.. ‘ .52? .1) :. 1.... .7 .5. :1 .v... .v. Kahuna .. $4 .. x '25? ...:::r. 5!. 11 seifidg up? . . I, .2. .5 i E. x Zn.» Li. .. u. I; :5 ‘ 2 i .4 . ; flaw». an“. .2; I. THESIS Jig UBRARY Miciztg State University This is to certify that the dissertation entitled BACTERIAL KIDNEY DISEASE (BKD) IN MICHIGAN SALMONIDS presented by Alaa-Eldin Abdel Mouty Mohamed Eissa has been accepted towards fulfillment of the requirements for the Ph.D. degree in Pathology Mom ,5 ”tango“ Major Professor’s Signature We ate MSU is an Affirmative Action/Equal Opportunity Institution PLACE IN RETURN Box to remove this checkout from your record. 10 AVOID FINES return on or before date due. MAY BE RECALLED with earlier due date if requested. DATE DUE DATE DUE DATE DUE 2/05 c:/CiRC/DateDue.iMd-p.15‘ _, ._ . _____—__ —— BACTERIAL KIDNEY DISEASE (BKD) IN MICHIGAN SALMONIDS By Alaa-Eldin Abdel Mouty Mohamed Eissa A DISSERTATION Submitted to Michigan State University in partial fulfillment of the requirements for the degree of DOCTOR OF PHILOSOPHY Department of Pathobiology and Diagnostic Investigation 2005 ba d:s WI ABSTRACT BACTERIAL KIDNEY DISEASE (BKD) IN MICHIGAN SALMONIDS By Alaa-Eldin Abdel Mouty Mohamed Eissa Bacterial Kidney Disease (BKD) caused by a Gram-positive bacterium, Renibacterium salmoninarum (R. salmoninarum) is a systemic disease that threatens the expansion of both cultured and wild salmonines worldwide. Historical records show that BKD affected Michigan’s brook trout as early as 1955 (Allison 1958) and continued its spread to most of other salmonid species such as coho salmon (Oncorhynchus kisutch) spawners in the late sixties (MacLean and Yoder 1970) followed by a potent epizootic among the Chinook salmon (Oncorhynchus tshawytscha) populations in Lake Michigan in the late 1980's (Holey et al. 1998). Despite the magnitude of the setback to fisheries conservation efforts in Michigan, relatively little research has been done on R. salmoninarum, primarily due to its slow-growing nature, which takes up to 12 weeks to obtain growth upon primary isolation. The tissue processing protocol and optimized culture technique developed in this study, has facilitated the isolation of large number of R. salmoninarum and achieved a remarkably shorter incubation time for primary isolation. A sort of disagreement in results among the three used diagnostic assays (nPCR, Culture, Q-ELISA) was recorded during BKD testing of the teral phas lest; pate role the tha tha pre BK ha' pie inl se a I fro an feral and captive salmonid stocks for BKD, which may reflect the different phases of R. salmoninarum infection at the time of sampling. Further, the testing results demonstrated the presence of six patterns, with each of the patterns representing a probable stage along the course of R. salmoninarum infection. Data also demonstrated that male spawner salmon play the same role played by female in transmission of R. salmoninarum by shedding of the bacteria and its soluble antigens in milt. Moreover, results revealed that Hinchenbrook coho strain is more susceptible to R. salmoninarum than the Michigan adapted coho salmon strain. Data also, supported the previous reports, which indicated that brook trout are highly susceptible to BKD. Also, data showed that prevalence of R. salmoninarum in the hatchery-raised brook trout is the same as wild strains residing in the water source and that Iron River brook trout are more vulnerable to R. salmoninarum infection than Assinica strain. Last, external parasites could played a possible role in initiation, speeding up the R. salmoninarum infection and BKD occurrence and mortalities is not related to changes in seasons. Finally, findings indicated that the adult parasitic sea lamprey is a new host range for R. salmoninarum where the bacteria were isolated from the kidneys of a number of sea lampreys from Lake Ontario in 2003 and 2004. Copyright by ALAA-ELDIN ABDEL MOUTY MOHAMED EISSA 2005 DEDICATION To my wife, children, and parents More wou:. fidd: ment Roccc and It In advls Anim Fnh IOIQ VaME ACKNOWLEDGEMENTS I would like to express my sincere gratitude to my major advisor Dr. Mohamed Faisal, for his sincere advising and endless support. This study would not be possible without the integration of his profound experience in the field of fish diseases. Also, I wish to express my deep appreciation to my advisory committee members Dr. Scot Fitzgerald, Dr. John Gerlach, Dr. Matti Kiupel and Dr. Rocco Cipriano for their tremendous support, valuable discussions, patience and fruitful collaboration. Special appreciation goes to Dr. Ehab Elsayed, for his sincere, endless advising and support. I also would like to thank all members of the Aquatic Animal Health Laboratory at Michigan State University for their assistance. My appreciation also, goes to Mr. Gary Whelan and all Michigan Department of Natural Resources personnel who have facilitated sample collection. I wish to express my appreciation to Dr. Clifford Starliper at the National Fish Health Laboratory in Virginia for his valuable discussion and suggestions for culture modifications. Also, I would like to thank Mr. John Hnath for his valuable comments and suggestions during writing the dissertation. I would like to thank the Egyptian government for giving me the opportunity and means to study in the USA. Deep appreciation also goes to the Great Lake Fisheries Trust (GLFT) for funding most of the research described in this dissertation. vi grate— sacrf ace: My deep gratitude goes to my beloved mother, father, brothers and sister for their sincere love and support throughout my entire lifetime. Lastly, I am grateful to my wife, Hend Nada and my kids for their eternal love, patience, sacrifices, and sharing the responsibility that enabled me to successfully accomplish my studies in the USA. vii usr or LIST or INTRO cumr‘ I.I'IlSIOr II. The p. I) N 2) C 3) Is 4.: P SIB 6IA 7)A 8) l.‘ ”first I) D IV. Epiz 1)( 3H TABLE OF CONTENTS LIST OF TABLES ....................................................................... xi LIST OF FIGURES ...................................................................... xiii INTRODUCTION ......................................................................... 1 CHAPTER 1. LITERATURES REVIEW. .......................................... 4 l. Historical perspectives ............................................................... 4 II. The pathogen .......................................................................... 5 1) Nomenclature and current classification of the etiological agent. . .. 5 2) Cell morphology ......................................................................... 6 3) Isolation, culture and culture characteristics ............................. 6 4) Preservation of cultures ....................................................... 9 5) Biochemical characteristics .................................................. 1O 6) Antibiotic susceptibility ..................................................... 10 7) Antigenic characteristics and virulence factors ......................... 11 8) Molecular and genetic diversity ............................................ 12 Ill. The disease .......................................................................... 13 1) Disease Course ................................................................. 13 3) External signs ............................................................ 13 b) Internal Lesions ......................................................... 14 c) Histopathology .......................................................... 15 2) Susceptibility .................................................................... 16 3) Pathogenesis and Immunity ................................................ 17 a) Process of infection and pathogenesis ........................... 17 b) Effect of BKD on host immune response ........................ 19 0) Environmental factors ................................................. 20 Effect of diet ........................................................ 20 Effect of temperature ............................................. 21 Effect of estuarine and salt-water environment ............ 22 IV. Epizootiology ......................................................................... 23 1) Geographical Distribution ..................................................... 23 2) Host range ........................................................................ 24 3) Disease transmission .......................................................... 25 a) Source of infection ...................................................... 25 b) Horizontal transmission ............................................... 25 c) Vertical transmission ................................................... 26 d) Fish as possible vectors and carriers .............................. 27 e) Possible vectors other than fish ..................................... 28 f) Reservoirs ................................................................ 29 viii 3II~I VI. Offe- WICon llC ZIA 3‘IE 4; P CHAP RENM V. Diagnosis of BKD ..................................................................... 29 1) Isolation and bacteriological identification of the agent ............... 29 2) Antigen-antibody reactions ................................................... 30 a) Agglutination test ........................................................ 30 b) Immunofluorescence ................................................... 30 c) Enzyme linked immunosorbent assay (ELISA) .................. 31 d) lmmunohistochemistry (IHC) ......................................... 32 3) Polymerase chain reaction (PCR) .......................................... 33 VI. Differential diagnosis ............................................................... 34 VII. Control ................................................................................. 36 1) Chemotherapy .................................................................... 36 ' 2) Adult segregation ................................................................ 38 3) Eradication ........................................................................ 39 4) Prophylaxis ........................................................................ 4O 1. Reducing the risk of BKD introduction .............................. 40 2. Vaccination ................................................................. 4O Gap of BKD knowledge in Michigan before 2002 ................................ 42 CHAPTER 2. PRIMARY ISOLATION OF RENIBACTERIUM SALMONINARUM FROM NATURALLY INFECTED SALMONINE STOCKS IN MICHIGAN USING A MODIFIED TISSUE PROCESSING PROTOCOL .............................................................................. 46 1. Abstract .............................................................................. 46 2. Introduction .......................................................................... 48 3. Material and Methods ............................................................ 51 4. Results ................................................................................ 58 1) Effect of sample processing and culture technique on the primary isolation of R. salmoninarum ............................... 58 2) Prevalence of R. salmoninarum isolated from Michigan salmonines .................................................................. 58 3) Confirmation of the retrieved isolates 60 5. Discussion ........................................................................... 62 CHAPTER 3. DIAGNOSTIC TESTING PATTERNS OF RENIBACTERIUM SALMONINARUM INFECTION IN SOME FERAL AND CAPTIVE SALMONINES ......................................................... 75 1. Abstract .............................................................................. 75 2. Introduction ......................................................................... 77 3. Material and Methods ............................................................ 8O 4. Results 84 5. Discussion ........................................................................... 86 ix CHAPTER 4. CURRENT STATUS OF RENIBACTERIUM SALMONINARUM INFECTION IN FERAL CHINOOK AND COHO SALMON AT MICHIGAN WEIRS AND HATCHERIES ........................ 96 1. Abstract .............................................................................. 96 2. Introduction ......................................................................... 98 3. Material and Methods ............................................................ 102 4. Results ............................................................................... 106 5. Discussion ........................................................................... 113 CHAPTER 5. PREVALENCE, SHEDDING AND SPREAD OF RENIBACTERIUM SALMONINARUM IN BROOK TROUT (SALVELINUS FONTINALIS) WITH SPECIAL EMPHASIS ON THE ASSOCIATED DISEASE EPIZOOTICS IN MICHIGAN ........................ 134 1 . Abstract .............................................................................. 1 34 2. Introduction ......................................................................... 136 3. Material and Methods ............................................................ 139 4. Results ............................................................................. 146 3) Prevalence of R. salmoninarum infections in hatcher captive and wild brook trout .......................................... 146 b) BKD outbreaks (epizootics) among the hatchery raised brook trout ................................................................ 148 5. Discussion ........................................................................... 152 CHAPTER 6. FIRST RECORD OF RENIBACTERIUM SALMONINARUM IN SEA LAMPREY (PETROMYZON MARINUS) FROM THE GREAT LAKES BASIN ................................................ 169 1 . Abstract .............................................................................. 169 2. Introduction .......................................................................... 170 3. Material and Methods ............................................................. 173 4. Results ................................................................................ 177 5. Discussion ........................................................................... 179 CHAPTER 7. CONCLUSION AND FUTURE RESEARCH ..................... 184 LIST OF REFERENCES ................................................................. 189 T Table ‘. of Rer...’ Table 2. oi Rent: Table 3. chlreck watershi Table 4. trout bro hatcten Table 5 D'Opaga Tabie 6. 0n the 1 isolates Table 7_ USGC an Table 8. Salmon; Table 9‘ IeIaI Spa geogfap Table 1; 2005 _____ TabIe ll Tabie 12 Ol'arian fl able 13. gameteS LIST OF TABLES Table 1. Summary of the morphological and biochemical characteristics of Renibacterium salmoninarum ....................................................... Table 2. Summary of the metabolic, antigenic and pathogenic characters of Renibacterium salmoninarum ...................................................... Table 3. Prevalence of Renibacterium salmoninarum in fall returning chinook and coho salmon spawners from Lake Michigan and Lake Huron watersheds ................................................................................. Table 4. Prevalence of Renibacterium salmoninarum in captive char and trout broodstocks collected in fall 2002 from Michigan state fish hatcheries .................................................................................... Table 5. Prevalence of Renibacterium salmoninarum in 10-15-month-old propagated fish. ........................................................................... Table 6. Results of conventional biochemical and motility tests performed on the 12 representative Renibacterium salmoninarum isolates ....................................................................................... Table 7. Standard concentration and expected inhibition zones for each used antibiotic disc ........................................................................ Table 8. Inhibition zones in mm produced by the 12 Renibacterium salmoninarum isolates used in the antibiogram ................................... Table 9. Frequencies of different diagnostic testing patterns of salmonid feral spawners and captive broodstocks collected from different geographical locations in Michigan during fall 2002 .............................. Table 10. Details of samples collected from spawning chinook and coho salmon returning to egg-take weirs throughout the period from 2001- 2005 .......................................................................................... Table 11. Chinook salmon juvenile fingerlings collected from Michigan state fish hatcheries in the period from 2002-2005 ............................. Table 12. Renibacterium salmoninarum prevalence and intensity in ovarian fluid and milt of the 2004 chinook and coho salmon Spawners.... Table 13. Renibacterium salmoninarum prevalence in kidney and gametes of the 2004 chinook salmon spawners ................................... xi 44 45 67 68 69 7O 71 72 92 120 121 122 123 Table 1 among I COTTE’SQ 2001 to Table 1 through. fifigefir TaNe 1 among Slockm TaNe‘ Ottafic Table 1 based Table 14. Renibacterium salmoninarum prevalence in Kidney and gametes of the 2004 coho salmon spawners (Shedding agreements possibilities between kidney and gametes) ......................................... Table 15. Renibacterium salmoninarum infection prevalence and intensity among the Little Manistee River chinook salmon feral spawners and their corresponding hatchery raised fingerlings throughout the period from 2001 to 2005 ................................................................................ Table 16. Renibacterium salmoninarum infection prevalence and intensity among the Swan River Weir chinook salmon feral spawners and their corresponding hatchery raised fingerlings throughout the period from 2001 to 2005 ............................................................................... Table 17. Details of samples collected from brook trout broodstocks throughout the period from 2001-2004 and pre-stocking 18-month-old fingerlings collected throughout the period from 2002-2005 .................... Table 18. Renibacterium salmoninarum infection prevalence and intensity among brook trout broodstocks and their corresponding 18 months pre- stockin'g fingerlings throughout the period from 2001 — 2005 .................. Table 19. Prevalence of Renibacterium salmoninarum in 2003-2004 Lake Ontario sea lampreys using nPCR, Q-ELISA and culture ...................... Table 20. Confirmation of R. salmoninarum isolates using some culture- based assays, serological and molecular assays ................................. xii 124 125 127 159 160 181 182 Figure I mthd waters: Figure I mfiflnm. watersh '~ 1 Fgae, CMDCCK Figure A salmon FIQU'Q : Capfiye Figure SEIITITQr and 23 FInge fe'al SI IIII'OUg FIQUre SEImO Wefis! FIgure IEmalI Weir; FISUre "Item; Cortes FIQUIE anions FISUre “GHQ; LIST OF FIGURES Figure 1. Prevalence of Renibacterium salmoninarum in male and female returning chinook salmon spawners from Lake Michigan and Lake Huron watersheds .................................................................................. 73 Figure 2. Prevalence of Renibacterium salmoninarum in male and female returning coho salmon spawners from Platte River Weir, Lake Michigan watershed .................................................................................... 74 Figure 3. Frequencies of different diagnostic testing patterns of feral chinook salmon spawners ............................................................... 93 Figure 4. Frequencies of different diagnostic testing patterns of feral coho salmon spawners collected from the Platte River Weir .......................... 94 Figure 5 - 6. Frequencies of different diagnostic testing patterns of captive hatchery broodstock ............................................................ 95 Figure 7. Prevalence of Renibacterium salmoninarum in feral chinook salmon spawners collected from two of Michigan weirs between 2001 and 2005 ..................................................................................... 129 Figure 8. Renibacterium salmoninarum prevalences and intensities in feral spawner coho salmon strains returning to Platte River Weir throughout 2001-2004 .................................................................... 130 Figure 9. Prevalence of Renibacterium salmoninarum in feral Chinook salmon spawners males and females collected from two of Michigan weirs between 2001 and 2005 131 Figure 10. Renibacterium salmoninarum prevalence and intensity in females and males of coho salmon spawners returning to Platte River Weir throughout the period from 2002-2004 ....... . ................................ 132 Figure 11. Renibacterium salmoninarum prevalence and intensity of infection in gamete donor feral spawner coho salmon strains versus their corresponding 18-month juvenile fingerlings throughout 2001-2004 ......... 133 Figure 12. Prevalence and intensity of Renibacterium salmoninarum among the adult brook trout collected through 2001-2003 ...................... 161 Figure 13. Renibacterium salmoninarum Prevalence and intensity in kidneys and gametes of the Iron River brook trout broodstock in from xiii T I Marque Figure Daseas- Figure i hear; r Figure‘ hea‘l’y f: retreta Reniba, Figure i were I. Years at Fig-are 1 chronic brook tr kfifieyt Figure ‘ chronic brook Ii aifigen Figure Charac Marquette State Fish Hatchery. ............................................ 162 Figure 14. An Iron River Brook trout fingerling with Bacterial Kidney Disease. .................................................................................. 163 Figure 15. Kidney tissue of Iron River brook trout fingerling exhibiting heavy Renibacterium salmoninarum infection .................................... 164 Figure16. Kidney tissue of Iron River brook trout fingerling exhibiting heavy Renibacterium salmoninarum infection after enhanced antigen retrieval procedures using Alkaline Phosphatase Red and goat anti- Renibacterium salmoninarum antibody ............................................. 165 Figure 17. Hematoxylin and Eosin stained slide of kidney showing a severe granulomatous reaction that is replacing kidney tissues of a 3 years old Assinica brook trout ......................................................... 166 Figure 18. An immunohistochemical stained Kidney tissue section with chronic multi-focal granulomatous reaction from a 3 years old Assinica brook trout with absence of bacterial cells or antigen from the affected kidney tissues. ............................................................................ 167 Figure 19. An immunohistochemical stained Kidney tissue section with chronic multi-focal granulomatous reaction from a 3 years old Assinica brook trout exhibiting a mild chronic presence of bacterial cells or antigens after enhanced antigen retrieval procedures ......................... 168 Figure 20. Nested PCR assay performed on isolates showing the characteristic 320 bp band of R. salmoninarum isolates ......................... 183 xiv (p57 salrr BKD Atiar Scot ram! USA dise Ame INTRODUCTION Bacterial Kidney Disease (BKD), caused by the Gram-positive bacterium Renibacterium salmoninarum (R. salmoninarum), is a systemic disease that afflicts salmonid fish populations worldwide. R. salmoninarum is an obligate intracellular pathogen that is transmitted both horizontally (Mitchum and Sherman 1981; Bell et al 1984) and vertically (Evelyn et al. 1984, 1986). R. salmoninarum pathogenicity relies upon a number of extracellular proteins (ECP) that possess immunosuppressive (Turaga et al. 1987; Fredriksen et al. 1997). The ECP contain a water-soluble, cell surface, 57-kDa protein (p57) that has been demonstrated to be a major virulence factor of R. salmoninarum (Getchell et al. 1985; reviewed in Wiens and Kaattari 1999). BKD was originally known as the Dee Disease, due to its initial discovery in Atlantic salmon (Salmo salar) from Aberdeenshire Dee and the River Spey in Scotland in 1930 (Anonym 1933). Few years later the disease was first reported in brook trout (Salve/inus fontinalis), brown trout (Salmo trutta) and rainbow trout (Oncorhynchus mykiss) reared in a hatchery in Massachusetts, USA (Belding and Merrill 1935). Since the appearance of this initial report, the disease was reported in most of the cultured and wild salmonines from North America. Since, the first report of BKD in brook trout yearlings from Michigan in 1 955, the disease quickly spread to affect other salmonid species such as echo and chinook salmon. BKD resulted in epizootics among coho salmon spawners in 1967 (McLean and Yoder 1970), chinook salmon spawners Fais; prog sub" caus WDCI numt Thei star ‘— Wbdi obufi and C nalur SBIm( during the 1980s (Holey et al. 1998) and recently harvested thousands of hatchery raised brook trout between the period from 2002 to 2003 (Eissa 2005, this dissertation). These continuous eruptions of BKD outbreaks and high prevalence of the R. salmoninarum among almost all the tested salmonid populations throughout this study revealed a new fact that R. salmoninarum is enzootic in Michigan salmonines and Great Lakes water basin. Despite the aforementioned facts, the publications describing the status of BKD in Michigan salmonines fish species are fairly scarce (Hnath and Faisal 2005). This intensifies the needs to fill the gap between the rapid progress of BKD and research performed on BKD in Michigan. This submitted study is a trial to fill some of these gaps, by studying both the causative agent and the affected salmonid fish populations in Michigan. In brief, chapter, 2 in this study dealt with the development of tissue processing protocol and culture technique that facilitated the isolation of large number of R. salmoninarum isolates within relatively short incubation time. The isolation of such large number of isolates from different salmonids, ages, strains, and locations lead to a conclusion that BKD is enzootic in Michigan. Chapter 3 describes the analysis of different diagnostic testing patterns produced from different agreements and disagreements between results obtained by three BKD diagnostic assays (Nested PCR, Quantitative ELISA, and Culture) which allowed me to track the progress and different stages of naturally occurring R. salmoninarum infection in some Michigan feral salmonines. In chapter 4 the ability of both chinook and coho females and mae disc. fish: bot mete 8m”- ufied Fume too; Fina salmt butn Doss males to shed R. salmoninarum through the ovarian fluid and milt has been discussed. These data shed the light on the possible role of male spawner fish to spread the disease through shedding the pathogen via the milt. Thus, both males and females should equally utilized for BKD testing and culling procedures in weirs. ln chapters 5, the retrieved data supported the previous reports, which emphasized that brook trout are highly susceptible to R. salmoninarum infection. Also, this study shed the light on the possible contribution of a number of factors to development of BKD epizootics in Michigan hatcheries. Further, the study suggested a number of efficacious control strategies for stopping the BKD associated mortalities and minimizing the spread of BKD. Finally, data in chapter six demonstrated the successful isolation of R. salmoninarum from the kidneys of adult sea lamprey (Petromyzon man'nus) but not from blood or any other organ, which indicated that sea lamprey, is a possible non salmonid host range for R. salmoninarum infection. CHAPTER ONE LITERATURE REVIEWS |. Historical perspectives Bacterial Kidney Disease (BKD), caused by the Gram-positive bacterium Renibacterium salmoninarum, is a systemic disease that afflicts salmonid fish populations worldwide. The condition was originally described as the Dee Disease because it was first observed among Atlantic salmon (Salmo salar) from Aberdeenshire Dee and the River Spey in Scotland in 1930 (Anonym 1933 and Smith 1964) Other synonyms of the disease include Kidney Disease, Corynebacterial Kidney Disease and Salmonid Kidney Disease (Fryer and Sanders 1981 ). A few years later, Belding and Merrill (1935) described a very similar infection that caused losses in brook trout (Salve/inus fontinalis), brown trout (Salmo trutta) and rainbow trout (Oncorhynchus mykiss) reared in a hatchery in Massachusetts, USA. By 1953, due to serious outbreaks, BKD had become a limiting factor in rearing brook trout, brown trout, rainbow trout, chinook salmon (Oncorhynchus tshawytscha), coho salmon (Oncorhynchus kisutch) and sockeye salmon (Oncorhynchus nerka) in many hatcheries in the State of Washington (Earp et al. 1953). In the following year, the disease was found in the feral salmon in the same state (Rucker et al. 1954). In 1955, BKD spread to the Great Lakes basin with the introduction of salmonines and their products from the Pacific Northwest and . The : there virtue exist II. Thi 1)No 82 W88 8 Earp later I plus c Comp this be IITEy ic (Allison 1958). Reports from Canada linked the disease to mortalities in wild salmonines from Nova Scotia (Pippy 1969; Paterson et al. 1979) to British Columbia (Evelyn et al. 1973; 1981). By 1988, the disease became widespread in Europe (England, France, Finland, Germany, Iceland, Italy, Scotland, Spain, Turkey and Yugoslavia), North America (USA and Canada), and Japan (reviewed in Bullock and Herman 1988; Fryer and Lannan 1993). The disease continued its spread to Chile (Sanders and Barros 1986) and there is a current consensus among fish health professionals that BKD is virtually prevalent in all parts of the world where wild or cultured salmonines exist (European Commission 1999). II. The pathogen 1) Nomenclature and current classification of the etiological agent Based on Gram stain properties, morphology, the causative bacterium was suggested to be a member of the genus Corynebacterium by Ordal and Earp (1956) and subsequently by Smith (1964). Sanders and Fryer (1980) later refuted this classification based on the absence of mycolic acid, guanine plus cytosine (G + C) content of DNA, cell wall sugar and amino acid compositions of the peptidoglycan cell wall layer. The authors proposed that this bacterium formed a single species in a new genus Renibacterium and they identified the bacterium as Renibacterium salmoninarum (Sanders and Fryer 1980). Sequencing of the 16S ribosomal ribonucleic acid (rRNA) from R. salmoninarum (Gutenberger et al. 1991) and recent evaluation of G + C content (Banner et al. 1991) placed the organism in the Gram-positive eubacterial subdivision of actinomycetes. Arthrobacter and Micrococcus spp. are the closest relatives to R. salmoninarum (Holt et al. 2001). 2) Cell morphology Renibacterium salmoninarum is a short rod (0.3-1.0 by 1-1.5 um), Gram- positive, non-sporulated, non-capsulated, non-motile, and non acid-fast bacterium that is arranged in pairs (diplobacilli) and rarely as short chains (Sanders and Fryer 1980). Renibacterium salmoninarum consists of two regions; a central region filled with lightly stained filaments (represent DNA) and a peripheral region filled with small, electron dense ribosomes (Young and Chapman 1978). 