaller.

There has been little study of the incidence of salmonellae in the

marine environment. It is realized that turtles are a major carrier of

Salmonella and therefore the Food and Drug Administration has

prohibited interstate shipment of turtles. Nine serotypes were isolated

from water in aquaria housing turtles (40). In another study, seagulls

were found to contribute a new serotype to a water environment (52).

Reptiles, also present in the aquatic environment, have been found to

be contaminated with salmonellae while living in Swiss zoos. Thirty

percent of the reptiles in the Basel zoo, 43% of those in the Bern zoo,

and 30% of reptiles in the Zurich zoo were positive for salmonellae

(54). Salmonellae have also been isolated from oysters (3, 60), clams

(2), shrimp (18), cockles (34), and lalakupong (34). In addition,

salmonellae have been isolated from marine waters (2, 3, 27, 36, 60)

and sediment (26).

Microflora of Seafoods

In addition to the Salmonella serotypes already mentioned, many

overt pathogens and opportunistic pathogens have been reported to be

present in seafoods. Table I gives a brief summary of the microbes that

have been isolated from oysters and blue crabs. These organisms have

not been reported in mullet or clams.










TABLE 1
MICRDFLCRA OF THE SEAFOODS STUDIED
ORGANISM SEAFOOD LOCATION
Vibrio parahaemolyticus oyster Mississippi Sound
blue crab Chincoteague Bay
oyster laboratory
oyster Long Island Sound
blue crab unknown
Pseudomonas spp. blue crab unknown
oyster Long Island Sound
oyster laboratory
oyster Galveston Bay
Flavobacterium-Cytophaga oyster Long Island Sound
blue crab unknown
oyster Galveston Bay
oyster laboratory
Achromobacter-Alcaligenes oyster Long Island Sound
oyster laboratory
oyster Galveston Bay
Bacillus blue crab unknown
oyster laboratory
oyster Galveston Bay
Acinetobacter blue crab unknown
oyster Galveston Bay
Aeromonas oyster Galveston Bay
Moraxella oyster Galveston Bay
Coryneforms oyster Galveston Bay
Vibrio cholerae oyster Apalachicola Bay
Clostridiun botulinum type F blue crab York River, VA


REFERENCE
38
35
46
47
59
59
47
46
67
47
59
67
46
47
46
67
59
46
67
59
67
67
67
67
29
69





15

Relationship of Salmonellae to Indicator Groups

The use of specific groups of microorganisms to indicate the pos-

sible presence of pathogenic organisms had its beginning near the turn

of the twentieth century (30). The purpose of these indicator organ-

isms was to detect the presence of sewage contamination in the potable

water supply. Twenty years later, indicators were found to be of use in

the shellfish industry, where bacteriological standards for harvest

waters were being developed. Advantages of utilyzing these indicator

organisms included the relative ease and short duration of the analy-

ses. In 1946, the first quantitative guideline for coliform counts in

water from harvesting areas was established, which placed a limit of

seventy organisms per 100 rrL water. This was modified slightly in 1965,

and in 1974 the fecal coliform limit of fourteen organisms per 100 rrL

water was established. Presently either limit is accepted by the Food

and Drug Administration (30).

Problems have arisen with the use of indicator organisms, since

there is no single group which contains all the desirable characteris-

tics of an indicator. One of the first problems arose in 1961 when a

study by Tennant and Reid (64) found that 26.7% of the coliform organ-

isms did not ferment lactose with acid and gas in 48 hours at 35.5 C.

Many studies have shown the poor correlation of coliforms and/or fecal

coliforms to the presence of pathogenic organisms (18, 41, 55, 58) as

well as the poor correlation of pollution to pathogenic organisms (14,

55). Attempts have been made (2, 3, 55) to determine the best indicator

group to use in the seafood industry; these studies have yielded con-

trasting results. In general, however, fecal coliforms have been found

to be slightly better indicators than total coliforms (2, 3, 41, 60).






16

Other emerging microbial problems have also complicated interpre-

tation of the results of indicator organisms. No correlation has been

seen between fecal coliforms and Vibrio cholerae (15, 28, 35, 37), an

emerging problem with shellfish. In addition, Hood (28) found that

Vibrio cholerae was able to survive for longer periods in estuarine

waters than fecal coliforms. For increased safety, it is advantageous

for indicator organisms to survive longer than the anticipated patho-

gen. Also, the increased incidence of enteroviruses in oysters has

caused Ellender et al. in 1980 (21) to suggest the use of a viral analy-

sis of shellfish as an adjunct to bacteriological analyses so that

shellfish safety is verified.

Another problem concerning the microbial regulation of harvesting

waters is the question of whether shellfish concentrate microorganisms.

This is reflected by the FDA's limit of 230 fecal coliforms per 100 rL

of shellfish, which is sixteen times greater than the limit allowed

for waters. It is generally agreed that shellfish have the ability to

concentrate organisms from overlaying waters (8, 21, 31); however, it

is not agreed whether this is of major sanitary importance (31, 58).

Therefore, water and sediment analyses must be interpreted with

caution. In addition, Presnell and Miescier (53) found that wild

ammrals and birds were the most likely sources of coliforms and fecal

coliforms in water and sediment. They expressed the need to ascertain

the presence of warm-blooded wildlife in areas adjacent to shellfish-

growing areas.

Survival of Salmonellae During Storage

It is of interest to the seafood industry to consider the surviv-

ability of Salmonella species during commercial handling and storage






17

conditions. Although no intensive studies have been conducted

pertaining to this subject, several studies have given indications-of

the survivability of salmonellae within seafoods and nonseafoods. In

nonseafood products, salmonellae survived less than ten days at 5 to

7 C in ground rabbit meat (62), and in a study involving "soul foods",

S. typhimurium survived for five days at 10 C in all foods studied,

which included collard greens, field peas, sweet potatoes, and semi-

processed pig offals (61). In seafoods, Kelly and Arcisz (39) found

that S. typhosa remained viable within the bodies or shell liquors of

oysters long enough to cause illness when oysters are eaten within the

"usual period" elapsing between the time they are removed from the

infected water and the time they are consumed. Salmonellae were

isolated from the shell liquor of oysters after refrigeration at 5 C

for forty-nine days. In a study evaluating depuration techniques (33),

S. typhimurium was found to persist in oysters for the entire

forty-nine days of the experiment. This was noteworthy in that

depuration procedures currently in use for commercial oysters are based

on the removal of fecal coliforms within 48 hours and may be deceptive

and 'ineffective in removing some human waterborne disease organisms.

In a storage study of oysters conducted at 20 to 25 C, S.. typhimurium

and S. senftenberg were detected until the sixteenth day of storage

(65). Collectively, these results support the hypothesis that

salmonellae can survive normal handling procedures practiced in the

seafood industry today.














MATERIALS AND METHODS

Materials

All microbiologcial culture media were obtained dehydrated from

Difco Laboratories (Detriot, MI) or Baltimore Biological Laboratories

(Cockeysville, MD). Media were prepared according to directions and

were at ambient temperature before inoculation, with the exception of

pour plates. Salmonella antisera were obtained from Fisher Scientific

Co. (Pittsburgh, PA) or Difco Laboratories (Detroit, MI).

All glassware was sterilized at 121 C for thirty minutes using wet

heat or at 170 C for one hour using dry heat.

Sampling Plan

The number of samples of each animal from each coast required for

analysis was dependent on a variety of factors. Because of the

pathogenicity of Salmonella and the zero tolerance in foods, the

sampling plan needed to be relatively stringent. If the food is to be

consumed raw, as clams and oysters frequently are, Salmonella is

considered a direct hazard in foods and therefore the sample size

recommended by the International Carnission on Microbiological

Specifications for Foods should be at least thirty for investigative

purposes (32). Based on this information, thirty animals of each

species and from each coast were analyzed, for a total of 240

individual samples.














MATERIALS AND METHODS

Materials

All microbiologcial culture media were obtained dehydrated from

Difco Laboratories (Detriot, MI) or Baltimore Biological Laboratories

(Cockeysville, MD). Media were prepared according to directions and

were at ambient temperature before inoculation, with the exception of

pour plates. Salmonella antisera were obtained from Fisher Scientific

Co. (Pittsburgh, PA) or Difco Laboratories (Detroit, MI).

All glassware was sterilized at 121 C for thirty minutes using wet

heat or at 170 C for one hour using dry heat.

Sampling Plan

The number of samples of each animal from each coast required for

analysis was dependent on a variety of factors. Because of the

pathogenicity of Salmonella and the zero tolerance in foods, the

sampling plan needed to be relatively stringent. If the food is to be

consumed raw, as clams and oysters frequently are, Salmonella is

considered a direct hazard in foods and therefore the sample size

recommended by the International Carnission on Microbiological

Specifications for Foods should be at least thirty for investigative

purposes (32). Based on this information, thirty animals of each

species and from each coast were analyzed, for a total of 240

individual samples.














MATERIALS AND METHODS

Materials

All microbiologcial culture media were obtained dehydrated from

Difco Laboratories (Detriot, MI) or Baltimore Biological Laboratories

(Cockeysville, MD). Media were prepared according to directions and

were at ambient temperature before inoculation, with the exception of

pour plates. Salmonella antisera were obtained from Fisher Scientific

Co. (Pittsburgh, PA) or Difco Laboratories (Detroit, MI).

All glassware was sterilized at 121 C for thirty minutes using wet

heat or at 170 C for one hour using dry heat.

Sampling Plan

The number of samples of each animal from each coast required for

analysis was dependent on a variety of factors. Because of the

pathogenicity of Salmonella and the zero tolerance in foods, the

sampling plan needed to be relatively stringent. If the food is to be

consumed raw, as clams and oysters frequently are, Salmonella is

considered a direct hazard in foods and therefore the sample size

recommended by the International Carnission on Microbiological

Specifications for Foods should be at least thirty for investigative

purposes (32). Based on this information, thirty animals of each

species and from each coast were analyzed, for a total of 240

individual samples.






19

Samples

Thirty samples of each seafood (oysters, clams, mullet, and crabs)

were harvested between August 1981 and August 1982, from both a west

coast location and an east coast location within the state of Florida.

The west coast location was at the mouth of the Suwannee River and the

east coast location was in the Intracoastal Waterway 500 meters south

of the bridge on State Road 206 in Crescent Beach. Crabs were harvested

by trapping, oysters by tonging, and clams by digging. The mullet were

fresh whole commercial samples purchased in the vicinity of the

sampling locations (Suwannee, FL and St. Augustine, FL), and had been

iced prior to transportation to the laboratory. Eighteen of the thirty

east coast crabs were purchased live in St. Augustine and were not iced

during transportation. The samples were transported to the laboratory

at the University of Florida (Gainesville) in sanitized insulated

coolers with analysis begun within four hours of harvest or purchase.

No attempt was made to cool the samples (with the exception of the

mullet) because of the short time span involved between collection and

analysis.

Salmonella Analysis

The method for isolation of Salmonella generally followed the

Bacteriological Analytical Manual (B4M) (66) as follows. Individual

shellfish were blended for two minutes at 8000 rpm in a 1:10 dilution

using lactose broth. Crab weighing over 100 grams were blended with

lactose broth and brought to a final volume of 900 grams total volume.

Mullet samples were not blended, but placed whole into individual

plastic bags containing lactose broth in a 1:10 proportion. The bags

were heat-sealed, the samples shaken, and the bags incubated. This






19

Samples

Thirty samples of each seafood (oysters, clams, mullet, and crabs)

were harvested between August 1981 and August 1982, from both a west

coast location and an east coast location within the state of Florida.

The west coast location was at the mouth of the Suwannee River and the

east coast location was in the Intracoastal Waterway 500 meters south

of the bridge on State Road 206 in Crescent Beach. Crabs were harvested

by trapping, oysters by tonging, and clams by digging. The mullet were

fresh whole commercial samples purchased in the vicinity of the

sampling locations (Suwannee, FL and St. Augustine, FL), and had been

iced prior to transportation to the laboratory. Eighteen of the thirty

east coast crabs were purchased live in St. Augustine and were not iced

during transportation. The samples were transported to the laboratory

at the University of Florida (Gainesville) in sanitized insulated

coolers with analysis begun within four hours of harvest or purchase.

No attempt was made to cool the samples (with the exception of the

mullet) because of the short time span involved between collection and

analysis.

Salmonella Analysis

The method for isolation of Salmonella generally followed the

Bacteriological Analytical Manual (B4M) (66) as follows. Individual

shellfish were blended for two minutes at 8000 rpm in a 1:10 dilution

using lactose broth. Crab weighing over 100 grams were blended with

lactose broth and brought to a final volume of 900 grams total volume.

Mullet samples were not blended, but placed whole into individual

plastic bags containing lactose broth in a 1:10 proportion. The bags

were heat-sealed, the samples shaken, and the bags incubated. This






20

method was used because of the larger size of the mullet and the desire

to analyze the entire fish. All samples were incubated in blender.jars

or bags at 35 C for 24 + 2 hours. Selective enrichment using both

tetrathionate broth and selenite cystine broth followed using a 1-mL

aliquot into 10 rL selective enrichment and incubated at 35 C for 24 +

2 hours. Samples from each tube were streaked onto three selective

plating media: xylose lysine desoxycholate agar (XLD), brilliant green

agar (EG), and bismuth sulfite agar (BS). These plates were incubated

for 24 + 2 hours at 35 C. Two typical colonies from each medium, if

present, were transferred to triple sugar iron agar (TSI) slants and

lysine iron agar (LIA) slants, which were incubated at 35 C. All

isolates with positive LIA reactions were retained for biochemical

analysis, as stated in the BPM (66). Isolates were purified by the use

of both selective and nonselective media prior to biochemical analysis.

Biochemical tests performed and media utilized are shown in Table

2. Cultures were discarded if they produced the biochemical reactions

listed in Table 3. All other cultures were subjected to serological

identification using polyvalent antisera (A-I, V.). Positive polyvalent

cultures were specifically identified by the laboratories of the

Florida Department of Health and Rehabilitative Services located in

Jacksonville.

MPN Studies

A quantitative study of the presence of salmonellae in oysters and

fresh-water clams (Polymesoda caroliniana) from the west coast harvest

location was performed using five 10-nL samples of the same dilution

incubated in 90 rL lactose broth (51). The analyses were performed in

























TABLE 2
BIOCHEMICAL TESTS PERICRVED FCR ISOLATION CF SALMONELLA


TEST
Presence of urease enzyme
Ability to ferment dulcitol
Ability to ferment lactose
Ability to ferment sucrose
Ability to utilize malonate
as a sole carbon source
Ability to utilize citrate
as a sole carbon source
Ability to convert tryptophan
to indole
Ability to grow in the presence
of potassium cyanide
Production of acid end products
Production of acetylmethyl-
carbinol
Presence of lysine decarboxylase


NED ILM EPLOYED
Urea broth
Phenol red dulcitol broth
Brom cresol purple lactose broth
Brom cresol purple sucrose broth
Malonate broth

Simnon's citte agar slant

Tryptone broth with Kbvac's reagent

KCN broth

VRVP medium with methyl red
VRVP with alpha-naphthol and KOH


Lysine decarboxylase broth






22




















TABLE 3
BASIS FCR DISCARDING ISOLATES

1. Urease present

2. Lactose fermentation, unless
a. mralonate test is positive
b. acid slant on TSI

3. Sucrose fermentation, unless acid slant on TSI

4. Growth in KCN, VP positive, and NR negative






23

duplicate and the most probable number technique was used to quantitate

the results. Composite samples of 100 grams for oysters and 200 grams

for clams were prepared to increase the number of individual mollusks

sampled during each analysis.

Storage Studies

A storage study was conducted in June 1982, to observe the

survival of salmonellae in oysters and fresh-water clams under

refrigerated conditions. This study was performed in conjunction with

the MPN study previously mentioned. Oysters and fresh-water clams

(Polymesoda caroliniana) from the west coast harvesting location were

analyzed for salmonellae on days 0, 5, and 10. To simulate commercial

storage conditions, storage was in an insulated cooler with the lid

open inside a walk-in cooler which maintained a temperature of 3.3 to

7.3 C. Because burlap bags are used commercially for storing oysters,

air flow was determined to be advantageous.

Sediment Samples

Five sediment samples taken from a sand bar at the rmuth of the

Suwannee River were analyzed for Salmonella. This bar was chosen

because of the large number of waterbirds commonly found in the

vicinity.

Aerobic Plate Count

The pour plate method using standard plate count agar was utilized

to quantitate the mesophilic aerobic bacteria (APC). This analysis was

performed in duplicate using Butterfield's phosphate buffer (66) as the

diluent. Composited samples of fifty grams or more were used for the

oysters and east coast clams while the mullet, crabs, and west coast

clams were larger and therefore not composited. The colonies on the






23

duplicate and the most probable number technique was used to quantitate

the results. Composite samples of 100 grams for oysters and 200 grams

for clams were prepared to increase the number of individual mollusks

sampled during each analysis.

Storage Studies

A storage study was conducted in June 1982, to observe the

survival of salmonellae in oysters and fresh-water clams under

refrigerated conditions. This study was performed in conjunction with

the MPN study previously mentioned. Oysters and fresh-water clams

(Polymesoda caroliniana) from the west coast harvesting location were

analyzed for salmonellae on days 0, 5, and 10. To simulate commercial

storage conditions, storage was in an insulated cooler with the lid

open inside a walk-in cooler which maintained a temperature of 3.3 to

7.3 C. Because burlap bags are used commercially for storing oysters,

air flow was determined to be advantageous.