3) Isolation, culture and cultural characteristics Renibacterium salmoninarum is a slow growing organism (Sanders and Fryer 1980). Earp et al. (1953) cultured the bacterium on an artificial medium for the first time from infected kidney tissues on a medium that consisted of fish extract, glucose, yeast extract and meat infusion in agar. The authors achieved limited growth with first appearance of colonies after more than two WEE’ Nu. grouI funr. usec rese: U\ He I6» Slit er; Ints 60' combined with sulfaguanidine and sulfadiazine (Allison 1958). Wolf and Dunbar (1959) tested 34 therapeutic agents including erythromycin thiocyanate and sulfamerazine on 16 strains of R. salmoninarum using the disk method for drug sensitivity screening followed by in vivo feeding trials with experimentally infected fish. They concluded that erythromycin fed at the rate of 100 mg per kg of fish for 5 consecutive days gave the best results. Generally, due to the occurrence of the bacterium intracellularly as well as extracellularly, these treatments only suppressed the systemic spread of the organism and induced partial relief (Amos 1977). Intramuscular (i.m.) and lntraperitoneal (i.p.) administration of sulfonamide drugs significantly reduced prespawning mortality among chinook salmon broodstocks being hold prior to spawning (Amend and Fryer 1968). However, sulfonamides administered by i.m. or i.p. routes often produced sterile abscesses at the injection site in adults and induced mortalities and teratogenicity with their progeny (Amos 1977) In an attempt to reduce or prevent vertical transmission of BKD, salmon eggs were water hardened for 1hour in 2 ppm erythromycin (Amos 1977). However, erythromycin was rapidly eliminated and dropped below detectable level within 24 hours after water hardening (Evelyn et al. 1986a). Monthly subcutaneous (S. C.) injection of adult female Pacific salmon with 11mg/kg erythromycin reduced pre-spawning mortality due to BKD (Klontz 1983). .lnterestingly, erythromycin remains in the eggs of injected females for up to 50 days before spawning (Evelyn et al. 1986; Moffitt 1991). It is believed that 37 v I p “mt em; min. dlSlr the] 2) A< erythromycin residues in the eggs assist in preventing vertical transmission of R. salmoninarum from parents to their offspring (Lee and Evelyn, 1994). Detectable amounts of erythromycin often remain in the perfused tissues of both juvenile and adult salmon long after they are no longer detected in the plasma and muscle (Moffitt 1991; Haukenes and Moffitt 1999) and this possibly contributes to the efficacy of erythromycin against the slow growing R. salmoninarum. Feeding erythromycin can efficiently reduce mortalities of infected hatchery raised salmonids (Wolf and Dunbar 1959; Austin 1985; Moffitt and Bjornn 1989). A dose of 200 mg/ kg body weight for 21 days was most effective (Moffitt, 1992). Erythromycin is only available as an lnvestigational New Animal Drug (INAD) through the Food and Drug Administration (FDA) (Moffitt 1992). Austin (1985) tested more than 70 antimicrobial compounds both in vivo and in vitro and found that clindamycin, erythromycin, kitasamycin, penicillin G and spiramycin were useful for combating early clinical BKD cases while cephradine, lincomycin and rifampicin were effective prophylactically but had limited use therapeutically. Hsu et al. (1994) tested the efficacy of enrofloxacin in treating BKD in vitro and in vivo and they concluded that low minimal inhibition concentrations (Mle), high bioavailability and large volume distribution of the antibiotic make it good candidate for use as effective therapeutic against BKD. 2) Adult segregation 38 us. \‘l' E 3)! erac man sa/n their 1992 dish Broodstock segregation is a more practical method for reducing the prevalence and levels of R. salmoninarum in hatchery-reared salmon (Pascho et al. 1991) and for increasing survival during their downriver migration and entry into seawater (Pascho et al. 1993; Elliot et al. 1995). This procedure aims to interrupt vertical transmission of R. salmoninarum by isolating or destroying eggs from brood fish that exhibit clinical signs of BKD or test positive, with a high titer, against R. salmoninarum antigens. The method is used successfully in a number of US states and Canadian provinces such as Washington, Idaho, Michigan, Wisconsin, and Ontario. 3) Eradication Due to the complicated nature of BKD and its obvious threats to fisheries, Hoskins et al. (1976) recommended complete destruction of the infected stocks and disinfection of the holding facilities to achieve complete eradication of the disease. However, this procedure is considered by fisheries managers as impractical due to the widespread occurrence of R. salmoninarum (Sanders and Fryer 1980). Eradication can be of value in single fish farms or hatcheries that receive their water supply from specific pathogen free source (European Commission 1999). Eradication procedures should be followed by standard, cleaning and disinfection procedures. Although some trials have been made to eradicate 39 0f 8C BKD from fish farmed in open waters (e.g. sea and lake cages) or from farms and hatcheries with water supply from rivers, results were very discouraging. After eradication procedures have been applied in the fish farm and hatcheries, restocking should only utilize certified BKD-free stocks. Restocking should be followed by two inspections and laboratory examinations per year for a total period of two years before the facility can be designated as “BKD-free” (European Commission 1999). 4) Prophylaxis 1. Reducing the risk of BKD introduction Special attention should be paid to prevent the introduction of infected fish or their gametes (Evelyn et al. 1984; Yoshimizu 1996). This can only be achieved through prior examination and quarantine. Special requirements of water supply, wild birds and amphibians’ control. In addition, restriction of movement of vehicle, visitors as well as utensils from infected into free areas is equally important. Repopulation must be accompanied with certificate issued by the competent authority certifying that the fish or eggs are specific pathogen free. 2. Vaccination 4O Sd 9X the In the last two decades, vaccination against BKD has achieved different levels of success. Paterson et al. (1981) reported that an inactivated suspension of R. salmoninarum mixed 1:1 with Freunds adjuvant (FCA) administered by i.p. injection, reduced the level of infection of R. salmoninarum in yearling salmon but, did not completely eliminate the infection. Sakai et al. (1993; 1995) found that although vaccination evoked specific antibodies, these antibodies did not endow with a protection. Piganelli et al. (1999) demonstrated that oral administration of R. salmoninarum expressing low levels of cell associated p57, resulted in an extension of the mean time to death after challenge and they concluded that the protection was not due to humoral antibody. This conclusion supported earlier histopathological indications of an involvement of the cell mediated immune response in recovery, due to intracellular survival and the composition of inflammatory cells in connection with signs of regression (Munro and Bruno 1988). Rhodes et al. (2004) presented DNA adjuvants and whole bacterial cell vaccines against R. salmoninarum that were tested in chinook salmon fingerlings. These authors concluded that whole cell vaccines of either a nonpathogenic Arthrobacter spp. or an attenuated R. salmoninarum strain produced limited protection against acute intraperitoneal challenge with virulent R. salmoninarum. They also concluded that the addition of either synthetic oligodeoxynucleotides or purified R. salmoninarum genomic DNA as adjuvants did not increase protection, however a combination of both whole cell vaccines significantly increased survival 41 among fish naturally infected with R. salmoninarum. Also, the surviving fish treated with the combination vaccine exhibited reduced levels of bacterial antigens in the kidney. Gap of BKD knowledge in Michigan before 2002 Although BKD was virtually reported wherever salmonid fishes are present (Fryer and Sanders 1981; Bullock and Herman 1988, Klontz 1983), publications describing the status of BKD in Michigan salmonids fish species are rather scarce (Hnath and Faisal 2005). Historical records showed that BKD affected Michigan brook trout as early as 1955 (Allison 1958). Like in other parts of the USA and Europe, BKD continued its spread to the Coho salmon (Oncorhynchus kisutch) spawners in the late sixties (MacLean and Yoder 1970) and caused epizootics of chinook salmon (Oncorhynchus tshawytscha) in Lake Michigan in the late 1980’s (Holey et al. 1998; Johnson and Hnath 1991). Despite these reports of BKD in Michigan, only two studies have dealt with R. salmoninarum isolation from infected Michigan fish. Starliper (1996) and Starliper et al. (1997) isolated and identified R. salmoninarum isolates from chinook salmon collected from Lake Michigan weirs in Michigan and Wisconsin. Additional investigations showed that R. salmoninarum affects more salmonid fish species than originally thought. For example, Jonas et al. 2002 detected R. salmoninarum antigens in Lake whitefish (Coregonus clupeformis) and bloaters (C. hoyr) collected from Lake 42 Michigan in 1997-1999. Hnath and Faisal (2005); Wright and Faisal (2005) emphasized the fact that R. salmoninarum is endemic to the Great Lakes basin and effective control measures have to be seriously pursued. In order to develop sound management strategies to control BKD in Michigan, several gaps of knowledge have to be filled. This submitted study is a trial to fill some of these gaps. 43 Test Criteria Gmmsmm + PAS (Periodic Acid Schiff) + stain Zeihl-Nielsen ( Acid Fast) Non acid fast stain nine Bile solubil r utilization Casein Catalase rome oxidase DNase APl-ZYM' Escufin Esterase Gelatin l - APl-ZYM* Hemolytic activity Complete clearance zone around bacteria lndole test M Red Nitrate reduction Tween-20, 40 and 60 Tween-80 Urease Table 1. Summary of the morphological and biochemical characteristics of Renibacterium salmoninarum. ABl-ZYM" is a bacterial enzymes based assay used for the specific identification of different bacteria. 44 Criteria Description Motility Non motile Growth at 15 “C + Growth at 5, 22 °C + Growth at O, 30, 37 °C No growth Mol % G+C 53 Mycolic acid Absent Cell wall peptidoglycan amino acids Glutamic, lysine , alanine and glycine Cell wall sugars Glucose, arabinose, mannose, and Requirement for cysteine Required Survival Obligate intarcellular Major antigenic factor 57 kDa protein (P57) Antigenicicity Strains appears antigenically homologous Leucoagglutinins Exist Leucocytolysins Exist Metalloproteinase Exist Immune-complexes Occurs in kidney, liver, spleen Biochemical and genetic Biochemically uniform with very minimal diversity genetic differences Phylogeny Phylogentically related to actinomycetes and closely related to Arthrobacter spp and Brevibacterium Survival in river water Up to 1 week Survival in feaces and mud Up to 21 days Transmission Horizontal (wounds, orofecal, gills, contact) and vertical (intraovum or egg shell contamination) Table 2. Summary of different metabolic, antigenic and pathogenic characters of Renibacterium salmoninarum 45 in La‘ not 6 Sam; fishe R. sa wmd Gems Magi shor rel/8‘7 Spafi CHAPTER TWO Primary Isolation of Renibacterium salmoninarum from naturally infected salmonine stocks in Michigan using a modified tissue processing protocol ABSTRACT Throughout the 1980s, massive dieoffs involving chinook salmon occurred in Lake Michigan. These well-publicized epizootics were attributed primarily, but not entirely, to Bacterial Kidney Disease (BKD) caused by Renibacterium salmoninarum (R. salmoninarum). Despite the magnitude of the setback to fisheries conservation efforts in Michigan, relatively little research was done on R. salmoninarum, primarily due to the slow-growing nature of this bacterium which takes up to four weeks to obtain a primary isolation. In this study, I developed a tissue processing protocol that collected the whole kidney of an infected fish and exposed it to high sheer stomaching. This significantly shortened the incubation time and allowed R. salmoninarum to be cultured with relative ease. A total of 566 R. salmoninarum isolates have been retrieved from the kidneys of wild, feral, and captive fish assayed between 2002-2004 from spawning weirs and state fish hatcheries at various locations in Michigan. 46 exar with gee. simil Antll enro erylj These isolates constitute a unique resource for future studies of R. salmoninarum and BKD in the Great Lakes. Findings also demonstrated that R. salmoninarum is ubiquitous in Michigan because the pathogen was isolated from each population and lot of fish examined. Prevalence of R. salmoninarum and the clinical lesions associated with infection varied among species, strains of the same species, and geographic locations. Renibacterium salmoninarum isolates were biochemically homogenous and similar to those of other R. salmoninarum strains isolated worldwide. Antibiogram revealed high sensitivity of R. salmoninarum isolates to enrofioxacin and ciprofloxacin. Interestingly, two isolates were resistant to erythromycin, which is the antibiotic of choice for treatment of BKD. 47 modéf lime. INTRODUCTION Due to its slow-growing nature, Renibacterium salmoninarum Sanders and Fryer 1980, the causative agent of bacterial kidney disease (BKD), is difficult to isolate. Over the last six decades, scientists have utilized a number of bacterial media for this bacterium such as Minced Chick Embryo medium, Dorset Egg Medium, Cysteine Blood Agar (KDM1) (Ordal and Earp, 1956), KDM2, which contains 20 % fetal bovine serum (Evelyn, 1977), Charcoal Agar Medium (Daly and Stevenson, 1985) and Selective Kidney Disease Medium (SKDM) supplemented with the four antibiotics; cycloheximide, D-cycloserine, polymyxin B, and oxolinic acid (Austin et al., 1983). Incubation periods of up to 12 weeks have been necessary to isolate R. salmoninarum. To shorten the incubation time, Evelyn, et al. (1989) added a nurse R. salmoninarum culture to the center of the KDM2 culture plates. This modification both accelerated growth of the bacterium and shortened incubation time. The authors attributed the accelerated growth to the metabolites secreted by the initial nurse culture. Further, Evelyn et al. (1990) replaced the nurse culture with 25 ul of filter- sterilized broth that has previously been used to grow R. salmoninarum (referred to as spent broth) and continued to observe the accelerated growth. The authors attributed the accelerated growth to the presence of metabolites produced by the pathogen during its growth. Using the same approach, Teska (1993) and Starliper et al. (1998) incorporated R. salmoninarum spent medium into the KDM2 medium’s constituents (1% WV, 48 designated as KDM 2+M) and reported a shortened incubation time and profuse bacterial growth. Most of the previously mentioned studies have been performed on secondary bacterial cultures. However, primary isolation, particularly from carrier fish with negligible tissue bacterial concentration, continues to be a challenge for accurate epizootiological studies (European commission, 1999). In the State of Michigan, it has been documented that BKD has exist since the early 19508 (Allison, 1958). BKD has been incriminated to cause mass mortalities in the Great Lakes and in hatchery-propagated fish (Holey et al, 1998; Johnson and Hnath, 1991). Despite the potential association between R. salmoninarum and clinical cases of BKD in Michigan’s salmonines, a relatively limited number of R. salmoninarum isolates were retrieved from Michigan and Wisconsin feral spawner salmon in fall of 1991 (Teska, 1994; Starliper 1996). Among the retrieved isolates, those from the Michigan side of Lake Michigan were the most genetically diverse (Starliper, 1996) and of higher virulence (Starliper et al., 1997). Integral to the host-pathogen interaction of R. salmoninarum is the formation of granulomatous host reaction in which bacteria are sequestered (Bruno, 1986; Sami et al., 1992). The presence of such granulomas can impede bacterial isolation using standard bacterial loops and thereby lead to inconsistent isolation results. In this study we combined a modified tissue processing procedure with the use of KDM2+M medium supplemented with antibiotics to select and enhance the primary isolation of R. salmoninarum. The 49 modified protocol was then used to determine R. salmoninarum prevalence among representative propagated and feral salmonine populations in Michigan. 