Sediment Samples

Five sediment samples taken from a sand bar at the rmuth of the

Suwannee River were analyzed for Salmonella. This bar was chosen

because of the large number of waterbirds commonly found in the

vicinity.

Aerobic Plate Count

The pour plate method using standard plate count agar was utilized

to quantitate the mesophilic aerobic bacteria (APC). This analysis was

performed in duplicate using Butterfield's phosphate buffer (66) as the

diluent. Composited samples of fifty grams or more were used for the

oysters and east coast clams while the mullet, crabs, and west coast

clams were larger and therefore not composited. The colonies on the






23

duplicate and the most probable number technique was used to quantitate

the results. Composite samples of 100 grams for oysters and 200 grams

for clams were prepared to increase the number of individual mollusks

sampled during each analysis.

Storage Studies

A storage study was conducted in June 1982, to observe the

survival of salmonellae in oysters and fresh-water clams under

refrigerated conditions. This study was performed in conjunction with

the MPN study previously mentioned. Oysters and fresh-water clams

(Polymesoda caroliniana) from the west coast harvesting location were

analyzed for salmonellae on days 0, 5, and 10. To simulate commercial

storage conditions, storage was in an insulated cooler with the lid

open inside a walk-in cooler which maintained a temperature of 3.3 to

7.3 C. Because burlap bags are used commercially for storing oysters,

air flow was determined to be advantageous.

Sediment Samples

Five sediment samples taken from a sand bar at the rmuth of the

Suwannee River were analyzed for Salmonella. This bar was chosen

because of the large number of waterbirds commonly found in the

vicinity.

Aerobic Plate Count

The pour plate method using standard plate count agar was utilized

to quantitate the mesophilic aerobic bacteria (APC). This analysis was

performed in duplicate using Butterfield's phosphate buffer (66) as the

diluent. Composited samples of fifty grams or more were used for the

oysters and east coast clams while the mullet, crabs, and west coast

clams were larger and therefore not composited. The colonies on the






24

plates were counted with the aid of a Quebec Colony Counter (American

Optical Co., Buffalo, NY) after incubation at 25 C for five days.

Coliform Analysis

Coliform and fecal coliform analyses were performed simultaneously

with the aerobic plate count analysis. These analyses were performed as

stated in the Compendium of Methods for the Microbiological Examination

of Foods (1) using the most probable number (MPN) technique. One rrL of

each dilution was transferred into either three or five 10-nL tubes

containing lauryl tryptose broth and incubated at 35 C for 48 + 2

hours. As soon as gas was detected by the use of Durham tubes, a

loopful of broth was transferred to tubes containing 10 mL of either

brilliant green bile 2% broth (BGB) or EC medium. The BGB tubes were

incubated at 35 C for 48 + 2 hours and the EC medium was incubated in a

constant temperature bath (Blue M, Blue.Island, IL) at 44.5 C for 48 +

2 hours. The number of coliforms were quantitated using the 3-tube or

5-tube MPN table for gassing BGB tubes and the fecal coliform count was

quantitated using the gassing BC tubes and the MPN tables.

Statistical Analysis

To determine if a correlation was present between salmonellae and

total coliform, fecal coliform, or aerobic plate count values, three

linear regression were made of the.percentage salmonellae recovered

versus total coliform, fecal coliform, and aerobic plate count. The
results given are the r2 values of the linear regressions.
results given are the r values of the linear regressions.






24

plates were counted with the aid of a Quebec Colony Counter (American

Optical Co., Buffalo, NY) after incubation at 25 C for five days.

Coliform Analysis

Coliform and fecal coliform analyses were performed simultaneously

with the aerobic plate count analysis. These analyses were performed as

stated in the Compendium of Methods for the Microbiological Examination

of Foods (1) using the most probable number (MPN) technique. One rrL of

each dilution was transferred into either three or five 10-nL tubes

containing lauryl tryptose broth and incubated at 35 C for 48 + 2

hours. As soon as gas was detected by the use of Durham tubes, a

loopful of broth was transferred to tubes containing 10 mL of either

brilliant green bile 2% broth (BGB) or EC medium. The BGB tubes were

incubated at 35 C for 48 + 2 hours and the EC medium was incubated in a

constant temperature bath (Blue M, Blue.Island, IL) at 44.5 C for 48 +

2 hours. The number of coliforms were quantitated using the 3-tube or

5-tube MPN table for gassing BGB tubes and the fecal coliform count was

quantitated using the gassing BC tubes and the MPN tables.

Statistical Analysis

To determine if a correlation was present between salmonellae and

total coliform, fecal coliform, or aerobic plate count values, three

linear regression were made of the.percentage salmonellae recovered

versus total coliform, fecal coliform, and aerobic plate count. The
results given are the r2 values of the linear regressions.
results given are the r values of the linear regressions.














RESULTS AND DISCUSSION

Salmonella Analysis Results

Isolation of Salmonellae From Various Seafoods

Previous studies have shown that the number of seafood.samples

found to contain salmonellae varies with respect to sampling method and

the seafood studied. A mean of 11.1% of the oyster homogenate samples

and 2.3% of the clam homogenate samples were found to contain

salmonellae in a study conducted by Andrews et al. (2, 3). In another

study (60), the percentage of positive samples was 11.4% for oysters.

It must be noted that these percentages were all taken from composite

samples, whereas this research was conducted using individual animals

as separate samples. Table 4 details the salmonellae recovered from the

four seafoods involved in this study. The results vary between seafoods

and sampling locations, as well as from previously stated findings of

other investigators.

Ten percent of the west coast oysters that were analyzed contained

Salmonella and 6.7% of the east coast oysters also contained

Salmonella, with the combined average of 8.3% of the oysters containing

salmonellae. These percentages are within the general range of those

found in the previous studies (3, 60). The incidence of Salmonella in

clams, however, was much higher than those previously reported (2),

with the west coast incidence of 43.3% and the east coast incidence of

13.3%. Although there is a marked difference between the samples from

each coast, many factors may account for this difference, among which














RESULTS AND DISCUSSION

Salmonella Analysis Results

Isolation of Salmonellae From Various Seafoods

Previous studies have shown that the number of seafood.samples

found to contain salmonellae varies with respect to sampling method and

the seafood studied. A mean of 11.1% of the oyster homogenate samples

and 2.3% of the clam homogenate samples were found to contain

salmonellae in a study conducted by Andrews et al. (2, 3). In another

study (60), the percentage of positive samples was 11.4% for oysters.

It must be noted that these percentages were all taken from composite

samples, whereas this research was conducted using individual animals

as separate samples. Table 4 details the salmonellae recovered from the

four seafoods involved in this study. The results vary between seafoods

and sampling locations, as well as from previously stated findings of

other investigators.

Ten percent of the west coast oysters that were analyzed contained

Salmonella and 6.7% of the east coast oysters also contained

Salmonella, with the combined average of 8.3% of the oysters containing

salmonellae. These percentages are within the general range of those

found in the previous studies (3, 60). The incidence of Salmonella in

clams, however, was much higher than those previously reported (2),

with the west coast incidence of 43.3% and the east coast incidence of

13.3%. Although there is a marked difference between the samples from

each coast, many factors may account for this difference, among which

























SALIONELLAE

SEAFtOD LOCATION OF
HPRVEST

Oysters West Coast
East Coast
Combined

Clams West Coast
East Coast
Combined

Mullet West Coast
East Coast
Conbined

Crabs West Coast
East Coast
caught
purchased
Combined


TABLE 4
RECOVERED FROM FOR~ SEAFDODS


IATE


SWPLES FOS./
# SAVMLED


July 82
August 81


October 81
August 81


November 81
January 82


February 82
March 82


3/30
2/30
5/60

13/30
4/30
17/60

0/30
0/30
0/60

11/30
9/30
3/12
6/18
20/60


42/240 17.5


PERCENT


10.0
6.7
8.3

43.3
13.3
28.3

0.0
0.0
0.0

36.7
30.0
25.0
33.3
33.3


TOTAL







are the differences in size of the clams and the apparent lower

salinity at the west coast location due to the movement of fresh water

discharged from the mouth of the river. The incidence of Salmonella in

crabs was also high, with 36.7% of the west coast crabs containing

Salmonella and Salmonella isolated from 30.0% of the east coast crabs.

Eighteen of the east coast crabs used for analysis were not caught in

the Intracoastal Waterway, but were purchased live in the vicinity of

the harvest location. These showed little difference in percent

recovery of salmonellae from the twelve east coast crabs harvested in

the Intracoastal Waterway. Mullet samples were all negative for

Salmonella; however, this may be a result of prior icing, incubation

temperatures, sampling methodology, and/or the fact that mullet are

free-swirming fish. These factors will be discussed in detail in the

following pages. If Salmonella is a contaminant as opposed to an

indigenous member of the estuarine environment, these variations in

percent incidence would be expected due to sporatic contamination.

There are several factors which may have influenced the outcome of

the salmonellae analyses in this study. First, because refrigeration is

known to injure many microorganisms, no attempt was made to cool the

samples. The short period between harvest and analysis maximumn time of

four hours) minimized any opportunity for extensive growth of the

microorganisms present. The aerobic plate counts were generally low,

indicating that competing microorganisms probably had not grown and

were not in such high quantity as to markedly inhibit the growth of

salmonellae. Thirdly, because low numbers of salmonellae were

anticipated, individual animals were used to draw a larger number of

smaller samples, thereby increasing the probability of recovering any






28

salmonellae present. Lastly, a preenrichment procedure was used, which

is recommended mainly for processed foods or foods with low levels of

contamination. It is possible that increased recovery of any injured

salmonellae occurred because of the use of a preenrichment medium,

which allowed the organisms to overcome any physiological stress.

A difference was seen in the number of salmonellae-positive

samples isolated from each coast. Salmonellae were isolated from a

total of 27 of 120 (22.5%) samples from the west coast location and 15

of 120 (12.5%) from the east coast location. This may be partially

explained by the differences in the surrounding environment of the two

areas, which differed in human population, wildlife, and sewage

disposal techniques. The west coast location is not highly populated,

with only a limited number of riverfront vacation homes and septic

tanks for sewage disposal. There were many water birds and animals in

the estuary of the Suwannee River because of the limited human

population. The east coast location, on the other hand, is much more

populated as well as industrialized with sewage treatment plants which

empty into the Intracoastal Waterway. There were fewer water birds and

animals in the surrounding area.

To investigate the possibility of Salmonella being present in the

entire estuarine environment rather than only in the seafoods studied,

five sediment samples were analyzed for Salmonella from a sand bar

approximately fifty meters from the harvest location of the west coast

oysters. The incidence of salmonellae in three of the five sediment

samples taken from a sand bar in the vicinity of the harvest location

of the clams and oysters on the West Coast indicates salmonellae may be

widely distributed in the environment. In this particular area, the






29

high number of water birds and animals that populate the area may

contribute to this incidence. These birds and animals were not as

prevalent at the east coast location, which could substantiate the

higher numbers of seafood being contaminated with salmonellae from the

West Coast. The importance of animal and waterbird transmission is

illustrated by research which indicates the seagull's capacity to

transmit a new serotype of salmonellae into an environment (52).

Differences were also noted between the species studied, with the

major distinction being that no salmonellae were isolated from the

mullet. This may have been due to mullet being the only free-swimning

fish studied, with the other seafoods being "bottom dwellers." Stream

bottom sediment was found to have a higher recovery rate of salmonellae

than surface waters (26), which would indicate that "bottom dwellers"

would be more likely to contain salmonellae. Additionally, mullusks are

known to be filter feeders, which results in the accumulation of

microorganisms from their environment (65). No such report is known

for fin fish. Another possibility for the lack of salmonellae found in

the mullet is the temperature of storage and of incubation. The length

of time the mullet were on ice is unknown, which may have been

detrimental to salmonellae, if present. In addition, the total volume

of fish and broth during the preenrichment section of the mullet

analysis was so great that several hours were required for all thirty

samples to reach the incubation temperature of 35 C. An additional

possibility for the lack of salmonellae found in the mullet is the

sampling method used. The plastic bag procedure was adopted to provide

analysis of the total surface area of the fish. This method can be

substantiated by the research involving sampling methods for detection






30

of salmonellae in raw chicken carcasses. D'Aoust et al. (19) found the

whole carcass rinse method to be superior to the thaw water analysis or

the skin method. By using this method, the gastrointestinal tract was

not punctured, and hence the contents of the tract were not accessible

to the preenrichment broth. Camnercially, the gastrointestinal tract is

not usually punctured during cleaning the fish. The gastrointestinal

tract of the other seafoods studied were blended with the other parts

of the animals. This difference in sampling methoddology between the

mullet and the other seafoods studied may have had some bearing on the

outcome of the analysis.

It should be noted that due to an incubator malfunction during the

preenrichment and selective enrichment segments of the analysis for

salmonellae in the east coast crabs, the incubation temperature

fluctuated between 37 and 45 C. Because salmonellae were recovered,

these results are presented.

WPN Studies

Quantitating the number of salmonellae per 100 grams of west coast

oysters using the nmst probable number (MPN) technique showed that

salmonellae were present in low numbers (Table 5). The highest number

obtained was 2.2 salmonellae per 100 grams of oysters with an upper

confidence limit of 12.6 and a lower confidence limit of 0.1 organisms

per 100 grams. Because of the small size of the oysters (between 3 and

15 grams each), it would be possible for one organism to be present in

every 300 oysters as a lower limit and two organisms present in each

oyster as an upper limit. The number of salmonellae consumed at one

meal of raw oysters would, therefore, be minimal. With the infective

dose being dependent on the consumer, food handling and preparation,


,^~ i. .-.,



























TABLE 5
NOST F BABLE NUMBER OF SA.M)NELLAE PRESENT IN OYSTERS

DAYS CF SAVPLE MPN PER
SITRPGE 100 g

0 A 0.0
B 2.2

5 A 2.2
B 2.2

10 A 0.0
B 2.2






32

time factors, and the nature of the food, it would appear that this

concentration of salmonellae would not frequently cause gastroenteritis

in nan. From a commercial standpoint, however, this concentration is

important because of the United States Food and Drug Adminis- tration's

ruling that no salmonellae are allowed in foods.

Quantitation of the number of salmonellae per 100 grams of west

coast fresh-water clams (Polymesoda caroliniana) yielded higher numbers

than those found in the oysters (Table 6), with the highest number

being 16.0 salmonellae per 100 grams of clam with a lower confidence

limit of 3.3 and an upper confidence limit of 52.9 organisms per 100

grams of clam. These numbers are still relatively low, indicating that

few salmonellae would be present in a single serving.

Storage Studies

In order to predict the survivability of the salmonellae under

commercial handling and storage conditions, a ten-day storage study was

performed in conjunction with the NPN study of west coast oysters and

fresh-water clams (Tables 5 and 6). It is apparent from these studies

that salmonellae are capable of survival at 5 C for ten days. This,

along with other studies (33, 39, 65), indicate that salmonellae can

survive typical handling and storage procedures presently practiced in

the seafood industry.

Serotypes

Salmonellae found in this study were of a variety of serotypes

(Table 7). The Centers for Disease Control (CDC) reported a total of

207 different Salmonella serotypes isolated from human sources (12).

These 207 serotypes represent approximately 12% of the more than 1800

known Salmonella serotypes and variants. The ten most frequently



























TABLE 6
MOST PfOBABLE NLUEER CF SALDNELLAE PRESENT


IAYS CF
STCRAPE

0


5


10


SAMPLE


A
B

A
B

A


IN FRESH-WATER CAMS

NPN PER
100 g

5.1
9.2

5.1
2.2

9.2
16.0












/

TABLE 7
SERILOGICAL IDENTIFICATION OF SLATES FIRCM RLR SEAIOCDS AND SEDIMENT

NUM3ER SPIPLES CONTAINING SERITYPE
SPECIES CLAVS OYSTERS CRABS LYESODA SEDIMENT
VEST EAST 'ESTa EAST\ WEST EAST VEST IEST

S. agona 5 1 3
S. allandale 1 1
S. anatuin 1 1
S. bareilly 2 2
S. braenderup 2 1 5 1
S. inverness 1 5 1 3
S. java 3 1
S. muenchen 8 1 3 6
S. redlands 2
S. tallahassee 1 7 1
S. thompson I

Edwardsiella tarda 2 1

b West coast oysters are those from the MPN study as vwll as the the individual animal study.
Polymesoda isolates are those from the fresh-water clam IPN study.





35

recovered serotypes accounted for over 72% of the isolates reported in

1979, which are listed in Table 8 (12). This illustrates the vast

differences in the frequency in which the various serotypes cause

gastroenteritis. The only serotype recovered in the seafoods studied

which is also found in this list, as well as the list of the ten most

frequently reported serotypes from animal sources (Table 8), is S.

agona, which was recovered from a sampling of east coast crabs and from

west coast sediment. All other serotypes recovered in the seafoods each

accounted for less than 1% of the reported isolates of Salmonella in

1979. Two serotypes, S. redlands and S. allandale, were not reported to

have been recovered from human or nonhuman sources in 1979. Table 9

details Salmonella serotypes isolated from seafoods in other studies.

It can be seen that five of these serotypes were among the ten most

frequently reported serotypes from either nonhuman or human sources in

1979.

Edwardsiella tarda, another member of the family Enterobac-

teriaceae, was found in west coast clams, both fresh-water clams

(Polymesoda) and salt-water clams (Mercenaria) (Table 7). Edwardsiella,

exhibits disease patterns and biochemical characteristics similar to

Salmonella. E. tarda is a motile, hydrogen sulfide producing, lactose

negative, and indole positive organism (16) that has been isolated from

patients having acute gastroenteritis, enteric fever, septicemia,

meningitis, wound infections, and surgical incisions (16, 68). The

ecology of E. tarda is also similar to Salmonella, having a wide

geographic distribution and the ability to infect numerous animal

species (68). Because of these similarities, indole positive isolates

were analyzed for E. tarda.
