50 i grow befc Brief Cystj wale "uni aut0< lollov. slerl Wflv) AH) Lou LEn 9909 andc MATERIAL AND METHODS Bacterial growth medium. The medium used throughout this study combined the addition of 10% fetal calf serum recommended by Evelyn et al. (1990) into the KDM2 medium, the four antibiotics recommended by Austin et al. (1983) in the SKDM, and the 1% (v/v) R. salmoninarum spent medium used by Teska et al. (1993) and Starliper et al. (1998) in the KDM2+M. The bacterial growth medium used in this study, that combined the modifications listed before, will be referred to as MKDM (modified Kidney Disease Medium). Briefly, MKDM consists of peptone (1 % w/v), yeast extract (0.05 % w/v), L- cysteine HCl (0.1 % WM and Cycloheximide (0.005 % w/v) dissolved in distilled water. The medium’s pH is adjusted to 6.8. Agar (1.5 % w/v) is added immediately after adjusting the pH of the medium. The medium is sterilized by autoclaving at 121 °C for 15 minutes and left to cool down to 48 °C then the following ingredients are added: new born calf serum (10 % v/v), 0.22 pm filter- sterilized R. salmoninarum spent broth (1 % v/v), Oxolinic acid (0.00025 % w/v), Polymyxin B sulfate (0.0025 % w/v) and D-cycloserine (0.00125 % w/v). All MKDM ingredients were purchased from sigma (Sigma Chemical Co, St. Louis, MO, USA) with the exception of agar, which was from Remel (Remel, Lenexa, Kansas, USA). Fish and sample processing. Details regarding host, age, and geographic origins are found in tables 3-5. In the fall of 2002, a total of 515 feral and captive spawning salmonids were collected from Michigan weirs and state 51 Hm? bmc: (Salt and 1 fish h; OSFF mum; ”WE: eXDOS FOlloy lildivic COlleC WEre C( beOkt fish hatcheries. Fish included 150 returning chinook salmon (Oncorhynchus tshawytscha) collected from the Little Manistee River Weir (LMRW), Manistee county, Michigan (Lake Michigan watershed), Swan River Weir (SRW) at Rogers City, Presque Isle county, Michigan (Lake Huron watershed) and Platte River Weir (PRW) at Beulah, Michigan (Lake Michigan watershed). An additional 165 Michigan-adapted coho (Oncorhynchus kisutch) and 56 Hinchenbrook coho salmon were collected from the Platte River Weir. Captive brood stock included 60 brook trout (Salvelinus fontinalis), 60 lake trout (Salvelinus namaycush) that were kept in raceways that receive water from Cherry Creek (Lake Superior watershed) at the Marquette State Fish Hatchery in Michigan’s Upper Peninsula. Further, a total of 12 brown trout (Salmo trutta) and 12 rainbow trout (Oncorhynchus mykiss) were collected from Oden State fish hatchery (OSFH) at Oden, Alanson, Michigan (Lake Michigan watershed). OSF H is the brown and rainbow trout broodstock station and is a major rearing facility for those two species in Michigan. Males and females were equally represented among samples. The sacrifice of the feral spawners entailed exposing the fish to carbon dioxide-laden water, followed by a blow to the head. Following gamete collection, the abdominal cavity was cut open to examine individual internal organs for signs associated with BKD, followed by the collection of kidney tissue samples. In the spring of 2003, a total of 480 hatchery-reared pre-stocking fingerlings were collected from a number of state fish hatcheries. In brief, a total of 120 brook trout and 120 lake trout fingerlings were collected from MSFH. Additional 52 180 brown trout and 60 rainbow trout fingerlings were collected from OSFH. In August 2004, a total of 15 brook trout fingerlings were sampled from Cedarbrook Trout Farm at Harrisonville, Michigan. Cross contamination was avoided by replacing dissecting tools with sterile tools following the dissection of each fish. Attempts to isolate R. salmoninarum from kidney tissues were performed by each of the following procedures: 1. streaking a 10 pl loopful of kidney tissue onto MKDM plates, 2. harvesting as much kidney tissue as possible, mincing the tissue in a sterile, plastic Petri dish with scissors, suspending the minced tissue in Hank’s balanced salt solution (HBSS, 1:4 w/v, Sigma), and then streaking one hundred microliters (ul) inoculum of the suspension onto MKDM, or 3. transferring the homogenate to 7.5 cm x 18.5 cm Whirl-Pak® bags (Nasco, Fort Atkinson, WI), suspending in HBSS (1 :4 w/v), then crushing the suspension in a Biomaster Stomacher—80 (Wolf Laboratories Limited) at the high speed setting for 120 seconds. One hundred pl of the suspension were added to one end of an MKDM plate and then spread over the surface using a sterile bacteriological loop. Inoculated plates were incubated at 15 °C for up to 30 days and were checked periodically for growth using an inverted dissecting microscope, thus allowing the detection of early colonial growth. 53 Confirmation of isolates. All colonies were investigated for their conformance with colonial and bacterial morphological criteria of R. salmoninarum, as previously detailed in Sander and Fryer (1980) and Austin and Austin (1999). A number of biochemical tests were performed including motility, using motility test medium (DIFCO- BD and Company Sparks, MD, USA), cytochrome oxidase with Pathotec strips (Remel), catalase test with 3 % hydrogen peroxide, hydrolysis of esculin using bile esculin agar (Remel), and DNAse test using DNAse test medium (Remel). Carbohydrate utilization was performed using basal media (DIFCO-BD). The basal medium was prepared according to manufacturer instructions prior to the addition of individual sugars. Ten ml of filter sterilized (0.45 pm) 10 % sugar solution was added to autoclaved and cooled (48 °C) basal media to obtain a final concentration of 1 % with the exception of salicin which was made as 5 % solution to reach 0.5 % final concentration. Each one of the following sugars was added individually to the basal medium to test for the utilization of each sugar: arabinose, glucose, lactose, maltose, rhamnose, salicin, sucrose, sorbitol, xylose. All sugars were from Sigma. Results of biochemical tests were matched against standard R. salmoninarum biochemical characters described by Bruno and Munro (1986). Nested PCR. Single bacterial colonies were identified using highly specific oligonucleotide primers designed by Pascho et al. (1998), which amplify a region of the gene encoding the R. salmoninarum p57 antigen in a nested polymerase chain reaction (nPCR). The nPCR assay using these primers is 54 considered the method of choice to confirm R. salmoninarum isolates (OlE 2003, Pascho and Elliott, 2004). Briefly, DNA was extracted from each isolate using DNeasy Extraction Tissue Kit (Qiagen Inc., Valencia, CA) according to the manufacturer’s protocol with minor modifications. Bacterial pellets were obtained by centrifugation at 6000 g for 20 minutes at 4 °C and subsequently incubated with lysozyme buffer that consisted of 180 pl of 20 mg lysozyme (Sigma) , 20 mM Tris-HCI, pH 8.0; 2 mM EDTA (Sigma) and 1.2 % (v/v) Triton X100 (Sigma) at 37 °C for 1 hour. The nPCR method and the primers recommended by Pascho et al. (1998) were used with slight modification to the volume of utilized DNA (5 pl for first round and 2 pl for second round PCR reaction), water, and master mixes (45 pl for first round and 48 pl for second round nPCR reaction). The controls were composed of a PCR mixture containing no DNA template (reagent negative control), a positive R. salmoninarum, and a positive tissue control. A volume of 10 pl of the nPCR product and controls were mixed with 2 pl of 6X loading dye (Sigma) and used to load a gel consists of 2 % agarose (Invitrogen Life Technologies, Carlsbad, CA). Each electrophoresis gel included a 1 k bp (with 100 bp increments) DNA ladder (Invitrogen). Gels were run at 100 volt for 30 minutes in 1 X Tris Acetate Buffer (1 X TAE) (Sigma). Gels were visualized with the KODAK EDAS Camera System and UV Trans-illuminator. Suspect colonies were considered positive for R. salmoninarum when a 320 bp band was detected. 55 Antibiogram. Two media were used to test the isolates for sensitivity to antibiotics using a modified Kirby-Bauer disc diffusion method (Bauer et al., 1966) 1. Antibiotic free MKDM agar medium 2. Modified Muller’s Hinton agar medium (MMHA): Muller’s Hinton Medium (MHA) is used in standard antibiotic sensitivity testing. L-cysteine was added to MHA to support the growth of R. salmoninarum. The MMHA was prepared by adding 1 g L-cysteine HCI (Sigma) to 0.5 g yeast extract (Sigma), 100 ml fetal bovine serum (Sigma), and 38 g of dehydrated MH agar medium (Remel), and then suspending the mixture in double distilled water to obtain a 1000 ml media volume. The antibiogram was performed on 14 representative R. salmoninarum isolates. Five-day-old colonies were suspended in sterile saline to obtain turbidity equivalent to a 0.5 McFarland standards (Remel). From each bacterial suspension 200 pl was spread onto antibiotic free MKDM and MMHA plates (one plate each/isolate). Cultures were left for a few minutes to allow the bacteria to adsorb to the agar surface. Using an automatic dispenser (Remel), antibiotic discs (5 mm in diameter) were placed on the culture plate surface. The plates were then inverted and incubated at 15°C for 5 days in a subambient temperature incubator (Fisher Scientific Company L.L.C. Hanover Park, IL). Culture plates were observed and results recorded by measuring the diameter of the zone of inhibition in millimeters around each disc using a calibrated ruler. 56 ant trlr.’ Ka' oil: iso' La': fro." the' The following antibiotic discs (all from Remel) were used in the antibiogram: chloramphenicol (C), terramycin (TE), sulmethoxazole - trimethoprim (SXT), carbenicillin (CAR), erythromycin (E), azithromycin (AZM), Kanamycin (K), clindamycin (DA), polymyxin B sulfate (PB), novobiocin (NV), ofloxacin (OFX), ciprofloxacin (CIP), enrofloxacin (ENO) and norfloxacin (NOR). Preservation and storage of isolates. Identified R. salmoninarum isolates were cryoperserved and deposited at the Aquatic Animal Health Laboratory, Michigan State University. Bacterial suspensions were prepared from 5 day-old cultures in MKDM broth (not supplemented with antibiotics) and then stored at —80 °C. 57 RESULTS Effects of sample processing and culture technique on primary isolation of Renibacterium salmoninarum. When MKDM was streaked with a loopful (10 pl) of infected kidney tissue, colonies were evident 15-20 days post incubation. Using minced kidney of the same tissue and increasing the inoculum to 100 pl shortened the incubation time to 10-15 days. However, when kidney tissue samples were stomached for 120 seconds, profuse growth was achieved within a relatively short period (5-10 days). Renibacterium salmoninarum colonies grew on and around streaked tissues and were creamy, glistening, smooth, convex and 1-2 mm in diameter. Representative colonies were individually picked and their identities confirmed using nested PCR assay. Because of the astounding success in shortening the incubation period and the absence of contaminants, stomaching of minced tissues and inoculating MKDM plates with 100 pl of tissue homogenate became the routine tissue processing procedure for the primary isolation of R. salmoninarum from tissues in this and subsequent studies. Prevalence of R. salmoninarum isolated from Michigan salmonines 1. Feral salmon population. Tables (3-5) show the numbers of fish examined, prevalence, and numbers of fish exhibiting BKD clinical signs. Most of the examined fish looked healthy and exhibited healthy-looking kidneys and internal organs. A number of fish in each of the species and lots examined 58 (IS an tha‘ exa BKI 2. P saln brov Dem sloc 3. P. sal/x high addi: sa/m Simul displayed whitish abscesses like nodules that sometimes coalesce to form patches in the kidneys’ parenchyma. The prevalence of the pathogen was highest in chinook salmon from the Platte River Weir chinook (96.3%), followed by Little Manistee weir chinook (82.5%), and Swan River weir chinook (48.3%)(table 3). As shown in figure 1 and 2, prevalence seems not to differ among males and females. Coho salmon spawners showed prevalence rates that reached up to 100% in the Hinchenbrook strain, with more than half of the examined fish showing clinical BKD signs (table 3). As depicted in Figure (2), BKD lesions were more apparent in females coho salmon than males. 2. Prevalence in captive broodstocks. Results indicated that R. salmoninarum is also widespread among captive broodstocks (table 4), with brown trout (the Wild Rose strain) being the highest in both prevalence and percent of clinical cases, followed by rainbow trout, brook trout, and Lake trout stocks. 3. Prevalence in propagated offspring fish. The prevalence of R. salmoninarum in propagated Iron River Brook trout fingerlings were remarkably high (83 %), with 50 % of the fish presenting with lesions typical of BKD. In addition, propagated Assinica BKT fingerlings also showed relatively high R. salmoninarum prevalence (42 %), with 16.66% showing clinical signs. Similarly, the R. salmoninarum prevalence and percentage of fish (60 %) with clinical signs were very high in BKT obtained from a fish farm (table 5). 59 fOL wt' dlpl dEit Rs II. E F ingerlings of lake trout, three strains of brown trout, and rainbow trout showed relatively lower prevalences (<25%) and lesser numbers of fish with clinical signs (table 5). Confirmation of the retrieved R. salmoninarum isolates. A total of 566 R. salmoninarum isolates were retrieved from infected fish tissues over a two- year period. All colonies were creamy-whitish, glistening, 1-2 mm in diameter, rounded, and smooth. Old colonies (over 40 days incubation) showed granular white or crystalline appearance. Gram staining demonstrated Gram-positive diplo- or coccobacilli. No capsules, metachromatic granules, or bipolarity were detected in the stained slides of all isolates. I. Molecular Confirmation. Nested PCR performed on all isolates exhibited the R. salmoninarum characteristic 320 bp band. ll. Biochemical Reactions. Results of the conventional biochemical testing of 12 representative isolates demonstrated isolate uniformity. Isolates were non- motile, catalase positive, cytochrome oxidase negative, esculin hydrolysis negative, DNAse negative and carbohydrate utilization negative (table 6). III. Antibiogram of the R. salmoninarum Isolates. Tables 7 and 8 show the details of the R. salmoninarum antibiogram results. Results indicate that, after 5-10 days incubation, the inhibition zones obtained from isolates cultured on antibiotic-free MKDM medium were sharper and more obvious than those 60 obtained by culture on MMHA medium. However, both media yielded relatively similar results. All 12 isolates were highly sensitive to enrofloxacin and ciprofloxacin with a 27mm and 23 mm average inhibition zone diameters respectively). Ten isolates were markedly sensitive to terramycin (21 mm average inhibition zone). Interestingly, two of the isolates retrieved from captive brown trout broodstock were resistant to erythromycin and azithromycin, while the remaining 10 isolates were sensitive or intermediately sensitive to erythromycin, azithromycin and sulfamethoxazole —trimethoprim, with average inhibition zones of 17mm, 15.5mm and 18mm, respectively. Moreover, all isolates were resistant to polymyxin B and clindamycin (average inhibition zone diameter of 0, 4mm respectively). In addition, most of the isolates were resistant to kanamycin; with an average inhibition zone diameter of 9mm. Isolates were sensitive to chloramphenicol, novobiocin, and carbenicillin showing average inhibition zones diameters of 20 mm, 14mm and 16mm respectively. 