TABLE 8
THE TEN MDST FREQUENTLY REPORTED SALMtNELLA SERDTYPES RCMA HLMN AND NONHLMAN SOUCES*, 1979


HLMN
Serotype
typhirmuriun**
enteritidis
heidelberg
newport
infants
agona
saint-paul
typhi
montevideo
oranienburg


Percent
32.6
8.5
8.0
6.2
4.6
3.5
2.8
2.1
2.0
1.9


Rank
1
2
3
4
5
6
7
8
9


N3NHLMN
Serotype
typhimurirLu**
agona
derby
infants
panama
heidelberg
oranienberg
montevideo
cholerae-suis
v. kunzendorf
weltevreden
worthington


reported to CDC
** includes var. copenhagen
Source: Salmonella Surveillance Annual Sumnary (12)


Rank
1
2
3
4
5
6
7
8
9
10


Percent
22.2
12.4
6.1
5.1
4.7
3.5
2.8
2.8


2.6
1.7
1.7























TABLE 9
SALMONELLA SEIOTYPES PREVIOUSLY REPORTED FRCM SEARFODS
SERDLYPE CLAMS OYSTERS OYSTERS SHRIMP
S. anatun X
S. blockley X
S. braenderup X
S. cerro X
S. derby X X
S. heidelberg X
S. hilversam X
S. infants X
S. lexington X
S. manhattan X
S. newport X
S. paratyphi B X
S. senftenberg .X
S. tennessee X
S. thompson X X
S. typhimurium X X
S. virchow X

Reference 2 3 61 18







Isolation Methodology

Although this study did not involve methodology, it is of

importance to discuss the effectiveness of recovering all the

salmonellae present in the seafoods analyzed. Successful isolation of

salmonellae is a complex multifactorial procedure and is dependent upon

the food studied, the medium used, and the laboratory personnel

performing the analysis. For the purpose of this study, the procedure

recommended in the BPM (66) was the most practical in that a standard

was needed. Higher recovery may have been possible by the use of an

alternative method, such as elevated temperatures or the use of more

selective media.

The problem with the isolation method was first identified during

an analysis of east coast crabs. In March 1982, due to incubator

failure, the preeenrichment and selective enrichment sections of the

analysis were incubated at a higher temperature, fluctuating between 37

C and 45 C. The results of this analysis revealed that 30% of the crabs

contained salmonellae. Two months later when the analysis was repeated,

no salmonellae were recovered. In August 1982, when the analysis was

performed for the third time, salmonellae again were not recovered.

This confirms the finding of Miller and Koburger (unpublished data)

that elevated temperatures provide higher recovery of salmonellae from

oysters (Salmonellae were recovered from 33/84 (39%) of the aliquots at

41 C and 43 C as opposed to 11/42 (26%) when using 35 C.). While

studying clams and oysters, Andrews et al. (2) tested the sensitivity

of the BAM method, which revealed that as few as eight to ten

salmonellae per 100 grams of artificially contaminated shellfish could

consistently be recovered, which indicated an acceptable level of





39

sensitivity. By the use of the fluorescent antibody (FA) test to

analyze water, Cherry et al. (14) were able to detect salmonellae in

60% nmre samples than when using the culture method employing elevated

temperatures. Because of the lack of a method which is optimal, exact

numbers and comparison of recovery between studies should be

interpreted cautiously.

Relationship to Total Coliforms, Fecal Coliforms,

and Aerobic Plate Count

A relationship between total coliforms, fecal coliforms or aerobic

plate count and the recovery of salmonellae was not apparent, with r

values of 0.15, 0.02, and 0.11, respectively (Table 10). Although there

are relatively few data in this study, these results emphasize the

inadequacy of relying solely upon an indicator system for determining

the safety of a seafood. An extreme case can be seen in the results of

the analyses of west coast clams. The total coliform level of 5

organisms per gram was low, the aerobic plate count of 260 organisms

per gram was far below the guideline of 500,000 organisms per gram

(42), and the fecal coliform count was zero. The percentage recovery

of salmonellae, however, was 43%. Although not quite as marked, east

coast clams exhibited the same behavior, with the aerobic plate count

at 1100 organisms per gram, coliforms at 2 organisms per gram, and

fecal coliforms at 2 organisms per gram. Thirteen percent of the

samples analyzed contained salmonellae from this group. Andrews et al.

(2) found total coliform and fecal coliform counts in clam meat to be

higher than those found in this study. Total coliform counts ranged

from 13 to 1720 organisms per gram and fecal coliform counts ranged



















AEROBIC PLATE G(UNT, TOTAL (LIFCRM, FECAL


TABLE 10
CGLIFCRIM, AND SAUvN ELLAE RECOVERED FI~M FRXR SEAFOODS


TOTAL
C(LIFIRMS*
MPN/g


FECAL
CDLIFC~TS*
NPN/g


SAUMDNELLAE
samples pos./ Percentage
# sampled


West coast oysters
East coast oysters

West coast clams
East coast clams

West coast mullet
East coast mullet

West coast crabs
East coast crabs
caught
purchased


July 82
August 81

October 81
August 81

November 81
January 82

February 82
March 82


* these numbers represent means of duplicate analyses


SEAFOOD


ATE


APC*
CFU/g


1100 Est
800 Est

260
1100 Est

4.4 X 105
5.1 X 10
5
7.5 X 105
1.3 X 108
7.9 X 104
2.6 X 10


78
306

4700
28
0
56


3/30
2/30

13/30
4/30

0/30
0/30


11/30
9/30
S 3/12
6/18


0.2
27

4
28
0
56


10.0
6.7

43.3
13.3


36.7
30.0
25.0
33.3






41

from 4.9 to 330 organisms per gram when salmonellae were detected in

clams.

Many studies have compared the incidence of salmonellae in

seafoods with the total coliform and fecal coliform counts of the

harvest waters. When studying 214 clams, Andrews et al. (2) found that

it was not until the total coliform PN of the waters exceeded 200

organisms per 100 rL that salmonellae were recovered from the clams.

The range of total coliform NPN of water where salmonellae were

recovered was from 490 to 11,000 organisms per 100 rL with the fecal

coliform range from 33 to 2300 organisms per 100 mL. When studying 539

oysters, however, Andrews and coworkers (3) found one salmonellae-

positive oyster which was harvested from water having a total coliform

NPN of 11 organisms per 100 mL water and a fecal coliform level of less

than 1.8 organisms per 100 nL water. Of their oyster samples found

positive for salmonellae, 7.5% had total coliform counts within the

approved range of a maximum of 70 organisms per 100 rL water. In

addition, a total of 2.4% of the oysters found positive for salmonellae

had fecal coliform levels within the approved range of a maximum of 14

organisms per 100 mL overlying water.

A measureable difference can be seen in these studies of the

correlation of coliforms to salmonellae, which clearly indicates more

study should be directed in this area. All that is now known is that

low numbers or even the absence of coliforms or fecal coliforms in 100

rL seawater or in the seafood meat may not insure the absence of

pathogenic microorganisms in mollusks harvested from these waters.

Therefore, the absence of pathogenic organisms from approved waters

based on current analysis methods cannot be assumed.






42

Salmonella as a Contaminant or an Autochthon

Although salmonellae are known to be ubiquitous in the

environment, their presence has been consistently thought to be

associated with fecal contamination. Being a human and animal ent ric

pathogen, this assumption seems reasonable. It is thought that

salmonellae cannot survive out of the human or animal body for extended

periods of time, and that the natural environment would therefore not

be a reservoir for the organism. Several studies related to water

quality have questioned these concepts. In 1967, Fair and Morrison

(22) were able to isolate salmonellae from a stream of high quality

where the total coliform count was 30 organisms per 100 nL water.

Throughout the entirety of the stream, there were no known additions of

human excreta. Salmonellae were isolated from all seven sampling

stations and the source of contamination was thought to be due to wild

and domestic animals. This article initiated the theory that naturally

occurring potable surface waters do not exist. A 1971 study agreed with

this theory when salmonellae were easily recovered within 350 ft. of

the origin of a supposedly "unpolluted" mountain stream where the only

reasonable source of pollution appeared to be terrestrial or aquatic

wildlife (14). Hendricks and Morrison (27) showed that salmonellae and

other enteric bacteria can not only maintain their populations in

polluted or unpolluted river water at temperatures as low as 10 C, but

also were capable of multiplication. This fact may help to explain the

ease with which salmonellae have been recovered from various streams.

Based on these studies as well as his own studies, Cherry et al. (14)

concluded that the possibility should now be entertained that these

bacteria may exist as free-living organisms multiplying under natural






43

conditions. This would indicate that salmonellae are autochthonous,

being indigenous in the estuarine environment.

Although there is some question as to the use of indicator

organisms to determine the safety of foods, this data, although

limited, showed that in several cases, such as the west coast clams,

determining the presence of fecal coliforms was not a good indication

of the presence of Salmonella in these seafoods. Due to the absence of

fecal coliforms, this may be another indication of the possible au-

tochthonous nature of Salmonella.

The United States Department of Agriculture has had to deal with

whether salmonellae in foods are "added" substances or whether they are

a natural part of domestic animals and fish. For example, a current

court decision ban importation of Indian shrimp, if it contains

salmonellae, because salmonellae are thought to be added substances,

thereby causing the product to be adulterated (4). In this case, the

salmonellae were thought to be present because of poor sanitary

practices in the processing plant. Salmonellae can thus be classified

as added, which changes the definition of adulteration to any substance

which "may render the food injurious to health." If the substance is

not added, the product is then considered adulterated only if the

substance would "ordinarily render the food injurious to health."

Salmonellae is not "ordinarily injurious" since its dangers can be

averted through proper cooking and storage. In this way, salmonellae do

not adulterate the food if they are naturally occurring (56). In 1980,

2.7% of the Gulf Coast shrimp in a study were found to be contaminated

with Salmonella (18), but since this contamination is thought to be

inherent in the product, Gulf Coast shrimp is not confiscated. This






44

discrepancy in rulings concerning Salmonella indicates the complexity

of the situation.

In the United States, salmonellae in red meats and poultry have

been thought to be inevitable. The National Research Council stated in

1975 (49) that complete elimination of salmonellae from domestic

animals was not feasible at that time, but that the development of

infection-free breeding stock, elimination of contaminants from feed,

improved conditions for holding animals before slaughter, and more

careful slaughtering practices are measures that can reduce the hazard.

Three Scandinavian countries, Denmark, Finland, and Sweden, have

attempted to raise salmonellae-free domestic meat animals by the use of

salmonellae-free feed ingredients and strict destruction or quarantine

of those animals contaminated with salmonellae (56). Various surveys

have indicated that these countries have a low incidence of Salmonella

in poultry, with the percent contamination ranging from 1% to 7%. The

United States percent contamination is estimated at approximately 30%

(70). Unfortunately, the impact of these programs has in no way

eliminated human salmonellosis. Reported cases per 100,000 population

are still high, with 10 cases per 100,000 people in Denmark, 44 in

Finland, 43 in Sweden, and 14 in the United States. These figures may

be distorted since they are reported cases and not true incidences.

Although the incidence may be reduced by the employment of these

precautionary measures, salmonellosis cannot be completely eradicated

at this time. Improved methods for the eradication of salmonellae would

be costly to the population on the whole, and therefore would be met

with opposition.






45

Significance of the Findings v

Because salmonellae were found in three of the four seafoods

studied, it is necessary to evaluate the significance of these

findings. In some cases, the number of samples in which salmonellae

were recovered was quite high, which causes one to question why

regulatory agencies have not placed restrictions on these products,

and, more importantly, why there is not a higher incidence of

salmonellosis caused by seafood products.

Most of these products will be cooked before eating. Members of

the genus Salmonella are killed during ordinary cooking times and

temperatures in foods having a high moisture content. In most

instances, foods that are to be heat processed can be made completely

safe with respect to salmonellae contamination without impairing the

quality of the food (7). The specific times and temperatures required

to kill salmonellae depend upon the number of bacteria present, the pH

of the food, the species of Salmonella, and the water activity of the

food. If the product is not cooked, this first defense fails. Such is

the case when eating raw clams and oysters.

The probability of salmonellae surviving the digestion process is

complicated by the time of consumption. Because the pH of the stomach

is lowest just after the meal begins, more bacteria are killed at this

time. An inversely proportional relationship between the amount of

gastric acid and the number of bacteria in the stomach has been found

(63). Because raw oysters and clams are most often consumed as

appetizers, the pH of the stomach would inhibit the majority of the

salmonellae.






46

A second factor involved in the consumption of raw oysters and

clams is the fact that alcohol often accompanies these appetizers..

Beer and wine have low pH's, which would be deleterious to the

salmonellae before the stomach is reached as well as aid the stomach in

producing acid conditions. The alcohol itself, in large quantities,

would also be inhibitory.

In spite of the deleterious effects of heat treatment, pH of the

stomach, and the consumption of alcohol, salmonellae are able to

survive in many instances. In the period of 1963 to 1973 in the United

States, five comnon-source epidemics of salmonellosis (one involving

twelve separate outbreaks) were attributed to fish and shellfish (7).

Therefore, the presence of these salmonellae, even in low numbers, must

not be ignored.

Relatively low numbers of salmonellae were found in oysters and

fresh-water clams. This would indicate that the salmonellae are not in

large enough quantity to cause severe symptoms. However, milder

symptoms may occur and would go unreported more often than severe

symptoms. In addition, as the salmonellae encounter various host

defense mechanisms, a portion of the original population will be

killed. If the total number of salmonellae were low to begin with,

these defense mechanisms might destroy the entire population. This

would account for the low numbers of reported cases of salmonellosis

due to consumption of contaminated seafood products.

Another interesting factor in the findings of this research is the

serotypes that were isolated. As stated earlier, these were varied and

many were not the common serotypes isolated from human and nonhuman

sources (Table 7). These rarer serotypes may be seldom isolated from






47

humans because the virulence may differ between serotypes, with the

more virulent serotypes being isolated more often because of their.

capacity to survive the host defenses and produce more severe symptoms.

There is also evidence that virulent species of Salmonella multiply

intracellularly whereas avirulent species do not (16). This would also

increase the incidence of particular species over others. Addition-

ally, after studying the lesser virulence of Salmonella isolates from

streams in New York State, Dondero et al. (20) concluded that it is not

inconceivable that the Salmonella genus in the environment may

frequently contain nonpathogenic strains.

The wide variety of serotypes isolated from these seafoods nay

also indicate that there is no single source of contamination. Eleven

serotypes were recovered from these products, with many of the samples

containing more than one serotype. As many as three serotypes were

recovered from an individual animal. The low numbers of salmonellae

recovered indicates that the contamination is minimal, and the number

of serotypes would indicate that the contamination is from a variety of

sources.














SUVMvRY AND CaNCLUSIONS

Analysis for the presence of Salmonella in four seafoods harvested

in the state of Florida was performed. Samples from both the east and

west coasts of Florida were used as being representative of the sea-

foods harvested in Florida. Aerobic plate counts, total coliform

estimates, fecal coliform estimates, storage studies, and quantitative

studies accompanied these analyses.

Results indicated that salmonellae were present in oysters, clams

and crabs in percentages of 8.3%, 28.3%, and 33.3% of the samples

analyzed, respectively. Salmonellae were not recovered from the mullet

samples. Sediment samples taken in the vicinity of the west coast

harvest location also contained salmonellae. Quantitation of the

salmonellae by the use of the MPN technique yielded between 2.2 and

16.0 salmonellae per 100 grams of oysters and fresh-water clams.

Storage tests showed that salmonellae are capable of surviving in

oysters and fresh-water clams at refrigerated temperatures (3-7 C) for

at least ten days. Aerobic plate counts, total coliform estimates, and

fecal coliform estimates did not correlate (r = 0.11, 0.02, and 0.15,

respectively) with the incidence of salmonellae.

Based on the results of this study, the following conclusions can

be drawn:

1. The incidence and distribution of Salmonella in three of the

four seafoods studied would indicate that either Salmonella as a

contaminant is present due to a relatively large and consistent amount






49

of environmental pollution or that Salmonella may be an autochthonous

member of the microflora of the estuarine environment. This is based

on the following observations: Higher numbers of salmonellae were

recovered from the west coast location, which is less populated with

humans and more populated with water birds and animals. With the

variety of serotypes recovered, it is probable that there was no single

source of contamination. Sediment analysis revealed that salmonellae

may be present in the environment as well as in the seafoods studied.

2. The method of treatment of the samples and the isolation method

used for analyzing salmonellae will cause differences in the results

obtained. The lack of refrigeration, minimal competing flora, the use

of a preenrichment medium, and the analysis of individual animals may

have increased the recovery of salmonellae in the study. More sensitive

methods of recovery, such as the use of elevated temperatures, may also

have increased recovery in this category of foods.

3. Under commercial storage and handling conditions, Salmonella

will be able to survive in oysters at least ten days. Temperatures from

5 to 10 C do not kill salmonellae, although the salmonellae do not

appear to multiply readily at these temperatures.

4. Many factors may influence the lack of confirmed reports of

seafoods transmitting salmonellae to humans. The serotypes isolated are

not those that are known to cause the majority of the human

salmonellosis cases reported in the United States. The virulence of

these serotypes, therefore, may not be as great as those serotypes

coanonly isolated from cases of human salmonellosis. Many of these

products are cooked, as are red meats and poultry which also often

contain salmonellae, and the cooking process destroys the salmonellae.