61 DISCUSSION Results from this study demonstrated that the combined use of MKDM medium and stomaching minced tissues diluted in HBSS was optimal for primary isolation of R. salmoninarum. The antibiotics Austin et al. (1983) incorporated into the medium combined with a shorter incubation period minimized the growth of contaminating bacteria and fungi. There are a number of factors that may have led to the improved growth of R. salmoninamm that was observed. First, thorough mincing and homogenization may have caused release of R. salmoninarum from granulomas and fibrous layers. Second, the relatively aggressive tissue processing may have led to a massive release of bacterial metabolites that are known to boost bacterial growth in vitro (Evelyn et al.1989; 1990). Third, a major part of the kidneys (posterior and anterior) were used in homogenization, a matter that increases the likelihood of isolating bacteria even if present in low numbers, as in the case of carrier fish. Pascho et al. (1987) were able to double the likelihood of isolating R. salmoninarum from infected fish by combining samples taken from three different spots in the kidneys of individually tested fish. Fourth, a heavy tissue inoculum (100 pl) was used, a matter which enhances the likelihood of bacterial isolation when compared to using a loopful (~ 10 pl only). Fifth, mixing kidney tissues with four times their weight of HBSS may have diluted inhibitory molecules present in tissue that Evelyn et al. (1981); Daly and Stevenson 1988 and Olsen et al. (1992) believed to lower the likelihood of isolating R. salmoninarum from homogenized kidney tissues. Last, the unique formula of HBSS with its rich 62 inorganic ions and electrolyte content might have played a role in adjusting the pH and osmotic balance. Our improved R. salmoninarum growth may be a result of an additive effect from some or all of the aforementioned points. Findings of the current study clearly demonstrate the advantages of this modified tissue processing in the improvement of primary isolation of R. salmoninarum from infected tissues, even if infection intensity is relatively low. Conventional biochemical tests revealed that R. salmoninarum isolates tested in this study were non-motile, catalase positive, cytochrome oxidase negative, esculin hydrolysis negative, DNAse negative and carbohydrate utilization negative. These findings coincide with the standard biochemical criteria of R. salmoninarum described by Smith (1964); Sanders and Fryer (1980); Bruno and Munro (1986) and indicate the biochemical uniformity of Michigan isolates among themselves and among other R. salmoninarum strains isolated worldwide. Our identifications were further confirmed with nPCR results as all R. salmoninarum isolates had the 320 bp band characteristic for R. salmoninarum (Pascho et al., 1998). The antibiogram performed on 12 R. salmoninarum representative isolates indicated that all tested isolates were highly sensitive to enrofloxacin, which is in agreement with the report of Hsu et al. (1994). In the study of Hsu et al. (1994), the authors performed an in vitro sensitivity test using the standard MIC (minimal inhibition concentration) method and an in vivo efficacy trial using enrofloxacin medicated food to treat juvenile rainbow trout experimentally infected with R. salmoninarum. The authors concluded that R. salmoninarum is 63 highly sensitive to enrofloxacin and suggested that the low Mle, high bioavailability, and large volume distribution of enrofloxacin make it a good candidate for treatment of BKD. Results of the present study showed that all isolates were highly sensitive to ciprofloxacin and intermediate sensitive to ofloxacin and norfloxacin. Moreover, the sensitivity of the isolates to terramycin, chloramphenicol, novobiocin, sulfamethaxozole - trimethoprim, carbenicillin and the resistance to polymyxin B coincide with previous reports (Austin, 1985; Wolf and Dunbar, 1959; Goodfellow et al., 1985). An unexpected result was the presence of two erythromycin and azithromycin resistant isolates (Oden BNT-BS-02 and Oden BNT-BS1-02), since the “wild — type” R. salmoninarum strains are known to be sensitive to macrolide antibiotics (Austin, 1985). However, this finding corroborates with Bell et al. (1988), who were able to develop erythromycin-resistant R. salmoninarum strains in vitro but were unable to describe the mechanism behind this resistance. The brown trout stock from which these two isolates were retrieved has never been treated with erythromycin. Resistance to erythromycin and other macrolide antibiotics is believed to be associated with mutational (Tanaka et al., 1968) or plasmid —mediated blockage (e.g. methylation) (Weisblum et al., 1971) of the binding sites on the 23 S RNA. Whether erythromycin-resistance observed in the brown trout strain has developed as a result of any of the mechanisms described for other Gram-positive bacteria is currently unknown and deserves further investigation. 64 From the relatively limited survey performed in this study, a number of interesting results were demonstrated that would vastly improve our current understandings of the status of BKD in Michigan, as well as help shape the design of future epidemiological studies. First, it is quite clear that R. salmoninarum is widespread in Michigan, as it has been isolated from every fish population and lot that was tested (tables 3-5). Second, infected fish are not only carriers, but some also developed clinical kidney lesions consistent with BKD. Third, vertical transmission seems to play a major role in BKD transmission in brown and rainbow trout, as fingerlings were kept throughout their life in raceways supplied with well water. Fourth, results also suggested that R. salmoninarum prevalence varies among the species examined, with brook trout and coho salmon being the highest in both prevalence and presence of kidney lesions. Fifth, even within the same species, fish strain seems to play a role in susceptibility to R. salmoninarum. For example, the Hinchenbrook coho salmon strain showed higher prevalence than that of the Michigan adapted coho salmon strain collected from Platte River. Also, the Hinchenbrook coho salmon strain showed relatively higher percent of kidney lesions when compared to Michigan-adapted coho salmon strain. This increased susceptibility could be due to the fact that the Hinchenbrook coho salmon strain was recently introduced to Michigan (in the 19903), while the other coho salmon strain has adapted to the Great Lakes basin since it’s introduction in the 1960s (Michigan Department of Natural Resources (MDNR). This also applies for the brook trout Iron River strain, which has recently been 65 inf cc hi. {ES adopted for propagation purposes, as opposed to the Assinica strain, which has been domesticated for five decades. On the contrary, there have been no noticeable differences in R. salmoninamm prevalence among three strains of brown trout. Variation in resistance to BKD among strains within the same species has also been reported by Winter et al. (1980) who made a similar observation with steelhead trout (Oncorhynchus mykiss). Last, in the case of chinook salmon, results suggest that R. salmoninarum prevalence varied among sites to which spawning runs return. For example, adult Platte River chinook salmon coming from Lake Michigan showed higher R. salmoninarum prevalence (96 %) and higher percent of clinical cases (11 %) when compared to Swan River chinook salmon (48 %, 5 % respectively) coming from Lake Huron. The same trend was observed in chinook salmon from the Little Manistee Weir, which exhibited a higher R. salmoninarum prevalence than those found at the Swan River weir. Spatial distribution and population density could play a role in elevating the prevalence of BKD among fish populations (Reno, 1998). In conclusion, this study has shed light on the widespread R. salmoninarum infections occurring in Michigan’s salmonids. The tissue processing protocol, combined with the modified medium, has facilitated the isolation of several hundred R. salmoninarum isolates. These isolates constitute an important resource for scientists studying R. salmoninarum and BKD in the United States in general and the Great Lakes in particular. 66 Host Weir # of Prevalence (positive/total) {lessrted Apparently Fish with Total healthy fish gross kidney Lesions * Chinook Little 63 47/ 63 5/63 52/63 salmon Manistee (74.60 %) (7.93 %) (82.53 %) River Swan 60 26/60 3/60 29/60 River (43.33 %) (5 %) (48.33 %) Platte 27 23/27 3/27 26/27 River (85.18 %) (11.11 %) (96.29 %) Michigan - Platte 165 112/165 30/165 142/165 adapted coho River (67.87 %) (18.18 %) (86 %) salmon Hinchenbrook 56 26/56 30/56 56/56 coho salmon (46.42 %) (53.57 %) (100 %) Total 371 234/371 71/371 305/371 (63 %) (19.1%) (82.2 %) Table 3. Prevalence of Renibacterium salmoninarum in fall returning chinook and coho salmon spawners from Lake Michigan and Lake Huron watersheds. * White-creamy patches in kidneys 67 Tal Iro hal Host Number of Prevalence 2::mined Apparently Fish with Total healthL kidney lesions Brook trout 60 22 10 32 (36.66 %) (16.66 %) (53.33 %) Lake Trout 60 40 3 43 (66.66 %) (5 %) (71.66 %) Brown Trout 12 8 4 12 (66.66 %) (33.33 %) (100 %) Rainbow trout 12 9 (75 %) 2 11 (16.66 %) (91.66 %) Total 144 79/144 19/144 98/144 (54.9%) (13.2%) (68%) Table 4. Prevalence of Renibacterium salmoninarum in captive char and trout broodstocks collected in the fall 2002 from Michigan state fish hatcheries. 68 Fish Species Number of Prevalence fish tested Apparently Fish with Total healthy kidney lesion * Brook trout 60 15 10 25 Assinica (25 %) (16.7 %) (41.7 %) Brook trout Iron 60 20 30 50 River (33.3 %) (50 %) (83.3 %) Brook trout 15 0 9 9 Cedarbrook (0 %) (60 %) (60 %) Lake Trout 120 22 0 22 (18.3 %) (0 %) (18.3 %) Brown trout 60 8 2 10 (Wild Rose) (13.3 %) (3.3 %) (16.7 %) Brown trout 60 14 1 15 Seeforellen (23.3 %) (1.7 %) (25 %) Brown trout 60 12 3 15 Gilchrist (20 %) (5 %) (25 %) Rainbow trout 60 8 2 10 (13.3 %) (3.3 %) (16.7 %) Total 495 99/495 57/495 1 56/495 (20%) (11.5 %) (31.5 %) Table 5. Prevalence of Renibacterium salmoninarum in 10-15 month-old propagated fish. All samples were collected in January 2003 except those from Cedarbrook, which were collected in August 2004. 69 Ta Ofl esl Isolate ID Conventional biochemical tests Motility C O E D CHO Marquette BKT-BS-02 + - - - - - Marquette LT-02-A Wild Cherry Creek BKT44- 02 Oden BNT-BS-02 Marquette LT-02-B Oden RBT-02 Marquette LT 24-02 Platte River CH-02 Oden BNT-BS1-02 Platte River HB-02 Swan River OHS-02 Platte River CO-02 + I I I I I + I I I I u +++++++++ I I I I I Table 6. Results of conventional biochemical and motility tests performed on the 12 representative Renibacterium salmoninarum isolates. Conventional biochemical tests used in this study are catalase (C), oxidase (O), esculin hydrolysis (E), DNAse (D), and carbohydrate utilization tests (CHO). 7O Antibiotic Inhibition zone diameter standards in mm Name Code Disk Resistant Intermediate Sensitive potency Terramycin TE 30 pg No zone <15 2 5 Chloramphenicol C 30 pg No zone 13-17 21 8 Trimethoprim - SXT 25 pg No zone <15 25 5 Sulfamethoxazole Erythromycin E 15 pg No zone <15 215 Azithromycin AZM 15 pg No zone <15 2 5 Clindamycin DA 241g No zone <15 35 Ciprofloxacin CIP 5 pg No zone <15 35 Enrofloxacin EN0 5 pg No zone <15 21 5 Ofloxacin OFX 5 fl No zone 13-15 36 Norfloxacin NOR 10 pg No zone 14-16 217 Kanamycin K 30 pg No zone 14—17 218 Carbenicillin CAR 100 pg No zone <15 27 Novobiocin NV 30 pg No zone <10 20 Polymyxin B PB 300 U No zone 9-11 22 Sulfate Table 7. Standard concentration and expected inhibition zones for each used antibiotic disc. 71 Isolate ID 1 2 3 4 5 6 7 8 9 10 11 12 Mean SE SD Antibiotic TE 25 20 20 8 25 27 25 24 8 26 25 22 21 .25 1 .89 6.50 SXT 20 18 19 18 20 22 18 14 12 18 19 18 18.00 0.76 2.70 C 25 22 12 20 24 18 17 20 20 27 18 16 20.00 1.20 4.16 CAR 17 18 7 18 15 14 12 14 10 18 18 8 14.00 1.16 4.03 E 19 22 13 7 10 20 20 23 9 20 17 20 16.70 1.57 5.46 AZM 17 20 12 8 12 17 18 22 8 17 19 16 15.50 1.30 4.52 K 10 8 12 10 9 14 10 10 6 8 10 6 9.40 0.65 2.27 DA 6 0 0 0 8 10 0 6 0 6 8 0 3.66 1.15 3.98 PB 0 0 0 0 0 0 0 0 0 0 0 0 0.00 0.00 0.00 NV 15 20 10 14 17 14 13 15 17 18 18 16 15.60 0.77 2.67 OFX 20 18 20 19 20 20 19 18 16 20 19 18 19.00 0.35 1.24 CIP 27 23 22 25 22 28 20 19 17 22 22 25 22.70 0.92 3.20 ENO 30 32 28 27 31 32 25 18 19 28 30 29 27.40 1.33 4.64 NOR 19 20 18 16 18 20 17 15 16 18 19 20 18.00 0.49 1.70 Table 8. Inhibition zones in millimeters (mm) produced by the 12 Renibacterium salmoninarum isolates used in the antibiogram. Note: 1 (Marquette BKT-BS-02), 2 (Marquette LT-02-A), 3 (Cherry Creek BKT44-02), 4 (Oden BNT-BS-02), 5 (Marquette LT-02-B), 6 (Oden RBT-02), 7 (Marquette LT 24-02), 8 (Platte River CH—02), 9 (Oden BNT-BS1-02), 1o (Platte River HB-02), 11 (Swan River CH5-02), 12(Platte River 00-02) 72 El % Non clinical I% Clinical LMCH LMCH SRCH SRCH female male female male Figure 1. Prevalence of Renibacterium salmoninarum in male and female returning chinook salmon spawners from Lake Michigan and Lake Huron watersheds. Prevalence was determined by calculating % positive Renibacterium salmoninarum culture retrieved from fish with clinical or without clinical lesions. * LMCH: Little Manistee River Weir chinook salmon * SRCH: Swan River Weir chinook salmon. 73 100%- 90%- 80%- 70%- 60%7 50°/o‘ 40°/o‘ 30%' 20°/o‘ 10%‘ 0% 0% non Clinical I% Clinical J; Ml Coho Coho HB Coho HB Coho female male female male Figure 2. Prevalence of Renibacterium salmoninarum in male and female returning coho salmon spawners from Platte River Weir, Lake Michigan watershed. Prevalence was determined by calculating % positive Renibacterium salmoninarum culture retrieved from fish with clinical or without clinical lesions. * Ml Coho: Platte River Weir Michigan adapted coho salmon " HB Coho: Platte River Weir Hinchenbrook coho salmon. 74 CHAPTER THREE DIAGNSOTIC TESTING PATTERNS OF RENIBACTERIUM SALMONINARUM INFECTION IN SOME FERAL AND CAPTIVE SALMONINES ABSTRACT Bacterial kidney disease, caused by Renibacterium salmoninarum (R. salmoninarum), is a slowly progressing disease that hampers salmon conservation and restoration programs in North America. The purpose of this study was to track the progress of naturally occurring R. salmoninarum infection in some of Michigan’s salmonid stocks using nested polymerase chain reaction (nPCR), quantitative enzyme linked immunosorbent assay (Q- ELISA), and culture. The Q-ELISA test detected 67.6 % infection prevalence, which is lower than culture (77.2 %) or nPCR (94.2 %), yet it provided semi-quantitative data on infection intensity. The disagreement in results among the three assays may reflect the different phases of R. salmoninarum infection at the time of sampling. The testing results demonstrated the presence of six patterns, with each of the patterns representing a probable stage along the course of R. salmoninarum infection. 75 Findings also suggested that fish stocks tested in this study are not uniform in the distribution of the diagnostic patterns. 76 INTRODUCTION Bacterial Kidney Disease (BKD) of salmonines, caused by Renibacterium salmoninarum, is a slowly progressing systemic infection, which often causes high losses among infected fish (Fryer and Sanders 1981). In addition to horizontal transmission, R. salmoninarum can be transmitted vertically (Evelyn et al. 1986 a,b). Therefore, BKD is a major concern for salmonine conservation and restoration programs worldwide in general, and in the Great Lakes basin, in particular (Faisal and Hnath 2005). Since the first report of Kidney Disease in 1930, a number of diagnostic assays have been developed to determine the presence of R. salmoninarum in infected fish tissues. Culture on selective media, fluorescent antibody technique, quantitative ELISA (Q-ELISA), and nested polymerase chain reaction (nPCR) are currently the most common diagnostic techniques used in the detection of R. salmoninarum (Pascho and Elliott 2004; OIE 2003). When multiple diagnostic tests were performed on the same sample, numerous discrepancies among findings were observed (Cipriano et al. 1985; Sakai et al. 1989; White et al. 1995; Jansson et al. 1996; Miriam et al. 1997; Pascho et al. 1998). While these inconsistencies were often difficult to interpret, most authors concentrated on these discrepancies to merely evaluate the sensitivities of various detection assays (Jansson et al. 1996; Chase and Pascho 1998; Pascho et al. 1998). For example, it has been estimated that the nested PCR assay, developed by Chase and Pascho 77 (1998), which uses primers specific for conserved regions of the major soluble antigen (msa) gene, has enabled the detection of as little as 10 bacterial cells/gram of kidney tissue (Pascho et al. 1998). Culture, on the other hand, requires the presence of 40-100 bacterial cells per gram tissue to ensure bacterial isolation (Lee 1989; Miriam et al. 1997). The quantitative ELISA assay primarily targets bacteria-secreted soluble proteins (Pascho and Mulcahy 1987; Meyers et al. 1993; Pascho et al. 1998). It has been estimated that Q-ELISA requires a minimal bacterial concentration of 1.3x 104 bacterial cells/ml of ovarian fluid and 103-cells/g kidney tissues are needed to produce consistent positive results (Pascho et al. 1998). Mechanisms involved in the initiation of infection, progression of the disease, death, and/or recovery from natural R. salmoninarum infections are currently unknown (reviewed in Evenden et al. 1993; Wiens and Kaattari 1999). It is well documented that R. salmoninarum can be transmitted vertically from parents to offspring (Evelyn et al. 1984; 1986). Horizontal transmission is believed to occur primarily through the oral-fecal route (Balfry et al. 1996), and to some extent through the gills (Flano et al. 1996) and skin lesions (Evenden et al. 1993). Renibacterium salmoninarum infections can persist in fish lacking clinical signs, while in others, the infection may progress, causing clinical signs with bacterial numbers reaching up to 109 colony forming units/ g of kidney tissues prior to death (Bruno 1986; Evelyn et al. 1996). 78 Renibacterium salmoninarum secretes a number of soluble proteins that seem to play a role in pathogenicity (Austin and Rodgers 1980; Bruno and Munro 1986; Wiens and Kaattari 1991; Hamel 2001). These bacterial proteins form complexes with fish antibodies that are deposited in kidney glomeruli and are then slowly eliminated (Sami et al. 1992). Therefore, the aim of this study is to utilize the limits of detection for each assay, what each assay detects, and the collective results of these assays to shed some light on the kinetics and course of infection within certain fish population. 79 MATERIALS AND METHODS Fish. Between October-November 2002, a total of 364 feral and captive spawning salmonids were collected from Michigan weirs and state fish hatcheries. Fish included 100 returning chinook salmon (Oncorhynchus tshawytscha) collected from the Little Manistee River Weir (LMRW), Manistee county, Michigan (Lake Michigan watershed) and Swan River Weir (SRW) at Rogers City, Presque Isle county, Michigan (Lake Huron watershed). An additional 131 Michigan-adapted coho (Oncorhynchus kisutch) and 53 Hinchenbrook coho salmon were collected from the Platte River Weir (PRW) at Beulah, Michigan (Lake Michigan watershed). Captive brood stock included 41 brook trout (Salvelinus fontinalis) and 39 lake trout (Salvelinus namaycush). The captive stocks were kept in raceways that receive water from Cherry Creek (Lake Superior watershed) at the Marquette State Fish Hatchery in Michigan’s Upper Peninsula. Males and females were equally represented among samples. The sacrifice of the feral spawners entailed exposing the fish to carbon dioxide-laden water, followed by a blow to the head. Following gamete collection, the abdominal cavity was cut open to examine individual internal organs for signs associated with BKD, followed by the collection of approximately one gram of tissue from anterior, posterior and middle kidney sections. Cross contamination was avoided by replacing dissecting tools with sterile tools following the dissection of each fish. 80 Sampling and sample processing: Samples from fish were analyzed individually unless othenlvise indicated. Kidney samples representing the anterior, posterior, and middle sections of the kidney were transferred in sterile 7.5 cm x 18.5 cm Whirl Pak® bags (Nasco, Forte Atkinson, and WI), kept on ice, and were softened as much as possible through multiple cycles of physical pressure. The homogenized kidney tissues were diluted in 1:4 (w/v) Hank’s Balanced Salt Solution (HBSS, Sigma Chemical Co, St. Louis, MO, USA) and then stomached for 2 minutes at high-speed using the Biomaster Stomacher-80 (Wolf Laboratories Limited, Pocklington, York, UK). In the case of coelomic fluid, 1 ml of each sample was diluted 1:2 (v/v) in HBSS for Q-ELISA testing. In the case of the milt, 1ml from each sample was diluted 1:2 (v/v) in HBSS for Q-ELISA testing. Culture. Isolation of R. salmoninarum was performed as described in Chapter 2 in this thesis. Briefly, 100 pl aliquots of stomached kidney tissues were spread onto MKDM (Eissa 2005, chapter 2). Culture plates were incubated for a period of 20 days at 15 °C. Inoculated plates were checked every 5 days for bacterial growth. Identification of the isolates was done according to the standard morphological criteria of R. salmoninarum (Sanders and Fryer 1980; Austin and Austin 1999). Molecular confirmation of the isolates was done using the nPCR method described by Pascho et al. (1998). 81 Measurements of Renibacterium salmoninarum antigen using the Quantitative Enzyme-linked Immunosorbent Assay (Q-ELISA). Aliquots (250 pl) of each sample were transferred into 1.5 ml safe lock microfuge tubes, to which an equal volume of 0.01 M Phospate Buffered Saline Tween 20 (0.05 %) (PBS-T20) (Sigma) with 5 % natural goat serum (Sigma) (Olea et al. 1993) and 50 pl CitriSoIv solution (Fisher Chemicals, Fairlawn, New Jersey, USA) (Gudmunsdottir et al. 1993) were added. The solution was then thoroughly mixed via vortexing, incubated at 100 °C on heat blocks with a rotary shaker for 15 minutes, followed by 2 hours of incubation at 4 °C. After incubation, the mixture was centrifuged at 60009 for 15 minutes at 4 °C. The aqueous supernatant of each sample was carefully collected and then transferred to a 1.5 ml microfuge tube for Q-ELISA testing. The Q-ELISA method used in this study is that described in detail by Pascho and Mulcahy (1987) as well as Alcorn and Pascho (2000). The positive-negative threshold absorbances were calculated according to the method described by Meyers et al. (1993) .The positive—negative cutoff absorbance for the kidney homogenate was 0.10. The tested positive samples were assigned the following antigen level categories: low (0.10 to 0.19), medium (0.20-0.99) and high (1.000 or more) (Pascho et al. 1998). Nested PCR. Bacterial DNA was extracted using the DNeasy tissue extraction kit (Qiagen-Valencia, CA, USA). DNA was extracted from 100 pl aliquots of kidney tissue homogenates according to manufacturer’s 82 instructions and the method described by Pascho et al. (1998) with minor modifications. The tissue pellets were obtained by centrifugation at 6000 g for 20 minutes at 4 °C and then incubated with lysozyme buffer consisting of 180 pl of 20 mg lysozyme (Sigma-Aldrich, Inc. St. Louis, MO), 20mM Tris- HCI (pH 8.0), 2 mM EDTA (Sigma) and 1.2 % (v/v) Triton X 100 (Sigma) at 37 °C for 1 hour. The nPCR method used primers recommended by Pascho et al. (1998) with slight modifications to the volume of DNA (5pl for the first round and 2p| for the second round nPCR) and master mixes (45pl for the first round and 48pl for the second round nPCR). The controls were composed of a PCR mixture containing no DNA template (reagent negative control), positive R. salmoninarum and positive tissue control. A volume of 10 pl of the nPCR product and controls were mixed with 2 pl of 6X loading dye (Sigma) and used on a 2 % agarose gel (Invitrogen Life Technologies, Carlsbad, CA). Each electrophoresis gel included a 1kbp DNA ladder with 100 bp increments (Invitrogen). Gels were run in 1 X Tris Acetate (1 X TAE) Buffer (Sigma). Gels were visualized under the KODAK EDAS Camera System and UV Trans-illuminator. Samples were considered positive when a 320 bp band was detected. 83 RESULTS Among the 364 fish examined, 343 fish (94.2%) were positive in the nPCR assay, 281 (77.2%) were culture positive and 246 (67.6%) were positive with the Q-ELISA. Over half (53.3%) of the fish used in this study gave positive results by all three diagnostic assays (table 9). The consistency among findings was highest in the case of Hinchenbrook coho (81.1%), followed by brook trout (63.4%). Only 7 fish (1.9%) were negative by all three diagnostic assays. As displayed in table (9), most Q-ELISA positive fish possessed low R. salmoninarum antigen concentrations (193/231, 83.5%), the highest proportions of which were in the LMRW Manistee chinook salmon and PRW Michigan-adapted coho salmon (64.3 %, 67.9 % respectively). Fish with medium and high R. salmoninarum antigen concentrations were found primarily in Hinchenbrook coho salmon (45.2%) and brook trout (29.2%) stocks. Combining the results of the three diagnostic assays performed on the same samples, 6 patterns were recognized. Pattern 1 represents fish that were positive with the nPCR only (24/364, 6.7%). Pattern 2 represents fish positive with both nPCR and culture assays (87/364, 23.9%). The majority of fish (194/364, 53.3%) were in Pattern 3, with positive results in all three diagnostic techniques. Pattern 4 represents fish positive with nPCR and Q- ELISA (38/364, 10.4%). Pattern 5 represents fish that were barely positive in the Q-ELISA assay (14/364, 3.8%). Pattern 6 was the least represented, 84 with only 7 fish (1.9%) that had negative results with all three assays used in this study. The distribution of fish representing each of the patterns differed among the fish stocks tested. For example, the majority of LMRW chinook salmon were in patterns 2 and 3 (Figure 3A), while SRW chinook salmon showed a wider distribution consisting of over half of the fish in patterns 1 and 2 (Figure 3B). In the case of PRW Michigan-adapted coho, almost all fish were in patterns 2-4 (Figure 4A). On the other hand, 75% of the Hinchenbrook coho salmon strain belonged to pattern 3 (Figure 48). Similarly, the two captive Salvelinus spp. broodstocks, though kept in the same hatchery, exhibited different diagnostic testing patterns (Figures 5 - 6), with over 60% of the brook trout belonging to Pattern 3. 85 DISCUSSION Findings clearIy suggested that R. salmoninarum infection is widespread in adult fish of the stocks tested in this study. Only 7 fish were negative out of 364 when tested by the three diagnostic assays. While these figures are staggering, one should not be surprised since R. salmoninarum has existed in Michigan salmonines for at least 50 years (Allison 1958) and was involved in the massive chinook salmon die offs of the 19808 in Lake Michigan (Johnson and Hnath 1991; Holey et al. 1998). However, it should also be emphasized that fish tested in this study were spawning adults (>4 years old); a matter that increases the likelihood of exposure to R. salmoninarum and allows time for the slow progression of this infection. Moreover, sampling took place at the peak of the spawning season, meaning that the fish were subjected to multiple stressors, such as starvation, hormonal changes, and physical pressure on internal organs due to distension of the gonads. Therefore, infection rates obtained in this study should not be considered representative of the overall R. salmoninarum prevalence at the population level. Regardless of these factors, data strongly suggested that R. salmoninarum continues to be enzootic in Michigan’s salmon and char species. In other areas of the world where R. salmoninarum is enzootic, prevalence of infection in feral and wild fish species have reached up to 100%. For example, in Iceland, arctic char and brown trout reached infection 86 levels of 100% and 81%, respectively (J6nsd6ttir et al. 1998). In North America, R. salmoninarum infection rates of 83% in brook trout from Wyoming, USA (Mitchum et al. 1979), and 35% in returning Atlantic salmon in the Margaree River, Halifax, Canada (Paterson et al. 1979) were reported. The findings also suggested that nPCR performed with primers targeting the msa gene is superior to culture and Q-ELISA methods in detecting R. salmoninarum infection. Most other studies comparing diagnostic assays concur with the supreme specificity and sensitivity of the nPCR technique developed by Chase and Pascho (1998). However, despite its high specificity and sensitivity, one cannot determine infection intensity based exclusively on nPCR results. The isolation of R. salmoninarum from infected tissues, in conjunction with the confirmation of representative colonies via nPCR has also been effective in identifying 76.4% of the infected fish in this study, although culturing is lower in sensitivity than nPCR alone. Retrieving R. salmoninarum from tissues by culture alone indicated a presence of at least 40-100 live bacterial cells/g, but did provide an estimate for the intensity of infection (Lee 1989; Miriam et al. 1997). Q-ELISA yielded 67.6% R. salmoninarum prevalence, which was lower than either nPCR (94.2%) or the culture assays (77.2%). Previous studies estimated that relatively high numbers of bacterial cells (1.3 x 104 bacteria/ml ovarian fluid, Pascho et al. 1998; and 103 cells/g kidney tissue, Jansson et al. 1996) are necessary for the detection of R. salmoninarum excreted proteins via the Q-ELISA assay. This lower sensitivity of Q-ELISA may not be due to 87 the assay or reagents themselves, but rather to the metabolic activities of R. salmoninarum at the time of testing, which influences the amount of bacterial antigens secreted. It is known that R. salmoninarum can live within fish tissues for a relatively long period in low numbers and in a quiescent state (Bruno 1986), and that R. salmoninarum activation and the secretion of extracellular proteins do not take place in infected fish all of the time. The inherent advantage of Q-ELISA is that this technique allowed us to recognize that the majority Q-ELISA positive fish had relatively low concentrations of R. salmoninarum antigen (83.5%, table 1). Only a minority of fish exhibited medium (6.5%) or high (10%) antigen concentrations. Low R. salmoninarum antigen concentrations indicated the presence of relatively lower numbers of R. salmoninarum in a less active metabolic status when compared to fish with higher R. salmoninarum antigen concentration, a matter that could be associated with either early or late stages of infection (Sami et al. 1992; J6nsdéttir et al. 1998). The lack of agreement in results of the three assays is difficult to explain, however, not surprising since the fish were naturally, rather than experimentally infected. Naturally infected fish of this study were likely at different phases of R. salmoninarum infection at the time samples were collected. This factor may have contributed to the appearance of diverse diagnostic patterns that ranged from full agreement among the three diagnostic assays (e.g., Patterns 3 and 6) to a more unexpected pattern (e.g., Pattern 5). Other factors that likely have contributed to the diversity of 88 diagnostic patterns include differences in the R. salmoninarum dose to which the fish were exposed, pathogenicity of specific R. salmoninarum strains, fish immunologic status, and individual genetic susceptibility. Careful examination of the six patterns reveals what appears to “be a logical progression of infection, with each of the patterns representing a probable stage along the course of R. salmoninarum infection. Pattern 1 is most likely the initial stage of infection establishment within the kidney, with a minimal number of bacteria localized in tissues. Pattern 2 indicates that the infection has been established and bacterial numbers are high enough to be isolated on the MKDM medium. Pattern 3 is the most common, with R. salmoninarum antigens exceeding the detection limit of Q-ELISA. In the fish in which the infection has progressed, R. salmoninarum antigen concentrations increase from low to medium to high. While high R. salmoninarum antigen concentrations are a strong indicator of active, well- established infections that may lead to clinical cases with mortalities, it does not necessarily indicate the presence of the characteristic clinical and pathological manifestations of BKD, including granuloma formation (Miriam et al. 1997; Jensdottir et al. 1998). This is most likely due to the fact that R. salmoninarum soluble antigens suppress a number of fish immune defense mechanisms and thereby host reactions to infection may be lacking (Turaga et al. 1987; Wiens and Kaattari, 1991; Fredricksen et al. 1997, Densmore et al., 1998, Jonstttir et al., 1998; Grayson et al. 2002). 