50

If the seafoods are not cooked, they are usually eaten as appetizers.

The pH of the stomach is lower at this period, which will be

detrimental to the salmonellae. Lastly, variation in susceptibility

anong different individuals within the population is well known, and

therefore the low numbers of salmonellae recovered from these seafoods

may not affect many people. All these factors combined may account for

the fact that these salmonellae-containing seafood have not been often

involved in human salmonellosis under normal conditions of harvesting,

processing, storage and consumption.














BIBLIOGRAPHY


1. Anerican Public Health Association. 1976. Compendium of methods
for the microbiological examination of foods. M.L. Speck (ed.).
Amrerican Public Health Association, Washington, D.C.

2. Andrews, W.H., C.D. Diggs, 3.3. Miescier, C.R. Wilson,.W.N. Adams,
S.A. Furfari, and 3.F. Musselman. 1976. Validity of members of the
total coliform and fecal coliform groups for indicating the presence of
Salmonella in the quahaug, Mercenaria mercenaria. 3. Milk Food Technol.
39: 322.

3. Andrews, W.H., C.D. Diggs, M.W. Presnell, 3.3. Miescier, C.R.
Wilson, C.P. Goodwin, W.N. Adams, S.A. Furfari, and J.F. Musselman.
1975. Comparative validity of members of the total coliform and fecal
coliform groups for indicating the presence of Salmonella in the
eastern oyster, Crassostrea virginica. 3. Milk Food Technol. 38:453.

4. Anonymous. 1982. Court of appeals holds Salmonella in shrimp is
"added." Food Chem. News 24:15.

5. Bowmar, E.3. 1964. Challenge of salmonellosis: major health
problem. Amer. 3. Med. Sc. 247:467.

6. Bruch, Carl W. 1968. Salmonellae in food products: a rising
hazard. In Proceedings of salmonellae in foods conference. Pennsylvania
State University, University Park.

7. Bryan, F.L. 1973. Activities of the Centers for Disease Control in
public health problems related to the consumption of fish and fishery
products. pp. 277-281. In C.O. Chichester and H.D. Graham. Microbial
safety of fishery products. Academic Press, New York.

8. Cambelli, V.3. and W.P. Heffernan. 1970. Accumulation of E. coli
by the northern quahaug. Appl. Microbiol. 19:239.

9. Canadian Health and Welfare. 1981. Food-borne and water-borne
disease in Canada, annual summary 1977. Health Protection Branch,
Health and Welfare Canada, Ottawa.

S10. Centers for Disease Control. 1981. Annual foodborne disease
summary 1979. Centers for Disease Control, Atlanta.

11. Centers for Disease Control. 1981. Annual summary 1980: reported
morbidity and mortality in the United States. Morbidity Mortality
Weekly Reports 29:3, 11-16, 73-74.








12. Centers for Disease Control. 1981. Salmonella surveillance annual
summary 1979. Centers for Disease Control, Atlanta.

S13. Centers for Disease Control. 1980. Annual summary 1979: reported
morbidity and rrortality in the United States. Morbidity and Mortality
Weekly Reports Vol. 28.

14. Cherry, W.B. 3.B. Hanks, B.M. Thomason, A.M. Murlin, J.W. Biddle,
and J.M. Croom. 1972. Salmonellae as an index of pollution of surface
waters. Appl. Microbiol. 24:334.

15. Colwell, R.R., R.J. Seidler, 3. Kaper, S.W. Joseph, S. Garges, H.
Lockman, D. Maneval, H. Bradford, N. Roberts, E. Remners, I..Huq, and
A. Huq. 1981. Occurrence of Vibrio cholerae serotype 01 in Maryland and
Louisiana estuaries. Appl. Env. Microbiol. 41:555.

16. Davis, B.D., R. Dulbecco, H.N. Eisen, and H.S. Ginsberg. 1980.
Microbiology, third edition. pp. 660-662. Harper and Row, Philadelphia.

17. D'Aoust, J.Y., D.J. Aris, P. Thisdele, A. Durante, N. Brisson, D.
Drgon, G. Lachapelle, M. Johnson, and R.P. Laidley. 1975. Salmonella
eastborne outbreak associated with chocolate. Can. Inst. Food Sci.
Technol. 8:181.

18. D'Aoust, J.Y., R. Gelinas, and C. Maishment. 1980. Presence of
indicator organisms and recovery of Salmonella in fish and shellfish.
3. Food Protect. 43:679.

19. D'Aoust, J.Y., P. Stotland, and A. Boville. 1982. Sampling method
for detection of Salmonella in raw chicken.carcasses. 3. Food Sci.
47:1643.

20. Dondero, N.C., C.T. Thomas, M. Khara, J.F. Tomoney, and G.M.
Fukui. 1977. Salmonella in surface waters of Central New YorK State.
Appl. Env. Microbiol. 33:791.

21. Ellender, R.D., D.W. Cook, V.L. Sheladia, and R.A. Johnson. 1980.
Entervirus and bacterial evaluation of Mississippi oysters. Gulf
Research Rep. 6:371.

22. Fair, J.F. and S.M. Morrison. 1967. Recovery of bacterial
pathogens from high quality surface waters. Water Resources Res. 3:799.

23. Fontaine, R.E., S. Arnon, W.T. Martin, T.M. Vernon, E.J.
Gangarosa, J.J. Farmer, A.B. Moran, J.H. Silliker, and D.L. Decker.
1978. Raw hamburger: an interstate common source of human
salmonellosis. Am. 3. Epidemiol. 107:36.

24. Frazier, W.C. and D.C. Westhoff. 1978. Food microbiology, third
edition. McGraw-Hill, Inc, New York.

25. Green, John H. 1968. Salmonella in fish and fishery products. In
Proceedings of salmonellae in foods conference. Pennsylvania State
University, University Park.








26. Hendricks, Charles W. 1971. Increased recovery rate of salmonellae
from stream bottom sediments versus surface waters. Appl. Microbiol.
21:379.

27. Hendricks, C.W. and S.M. Morrison. 1967. Multiplication and growth
of selected enteric bacteria in clear mountain stream water. Water Res.
1:567.

28. Hood, M.A. and G.E. Ness 1982. Survival of Vibrio cholerae and E.
coli in estuarine waters and sediments. Appl. Env. Microbiol. 43:578.

29. Hood, M.A., G.E. Ness and G.E. Rodrick. 1981. Isolation of Vibrio
cholerae serotype 01 from the eastern oyster, Crassostrea virginica.
Appl. Env. Microbiol. 41:559.

30. Hunt, D.A. 1977. Indicators of quality for shellfish waters. In
A.W. Hoadley and B.J. Dutka (ed.), Bacterial indicators: health hazards
associated with water. Amer. Soc. for Testing and Materials,
Philadelphia.

31. Hussung, D., R.R. Colwell, and R.M. Weiner. 1981. Seasonal
concentration of coliform bacteria by Crassostrea virginica, the
eastern oyster, in Chesapeake Bay. 3. Food Protect. 44:201.

S32. International Carmission on Microbiological Specifications for
Foods (ICMSF). 1974. Microbiology in foods. II. Sampling for
microbiological analysis: principles and specific applications.
Chapters 2,3,4,5. University of Toronto Press, Toronto, Canada.

33. Janssen, Werner A. 1974. Oysters: retention and excretion of three
types of human waterborne disease bacteria. Health Lab. Sci. 11:20.

34. Jegathesan, M., L.T. Wah, L.E. Soon, D.S. Har, L.B. Liat. 1976.
Bacterial enteropathogens in ralaysian shellfish. Tropical and
Geographical Med. 28:91.

35. Johnson, Phyllis T. 1976. Bacterial infection in the blue crab,
Callinectes sapidus: course of infection and histopathology. J. Invert.
Path. 28:25-36.

36. Kampelmacher, E.H. 1977. The spread and significance of
salmonellae in surface waters in the Netherlands. In A.W. Hoadley and
B.3. Dutka (ed.), Bacterial indicators: health hazards associated with
water. Amer. Soc. for Testing and Materials, Philadelphia.

37. Kaper, 3., H. Lockman, R.R. Colwell, and S.W. Joseph. 1979.
Ecology, serology, and entertoxin production of Vibrio cholerae in
Chesapeake Bay. Appl. Env. Microbiol. 37:91.

38. Keel, 3.A. and D.W. Cook. 1975. Isolation of Vibrio parahaemo-
lyticus from the Mississippi Sound. 3. Miss. Acad. Sci. 20:30.

39. Kelly, C.B. and W. Arcisz. 1954. Survival of enteric organisms in
shellfish. Pub. Health Reports 69:1205.








40. Kennedy, M.E. 1969. Salmonella serotypes isolated from turtle
environment. Can. 3. Microbiol. 15:130.

41. Loken, K.I., K.H. Culbert, R.E. Solee, and B.S. Pcmeroy. 1968.
Microbiological quality of protein feed supplements produced by
rendering plants. Appl. Microbiol. 16:1002.