89 Pattern 4 may represents fish that appear to be recovering from R. salmoninarum infection, as viable bacteria present in their tissues were not plentiful enough to be isolated, yet bacterial DNA and R. salmoninarum antigens continue to be present. Fish in Pattern 5 are possibly in an advanced stage of recovery, with only minute traces of R. salmoninarum antigens remaining. Indeed, all 14 fish in this pattern exhibited Q-ELISA values that neared those of the negative control. Renibacterium salmoninarum antigens form immune complexes that deposit in the kidney glomeruli and are eliminated slowly through the kidneys (Sami et al. 1992). Fish in Pattern 6 were either never exposed to R. salmoninarum, refractory to infection, or were infected and then totally eliminated R. salmoninarum and its antigen from their systems. Since R. salmoninarum is widespread in Michigan waters, it is more likely that fish in this group have been exposed to R. salmoninarum before testing. Further restoration and conservation efforts should focus on increasing the proportion of this pattern in salmonid populations. Findings suggest that fish stocks tested in this study are not uniform in the distribution of patterns (Figures 6-9). For example, most of the tested LMRW chinook salmon and PRW MI-adapted coho salmon (both returning from Lake Michigan) were either in pattern 2 (>25%) or 3 (>50%), albeit with low antigen concentrations. It is likely that R. salmoninarum infection in these two Lake Michigan stocks seldom progress. Patterns of SRW chinook salmon and captive lake trout were evenly distributed, indicating an ongoing 9O infection with many fish recovering. In the case of Hinchenbrook coho salmon and captive brook trout, both prevalence and intensity were high, with very few fish in patterns 46 Indeed, in both these stocks, overt clinical signs of BKD and mortalities (in the case of brook trout) are often observed (unpublished observations). Brook trout are known for their high susceptibility to R. salmoninarum infection (Snieszko and Griffin 1955; Mitchum et al. 1979), Hinchenbrook coho salmon strain were introduced to the Great Lakes basin from New York State relatively recently (G. Whelan, Michigan Department of Natural Resources, personal communication) and have proven to be more susceptible to R. salmoninarum infection when compared to the Michigan-adapted coho salmon strain that was introduced to the Great Lakes basin in 1967 (Borgeson 1970; Keller et al. 1990). While the explanations provided herein may logically illustrate the course of R. salmoninarum natural infection, it should be emphasized that the data of this study were generated using kidney tissues only. Kidneys are the primary targets of R. salmoninarum (Fryer and Sanders, 1981); however, other organs should also be assessed in future studies to better understand BKD pathogenesis, particularly in natural infections. So far, the relatively few studies addressing BKD course and progression of infection relied upon experimental infection (Flafio et al 1996, White et al. 1995). Moreover, further correlation of diagnostic testing patterns with clinical observations and tissue alterations in stained sections are needed to better evaluate impacts of R. salmoninarum infection at the population level. 91 Fish & # fish Frequencies of different diagnostic testing patterns" source“ tested Pattern 1 Pattern 2 Pattern 3 Pattern 4 Pattern 5 Pattern 6 LM-CH 42 0 1 1/42 25/42 1/42 5/42 0 (0 %) (26 %) (59.5 %) (2.4 %) (12 %) (0 %) SR-CH 58 1 5/58 1 5/58 12/58 8/58 5/58 2/58 (26 %) (26%) (20.7 %) (13.8 %) (8.6 %) (3.4 %) PR-CO 131 3/131 34/131 75/131 18/131 0 2/131 (2.3 %) (26%) (57.2 %) (13.7%) (0 %) (1.5 %) PR-HB 53 1/53 8/53 43/53 1/53 0 0 (1.9 %) (15%) (81.1 %) (1.9 %) (0 %) (0 %) MBKT 41 4/41 2/41 26/41 8/41 1/41 0 (9.8 %) (4.9 %) (63.4 %) (19.5 %) (2.4 %) (0 %) MLT 39 1/39 17/39 13/39 2/39 3/39 3/39 (2.6 %) (43.5 %) (30.8 %) (5 %) (7.7 %) (7.7 %) Total 364 24 87 1 94 38 14 7 (6.7 %) (23.9 %) (53.3 %) (10.4 %) (3.8 %) (1.9 %) Table 9. Frequencies of different diagnostic testing patterns of salmonid feral spawners and captive broodstocks collected from different geographical locations in Michigan during fall 2002. * Diagnostic testing patterns: Refer to different possible combinations of nPCR, Q-ELISA and Culture results: Pattern 1: Pattern 2: Pattern 3: Pattern 4: Pattern 5: Pattern 6: FOR (+) Q-ELISA (-) Culture (-) pCR (+) Q-ELISA (-) Culture (+) pCR (+) Q-ELISA (+) Culture (+) pCR (+) Q-ELISA (+) Culture (-) PCR (-) Q-ELISA (+) Culture (-) PCR (-) Q-ELISA (-) Culture H ** Fish & source: LM-CH: Chinook salmon collected from Little Manistee Weir SR-CH: Chinook salmon collected from Swan River Weir PR-CO: Michigan adapted coho salmon collected from Platt River Weir PR-HB: Hinchenbrook coho salmon collected from Platt River Weir MBKT: Brook trout collected from Marquette State Fish Hatchery MLT: Lake trout collected from Marquette State Fish Hatchery 92 [- Low I Medium I High [:1 patterns other than 3] 100x.- _ sow Flgure (3A) G) o c: 2 9 (D t- a. 100% 90%, Diagnostic Testing Patterns 30%- 8 70%‘I e 333 T; 40%: Flgure(3B) ID L— o. Diagnostic Testing Patterns Figure 3. Frequencies of different diagnostic testing patterns of feral chinook salmon spawners. Note: 3A: Chinook salmon from Little Manistee Weir 3B: Chinook salmon from Swan River Weir Diagnostic testing patterns: P (nPCR), Q (Q-ELISA) and C (Culture). Clear columns represent any diagnostic testing pattern other than pattern (3) Colored column represents pattern (3) with three colors referring to different 0- ELISA intensities in this pattern. Intensity was considered high if the antigen concentration 21; medium if the antigen concentration = 0.20-0.99; and Low if the antigen concentration = 0.10 to 0.19. This figure Is In color 93 Ll Low IMedIum Ingh Deny pattern other than (3)] 100% ' 90% ‘ 80% " 70% ‘ 00% ‘ 509p FIQUI’O (4A) 40% ‘ 30% ' 20* ‘ 10% ‘ 0% ‘ prevalence Dlag nostlc Testing Patterns 100% - 90% " 80% r 70% - 00% ~ 50% ‘ 40% .. 3096 r 20% . 10% .. 0% ‘ Figure (4B) prevalence Dlag nostlc Testlng Patterns Figure 4. Frequencies of different diagnostic testing patterns of feral coho salmon spawners collected from the Platte River Weir Note: 4A: Michigan adapted coho salmon 48: Hinchenbrook coho salmon Diagnostic testing patterns: P (nPCR), Q (Q-ELISA) and C (Culture) Clear columns: represent any diagnostic testing pattern other than pattern (3) Colored column: represents pattern (3) with three colors referring to different 0- ELISA intensities in this pattern. Intensity was considered high if the antigen concentration 21; medium if the antigen concentration = 0.20-0.99; and Low if the antigen concentration = 0.10 to 0.19. This figure color 94 II Low II Medium ll High Cl any pattern other than (3)] 100%- 90% ‘ 30%- 709% 60%- sow 40% sow 20% 10% 0%- Figure (5) prevalence Diagnostic Testing Patterns 100%" Figure (6) 90% . nox- 70% cow 50%- 40%- 30%“ 20%- 109% ow prevalence Diagnostic Testing Patterns Figure 5 - 6. Frequencies of different diagnostic testing patterns of captive hatchery broodstock. Note: Figure 5: Brook trout Figure 6: Lake trout Diagnostic testing patterns: P (nPCR), Q (Q-ELISA) and C (Culture) Clear columns: represent any diagnostic testing pattern other than pattern (3) Colored column: represents pattern (3) with three colors referring to different 0- ELISA intensities in this pattern. Intensity was considered high if the antigen concentration 21; medium if the antigen concentration = 0.20-0.99; and Low if the antigen concentration = 0.10 to 0.19. This figure is In color 95 CHAPTER FOUR CURRENT STATUS OF RENIBACTERIUM SALMONINARUM INFECTION IN CHINOOK (ONCORHYNCHUS TSHAWYTSCHA) AND COHO (ONCORHYNCHUS KISUTCH) SALMON AT MICHIGAN WEIRS AND HATCH ERIES ABSTRACT Since the recent introduction of chinook and coho salmon to Lake Michigan in the late 19603, number of Bacterial Kidney Disease (BKD) epizootics has resulted in mass dieoffs among the feral spawner stage of these fish. The first epizootic occurred among the coho salmon spawners in 1967 while the latest occurred among the same stage of chinook salmon throughout the period between late 19803 and early 19903. Management of the disease by hatchery personnel and natural resources managers attempting to interrupt the cycle of infection and focus on two life stages; namely, the gamete-collection stage and the fry/fingerling stage while reared at state fish hatcheries prior to their release. Data generated in this study provide additional evidence that (Renibacterium salmoninarum) R. salmoninarum infection is enzootic in Michigan and widespread in feral stocks of chinook and coho salmon in both lakes Michigan and Huron. Lake Michigan’s salmon tend to have an overall higher prevalence than that observed in Lake Huron’s fish. Renibacterium salmoninarum 96 prevalence in returning feral chinook salmon seem to fluctuate among years, although a definitive decrease can be observed since the start of this study in 2001. However, both strains of coho salmon spawners showed a steady decline in R. salmoninarum prevalence throughout the 4 years period. Data of this study demonstrates the ability of both chinook and coho salmon females and males to shed R. salmoninarum through the ovarian fluid and milt. Results also indicated that over 90% of female and 80% of male chinook salmon tested in this study from both watersheds were not shedding R. salmoninarum antigens along with their gametes. The case was different in coho salmon as both male and females shed R. salmoninarum antigens at different rates. The R. salmoninarum antigen concentrations in Hinchenbrook gametes were significantly higher than in the MI- adapted gametes. The BKD testing of both feral spawners and their hatchery raised offspring fingerlings demonstrates that the current testing and culling programs have been successful in reducing R. salmoninarum transmission. This study also demonstrates that some hatchery practices were more effective than others in controlling the spread of R. salmoninarum and that a reliable improvement in the reduction of R. salmoninarum prevalence within the hatcheries involved in this study has been achieved. 97 INTRODUCTION Over the last 150 years, several attempts have been made to introduce Pacific salmon species into the Great Lakes. The Michigan Department of Natural Resources (MDNR) initiated the most recent and successful of these introductions in 1966 for coho salmon (Oncorhynchus tshawytscha) and 1967 for chinook salmon (Oncorhynchus kisutch). In 1966, MDNR stocked a total of 659,000 coho salmon yearlings in a tributary of the Manistee River and the Platte River (Borgeson 1970). In 1967, similar number of chinook salmon smolts from the west coast was introduced into Lake Michigan (Keller et al.1990). After introduction, both chinook and coho salmon spread throughout the Great Lakes basin where they have become the most popular sport and commercial fishery in the State of Michigan (Dexter and O’Neal 2004). Currently, the Maintenance of the salmon population in the Great Lakes is primarily dependent upon the stocking of hatchery-propagated fish. This practice requires the collection of gametes at the weirs from the fall returning runs, the raising of the offspring at state hatcheries, and the subsequent release of fingerlings at a weight 4-6 g/fish (Dexter and O’Neal 2004). The stocked fingerlings move to the smolt stage at the various stocking sites in the rivers, and then begin their migration to the Great Lakes (Seelbach 1985). Three to four years later, spawning runs of salmon return with high fidelity to the Michigan 98 streams in which they were either stocked or spawned. Once either natural or man-assisted spawning has commenced, the fish perish (Dexter et al. 2004). In 1967, multiple cases of coho salmon mortalities were reported by anglers along the shores of Lake Michigan. MacLean and Yoder (1967) confirmed the presence of clinical BKD in adult coho salmon that were dying along the shores of Lake Michigan. The authors also reported that Lake Superior coho salmon suffered higher BKD prevalence than those of Lake Michigan and the males had higher prevalence than females. In 1986, clinical cases of were also observed in spawning chinook salmon runs at the Little Manistee River Weir, Michigan. The disease became more prevalent in subsequent years, and incidence ranged from 53-100% during 1986-1991 (Holey et al. 1998, Hnath and Faisal 2005). Concomitant with the BKD surge occurring at the weirs, chinook salmon die-offs were reported in 1986 and 1987 and reached a peak in 1989. Minimum estimates of 20,000 adult fish were found dead (Johnson and Hnath 1991). The majority of dead fish exhibited lesions indicative of BKD, hence BKD was considered to be a major contributing factor to the chinook salmon kills. Starliper et al. (1997) demonstrated that the R. salmoninarum isolates associated with chinook and coho salmon mortalities in Michigan are more virulent than those retrieved from other regions in North America. Renibacterium salmoninarum is an obligate intracellular pathogen that is transmitted both horizontally (Mitchum and Sherman 1981; Bell et al 1984) and vertically (Evelyn et al. 1984, 1986). Renibacterium salmoninarum pathogenicity relies upon a number of extracellular proteins (ECP) that possess 99 immunosuppressive, proteolytic, hemolytic, and DNA degrading activities (Austin and Rodgers 1980; Bruno and Munro 1986b; Turaga et al. 1987; Fredriksen et al. 1997). When ECP alone were injected into susceptible fish, 80-100% mortalities may occur (Shieh 1988). The ECP contain a water-soluble, cell surface, 57- kDa protein (p57) that has been demonstrated to be a major virulence factor of R. salmoninarum (Getchell et al. 1985; reviewed in Wiens and Kaattari 1999). The occurrence of vertical transmission of R. salmoninarum is well documented (Evelyn et al. 1984; Lee and Evelyn 1989), but believed to be rare (Hamel 2001). It seems that inclusion of R. salmoninarum-ECP into the eggs increases the susceptibility of the offspring to R. salmoninarum infection (Brown et al.1996). The studies of Brown et al. (1996) provided evidence that infra-ovum inclusion of p57 can result in decreased immune functions when the resulting fry are exposed to R. salmoninarum. The likelihood of vertical transmission of the disease (from parent to offspring) or infra-ovum antigen inclusion immunotolerance is related to the ovarian fluid infection levels (Hamel 2001). Another complication results from the fact that the entry of R. salmoninarum-ECP may cause life-long immunotolerance of the disease, greatly decreasing the probability of survival to spawning (Hamel 2001). Because R. salmoninarum can be transmitted vertically, MDNR adopted a stringent visual inspection on each spawning female and the subsequent culling of any gametes previously collected from spawning females showing overt signs of clinical BKD. In addition, kidney swabs of individual fish were routinely examined for the presence of R. salmoninarum soluble antigens using a 100 monoclonal antibody based Field ELISA (FELISA) (Gary Whelan, MDNR personal communication). This rapid field test allowed the detection of fish whose kidneys are laden with R. salmoninarum antigen, and exclusion of their eggs from further incubation (Beyerle and Hnath 2002; Hnath and Faisal 2005). Neither health inspection, nor FELISA were performed on males because the published studies of Klontz et al. (1983) and Evelyn et al. (1986) minimized the role that male fish play in the vertical transmission of R. salmoninarum. In the Great Lakes, chinook and coho salmon are not in their native range, yet many of the stocked fish are able to survive and return to rivers to successfully spawn. How returning salmon were able to co-exist with R. salmoninarum in a non-native range is currently unknown and deserves further investigation. This is particularly important since most of our knowledge on R. salmoninarum-returning spawner salmon interactions originated from studies performed in the Pacific Northwest, where the fish alternate between marine and freshwater environments. Hence, the major thrust of this chapter is to identify some of the basics of the R. salmoninarum- returning spawner salmon relationship in Michigan waters such as the prevalence and intensity of R. salmoninarum infection in returning spawning runs, the contribution of both males and females to shedding of R. salmoninarum and its immunosuppressive soluble antigens. Additional aim of this study is to determine the efficacy of the culling program and hatchery practices on minimizing vertical and horizontal transmission of R. salmoninarum. 