42. Martin, R.E. and G.T. Pitt. Undated. Handbook of state and federal
microbiological standards and guidelines. National Fisheries Institute,
Washington, D.C.

43. McCullough, N.B. and C.W. Eisele. 1951. Experimental human
salmonellosis: IV. Pathogenicity of strains of S. pollorum obtained
from spray-dried whole egg. 3. Infect. Dis. 89:259.

44. McCullough, N.B. and C.W. Eisele. 1951. Experimental human
salmonellosis: III. Pathogenicity of strains of S. newport, S. derby,
and S. bareilly obtained from spray-dried whole egg. 3.Infect. Dis.
89:209.

45. McCullough, N.B. and C.W. Eisele. 1951. Experimental human
salmonellosis: I. Pathogenicity of strains of S. meleagridis and S.
anatum obtained from spray-dried whole egg. 3. Infect. Dis. 88:278.

46. Murchelano, R.A. and 3. L. Bishop. 1969. Bacterial study of
laboratory-reared juvenile american oysters (Crassostrea virginica).
3. Invert. Path. 14:321.

47. Murchelano, R.A. and C. Brown. 1968. Bacterial study of the
natural flora of the eastern oyster, Crassostrea virginica. 3. Invert.
Path. 11:519.

48. National Marine Fisheries Service. 1982. Fisheries of the United
States 1981. National Marine Fisheries Service, United States
Department of Cramerce, Washington, D.C.

49. National Research Council. Ccrmittee on Food Protection. 1975.
Prevention of microbial and parasitic hazards associated with processed
foods. pp. 4-9. National Academy of Sciences, Washington, D.C.

/ 50. National Research Council. crnmittee on Salmonella. 1969. An
evaluation of the Salmonella problem. National Academy of Sciences,
Washington, D.C.

S51. Oblinger, 3.L. and 3.A. Koburger. 1975. Understanding and teaching
the most probable number technique. 3. Milk Food Technol. 38:540.

52. Pagou, S., W. Sonnabend, and U. Krech. 1974. Epidemiologische
zusannenhaenge zwischen mnnschlichen und tierischen salmonellen--
ausscheidern und deren urrwelt im schweizerichen Bodenseeraun. Zbl.
Bakt. Hyg. I Abt. Orig. B 158:395.







53. Presnell, M. and 3.3. Miescier. 1971. Coliforms and fecal
coliforms in an oyster-growing area. Water Poll. Control Fed. 3.
43:407.

54. Rudat, K.D., G. Beck, W. Frank, and G. Mrugowsky. 1966. Ueber das
vorkomnen von salmonellen bei reptilien im zoologischen gaerten.
Pathol. Micro. 29:623.

55. Schubert, R.H.W. and P. Scheiber. 1979. Untersuchungen ueber das
vorkomnen von salmonellen in trinkwasser togoischer wasserversorguns-
anlagen. Zbl. Bakt. Hyg. I Abt. Orig. B 168:356.

56. Silliker, John H. 1982. The Salmonella problem: current status and
future direction. 3. Food. Protect. 45:661.

57. Silliker, John H. 1980. Status of Salmonella --ten years later.
3. Food Protect. 43:307.

58. Silliker, 3.H. and D.A. Gabis. 1976. ICOSF methods studies. VII.
Indicator tests as substitutes for direct testing of dried foods and
feeds for Salmonella. Can. 3. Microbiol. 22:971.

59. Sizemore, P.K., R.R. Colwell, H.S. Tubiash, and T.E. Lovelace.
1975. Bacterial flora of the hemolymph of the blue crab, Callinectes
sapidus: numerical taxonomy. Appl. Microbiol. 29:393.

60. Slanetz, L.W. C.H. Bartley, and K.W. Stanley. 1968. Coliforms,
fecal streptococci and Salmonella in seawater and shellfish. Health
Lab. Sci. 5:66.

61. Stewart, Adelle W. 1981. Survival of bacteria in "soul foods" at
10-centigrade. 3. Food Protect. 44:271.

62. Sunki, G.R., R. Annapureddy, D.R. Rao. 1978. Microbial, biochem-
ical and organoleptic changes in ground rabbit meat stored at 5 to 7 C.
3. Ani. Sci. 46:584.

63. Tanner, F.W. 1944. The microbiology of foods, second edition.
p. 608. Garrand Press, Champaign, Illinois.

64. Tennant, A.D. and 3.E. Reid. 1961. Coliform bacteria in seawater
and shellfish. I. Lactose fermentation at 35.5 C and 44 C. Can. 3.
Microbiol. 7:725.

65. Thi Son, Nguyen and G. H. Fleet. 1980. Behavior of pathogenic
bacteria in the oyster, Crassostrea cormercialis, during depuration,
re-laying, and storage. Appl. Env. Microbiol. 40:994.

i 66. United States Food and Drug Administration. 1978. Bacteriological
analytical manual, fifth edition. Association of Official Analytical
Chemists, Washington, D.C.






56

67. Vanderzant, C., C.A. Thompson, Jr., and S.M. Ray. 1973. Microbial
flora and level of Vibrio parahaemolyticus of oysters (Crassostrea
virginica), water and sediment from Galveston Bay. J. Milk Food
Technol. 36:447.

68. Watson, James 3. 1974. The hemolysins of Edwardsiella tarda. M.S.
thesis, University of Florida, Gainesville.

69. Williams-Walls, N.3. 1968. Clostridium botulinum type F: isolation
from crabs. Science. 162:375.

70. Woodburn, M.J. 1964. Incidence of Salmonella in dressed
broiler-fryer chickens. Appl. Microbiol. 12:492.

71. Woodburn, M.J. and D. H. Strong. 1960. Survival of Salmonella
typhimurium, Staphylococcus aureus, and Streptococcus faecalis frozen
in simplified food substrates. Appl. Microbiol. 8:109.














BIORAPHICAL SKETCH

Margaret Bury Fraiser was born on April 29, 1959, in Yreka,

California. She graduated from A & M Consolidated High School, College

Station, Texas, in May, 1977. She attended Sterling College in

Sterling, Kansas, and Universitaet Salzburg in Salzburg, Austria, and

received a Bachelor of Science degree in youth leadership from Sterling

College in December, 1980. She enrolled as a graduate student in the

Food Science and Human Nutrition Department at the University of

Florida in January, 1981. She expects to receive a Master of Science

degree in food science and human nutrition with a minor in microbiology

in December, 1982.










I certify that I have read this study and that in my opinion it
conforms to acceptable standards of scholarly presentation and is fully
adequate, in scope and quality, as a thesis for the degree of Master of
Science.




ohn A. Kobur eC, Chaian
I yfessor of Wod Science
and Human Nutrition

I certify that I have read this study and that in my opinion it
conforms to acceptable standards of scholarly presentation and is fully
adequate, in scope and quality, as a thesis for the degree of Master of
Science.




3 as/L. Obl ger
Professor ofvFood Scien e
and Human Nutrition

I certify that I have read this study and that in my opinion it
conforms to acceptable standards of scholarly presentation and is fully
adequate, in scope and quality, as a thesis for the degree of Master of
Science.




Samuel R. Farrah
Associate Professor of Micro-
biology and Cell Science

This thesis was submitted to the Graduate Faculty of the College of
Agriculture and to the Graduate Council, and was accepted as partial
fulfillment of the requirements for the degree of Master of Science.

December 1982



Dean, 6/lege of Agriculto




Dean for Graduate Studies and
Research




University of Florida Home Page
© 2004 - 2010 University of Florida George A. Smathers Libraries.
All rights reserved.

Acceptable Use, Copyright, and Disclaimer Statement
Last updated October 10, 2010 - - mvs


TRACE ROUTE

Total Execution Time: 25 Milliseconds

MILLISECOND   CLASS.METHODMESSAGE
0sobekcm_page_globals.constructor
0sobekcm_page_globals.constructorApplication State validated or built
0sobekcm_database.verify_item_lookup_object
0sobekcm_page_globals.constructorNavigation Object created from URI query string
0sobekcm_database.verify_item_lookup_object
0sobekcm_page_globals.display_itemRetrieving item or group information
0sobekcm_page_globals.get_entire_collection_hierarchyRetrieving hierarchy information
0sobekcm_assistant.get_entire_collection_hierarchy
0cached_data_manager.retrieve_item_aggregation
0cached_data_manager.retrieve_item_aggregationFound item aggregation on local cache
0item_aggregation_builder.get_item_aggregationFound 'all' item aggregation in cache
0system.web.ui.page.page_load (ufdc.page_load)
0sobekcm_page_globals.constructor.on_page_load
0html_echo_mainwriter.add_style_referencesAdding style references to HTML
0html_echo_mainwriter.add_text_to_pageReading the text from the file and echoing back to the output stream
25html_echo_mainwriter.add_text_to_pageFinished reading and writing the file