101 MATERIALS AND METHODS Fish and sampling. In this study, samples were collected from three major egg-take weirs, and three state fish hatcheries in Michigan (table 10). Chinook salmon samples from returning spawners were collected from the Little Manistee River Weir (LMRW, Manistee County, Lake Michigan watershed) and Swan River Weir (SRW, at Rogers City, Presque Isle County, Lake Huron watershed). LMRW is the major chinook salmon egg collection operating weir on the Michigan-side of Lake Michigan, situated on the Little Manistee River, a major trout tributary that annually receives millions of fingerlings via stocking. Swan River Weir is the only egg-take facility on Lake Huron and is considered an ideal tributary for the further development of pre-smolts to the smolt stage before emigration to Lake Huron (Dexter and O’Neal, 2004). Coho salmon samples were collected from two strains of coho salmon; the Michigan-adapted and the Hinchenbrook strains. Adult coho salmon spawning runs were sampled at the Platte River Weir (PRW), off the Platte Bay, at Beulah, Ml (Lake Michigan watershed) during egg-takes in the falls of 2001 through 2004. Platte River Weir is the only operating egg-take weir on the Michigan-side of Lake Michigan that is used exclusively for collecting coho salmon gametes. For the purpose of this study, kidney tissues were sampled from 303 and 653 chinook salmon spawners at the LMRW and SRW respectively (table 10). A total of 383 and 273 kidney samples were sampled from Michigan adapted coho and Hinchenbrook coho salmon spawners respectively at the PRW (table 10). 102 Additionally, in 2004, ovarian fluid was collected from 280 and 60 chinook salmon females at SRW and LMRW respectively. Moreover, ovarian fluid was also collected from 60 Michigan adapted and 60 Hinchenbrook coho females at PRW. Concomitantly, milt from 60 LMRW chinook, 60 PRW Michigan adapted coho, and 60 PRW Hinchenbrook coho male spawners were collected in 2004. Following an approximate 8 (for chinook salmon) and 18 (for coho salmon) month period of egg incubation and fish rearing in three state fish hatcheries (Wolf Lake state hatchery (WLH) in Mattawan city, Platte River state hatchery (PRH) in Beulah city, and Thompson state hatchery (THH) in Manistique, Michigan), kidney tissues of juvenile fingerlings were collected prior to their release into the basins of lakes Michigan and Huron and subsequently analyzed for the presence of R. salmoninarum. Within the period of 2002-2005, a total of 965 chinook and 480 coho salmon kidney samples were collected from juvenile fingerlings at WLH (360 chinook salmon), PRH (425 chinook and 480 coho salmon), and THH (180 chinook salmon) (table 11). The sacrifice of feral spawners entailed exposing the fish to carbon dioxide- Iaden water, followed by a blow to the head. Following gamete collection, the abdominal cavity was cut open to examine individual internal organs for signs associated with BKD, followed by the collection of approximately one gram of tissue from anterior, posterior and middle kidney sections. Cross contamination was avoided by using sterile dissecting tools for each fish. Coelomic fluid samples were collected using sterile transfer pipettes from the egg/ovarian fluid mixture, transferred to 5 ml sterile polypropylene tubes, and kept on ice until 103 processed at the laboratory (Michigan State University, East Lansing, MI). Milt samples were collected directly from the middle stream of milt into sterile 10-ml polypropylene tubes. Fingerlings were euthenized by immersion in an overdose of anesthesia using MS-222 (tricaine methan sulfonate, Finquel- Argent Chemical Laboratories, Washington). Sampling and sample processing: Samples from fish were analyzed individually unless otherwise indicated. Kidney samples from the anterior, posterior, and middle sections of the kidney were transferred in sterile 7.5 cm x 18.5 cm Whirl Pak® bags (Nasco, Forte Atkinson, WI), kept on ice, and were softened as much as possible through multiple cycles of physical pressure. The homogenized kidney tissues were diluted 1:4 (w/v) with Hank’s Balanced Salt Solution (HBSS, Sigma Chemical Co, St. Louis, MO, USA) and then stomached for 2 minutes at high-speed using the Biomaster Stomacher—80 (Wolf Laboratories Limited, Pocklington, York, UK). In the case of either milt or ovarian fluid, 1 ml of each sample was diluted 1:2 (v/v) in HBSS for Q-ELISA. Measurements of Renibacterium salmoninarum antigen using the Quantitative Enzyme-linked Immunosorbent Assay (Q-ELISA). Aliquots of 250 pl of each sample were transferred into 1.5 ml safe lock microfuge tubes, to which an equal volume of 0.01 M Phosphate Buffered Saline Tween 20 (0.05 % PBS-T20) (Sigma) with 5 % natural goat serum (Sigma) (Olea et al. 1993) and 50 pl CitriSoIv solution (Fisher Chemicals, Fairlawn, New Jersey, USA) 104 (Gudmunsdottir et al. 1993) were added. The solution was then thoroughly vortexed, incubated at 100 °C on heat blocks with a rotary shaker for 15 minutes, followed by 2 hours of incubation at 4 °C. After incubation, the mixture was centrifuged at 60009 for 15 minutes at 4 °C. The aqueous supernatant of each sample was carefully collected and then transferred to a 1.5 ml microfuge tube for Q-ELISA. The Q-ELISA method used in this study was described by Pascho and Mulcahy (1987); Alcorn and Pascho (2000). The positive-negative threshold absorbances were calculated according to the method described by Meyers et al. (1993) .The positive—negative cutoff absorbance for the kidney homogenate was 0.10. The Q-ELISA positive samples were assigned the following antigen level categories: low (0.10 to 0.19), medium (0.20-0.99) and high (1.000 or more) as developed by Pascho et al. (1998). Intensity of infection among certain group of fish is determined by the prevalence of samples that possess high Q-ELISA antigen concentrations. Statistical Analysis: Due to the nature of this study, descriptive statistics were heavily relied upon. For year-to-year, salmon strains differences, gamete source, and hatchery comparisons, the data was tested for normality, and then analyzed by an analysis of variance (ANOVA), student t test (parametric) or Mann-Whitney Rank Sum (nonparametric) Tests with an alpha = 0.05 (P=0.05). 105 RESULTS 1. Renibacterium salmoninarum prevalence and intensity in kidney tissues of returning salmon spawners. Renibacterium salmoninarum antigens have been detected in the kidneys of chinook and coho salmon returning to both weirs in every year sampling took place. Generally, there was a slight decline in prevalence and intensity when the data of 2004 was compared with that of 2001. a. Chinook salmon returning spawners. The prevalence of R. salmoninarum in chinook salmon returning to the Little Manistee Weir (LMRW) gradually decreased from 84% in 2001 to 20 % in 2003, before abruptly rising to 67% in 2004. Additionally, R. salmoninarum intensity from the same fish groups declined from 5% in 2001 to 0% in 2002, and then increased slightly to 2.5% in 2003 and 2004. The prevalence of R. salmoninarum in the Swan River Weir (SRW) constantly declined, but the intensity followed a different trend. The prevalence of R. salmoninarum in the SRW chinook salmon declined from 46% in 2002 to 12.3 % in 2004. However, R. salmoninarum intensity in the SRW fish showed a slight decrease from 5% in 2002 to 3% in 2003, with a subsequent increase to 4% in 2004 (Figure 7). Comparison of the prevalence and intensity of R. salmoninarum in the feral spawner chinook from the two weirs demonstrated a consistently higher prevalence in the LMRW chinook salmon, with the exception of the samples taken in 2003. On the contrary, the intensity of the disease seemed to be higher in the SRW salmon over the same period of analysis (Figure 7). However, statistical analysis of the data revealed that difference 106 between the prevalence of R. salmoninarum in chinook salmon collected from the two different weirs and at the same hatchery in different years of collection was insignificant. To determine sex-related differences among chinook salmon from LMRW and SRW, R. salmoninarum prevalence and intensity was determined in separate groups of males and females returning to both weirs in 2002 and 2004. Data showed no statistically significant differences between males and females from both weirs, although there was a trend for males to have higher prevalences and intensities of infection as compared to females (Figure 10). b. Coho salmon returning spawners. The prevalence of R. salmoninarum in Michigan-adapted coho strain decreased from 84% in 2001 to 64.8 % in 2002 then to 40 % in 2003 ending with 24.2 % in 2004. Additionally, R. salmoninarum intensity from the same fish group showed no marked difference through the period between 2001 and 2004 (F igure 8). The prevalence of R. salmoninarum in the Hinchenbrook strain has decreased from 100 % in 2001 to 82 % in 2002 then to 29 % in 2003, before rising to 72.5% in 2004. The intensity of infection in the same group of fish followed a similar trend in which the intensity has decreased from 49 % in 2001 to 21.4 % in 2002 then to 10.4 % before sharply increasing to 47.5 % in 2004 (Figure 8). Comparison of the prevalence and intensity of R. salmoninarum in spawners of both coho salmon strains demonstrates a consistently higher prevalence and intensity in the Hinchenbrook coho with the exception of the samples taken in 2003. Additionally, clinical examination of the Hinchenbrook, but not the Ml-adapted, strain revealed 107 the presence of signs characteristic of BKD. Statistical analysis showed statistical difference (P< 0.05) increases in both prevalence and intensity of R. salmoninarum over the years in the Hinchenbrook strain as compared to the MI- adapted strain. Moreover, data showed no statistically significant differences between males and females from both weirs 2. Renibacterium salmoninarum prevalence and Intensity in ovarian fluid and milt of returning salmon spawners. The shedding of R. salmoninarum with the gametes was tested in 2004 returning spawners. As displayed in tables 12, 13 and 14, R. salmoninarum and its soluble antigens were passed along with the gametes of both sexes albeit not in all of the infected fish. a. Chinook salmon returning spawners. While 28/60 (47%) LMRW female salmon were infected; only 6 of these fish had R. salmoninarum antigens in their ovarian fluids (table 13). Similarly, only half of the infected SRW females exhibited R. salmoninarum antigens in their ovarian fluids. The same trend was noticed in the LMRW males, with only 20% of infected fish had R. salmoninarum antigens in their milt. Table 13 summarizes the difference in prevalence between kidneys and gametes of the same fish. More than 80% of the fish produced R. salmoninarum-free gametes (sum of groups 1 and 2 in table 13), even though some of these fish had R. salmoninarum in their kidneys. Indeed, a few of these fish exhibited medium and high R. salmoninarum antigen titers in the kidneys. In the case of LMRW males, the concentrations of R. salmoninarum soluble 108 antigens in milt as determined by Q-ELISA coincided with that found in the kidney tissues in all individual fish. Similar findings were observed in the LMRW, with the exception of females# 5 and 29, which had very high R. salmoninarum antigen concentrations in the ovarian fluid, while their kidney had low antigen concentrations. Another LMRW female (# 43) shed the R. salmoninarum antigen in a very low level in the ovarian fluid, while the kidney tissues tested negative. A similar trend was noticed with the SRW chinook salmon, where 18 females shed the R. salmoninarum antigen in the ovarian fluid, while the majority of females exhibited a comparable titer of R. salmoninarum antigens in both ovarian fluids and kidneys. Five fish (1.8%) shed the antigens in the ovarian fluids while their R. salmoninarum antigen in their kidney was below the detection level (Group 4 in table 13). b. Coho salmon returning spawners. Although 24.2% of the MI adapted coho strain was infected, only 11.7 % of these fish had R. salmoninarum antigens in their ovarian fluids. Similarly, while 72 % of the MI adapted coho strain was infected, only 50 % of these fish had R. salmoninarum antigens in their ovarian fluids (table 12). The same trend was noticed in the MI adapted coho males, with only 5% of infected fish having R. salmoninarum antigens in their milt samples. However, results demonstrated that the Hinchenbrook coho males shed more R. salmoninarum and its antigens (55 %) in milt than that of the MI adapted strains (5 %) (tables 12 and 14). The same trend was noticed when comparing the prevalence and intensity of R. salmoninarum antigens shed along with ovarian fluid of females of both strains (tables 12 and 14). 109 3. Renibacterium salmoninarum prevalence and intensity in kidney tissues of hatchery-raised juvenile fingerlings. The prevalence of BKD in juvenile spring salmon (originally hatched from the fall returning spawner parents) raised in three hatcheries was followed for four consecutive years (2002-2005; tables 15-16 and Figure 11). In general, R. salmoninarum prevalence and intensity infection were lower in offspring when compared to parent stocks. a. Chinook salmon juvenile fingerlings. In case of chinook salmon, this relationship was not present when the results of R. salmoninarum testing were grouped by individual hatchery. However, offspring raised in certain hatcheries tended to exhibit a consistent pattern. For example, chinook salmon fingerlings raised in Thompson state fish hatchery (THSF H) exhibited the lowest prevalence and intensity of R. salmoninarum in kidneys when compared to their cohorts raised in other hatcheries. Year to year comparison, however, showed that over the years, R. salmoninarum prevalence has declined in the other two hatcheries as well. For example, R. salmoninarum prevalence in spring chinook salmon fingerlings, originally spawned at LMRW and then raised in WLSFH, declined from 100% in 2002 to 5% in 2005 (table 15). Similarly, the prevalence of spring chinook salmon originally spawned at LMRW and raised at PRSFH declined from 100% in 2003 to 0% in 2004 and 5% in 2005. Likewise, spring chinook salmon originally spawned from SRW parents and hatched in WLSFH showed a decline in BKD prevalence from 35% in 2004 to 10% in 2005 (table 16). Sharp decreases 110 in BKD prevalence was also noticed in the spring Chinook salmon from PRSFH between 2003 and 2004 (92% vs. 0%) before slightly increasing to 8.3% in 2005. However, statistical analysis revealed non-significant differences in prevalence and intensity of infection when year-to-year comparison or hatchery-to-hatchery comparisons were adopted. b. Coho salmon juvenile fingerlings. The prevalence of BKD in spring coho salmon juvenile fingerlings raised in the Platte River State Fish Hatchery was followed up for three consecutive years (2003-2005). In general, R. salmoninarum prevalence and intensity was lower in offspring when compared to parent stocks (Figure 11). Year to year comparison, however, showed that over the years, R. salmoninarum prevalence has steadily declined in the two coho salmon strains. For example, R. salmoninarum prevalence in MI adapted coho salmon fingerlings, originally spawned from MI adapted coho salmon spawners at PRW and then raised in PRSFH, declined from 50 % in 2003 to 27 % in 2004 ending with 6.7 % in 2005. The same trend was noticed among the Hinchenbrook coho fingerlings raised at the same hatchery in which the prevalence was steadily decreased from 75 % in 2003 to 22 % in 2004 ending with slight decline to 20 % in 2005. Comparing the R. salmoninarum prevalence in the two strains of hatchery-raised coho salmon to that of their corresponding parents demonstrated that fingerlings follow a statistically significant (P<0.05) decline in the 2004 and 2005 samples of both strains. Data also demonstrated that Hinchenbrook coho salmon fingerlings possessed statistically significant 111 higher R. salmoninarum prevalence (P<0.05) than the Ml-adapted coho strain through the 3 years testing period. 112 DISCUSSION Data generated in this study provide additional evidence that R. salmoninarum infection is enzootic in Michigan and widespread in feral stocks of feral spawner salmon in both lakes Michigan and Huron. As displayed in Figure 7, Lake Michigan’s Chinook salmon tends to have an overall higher prevalence than that observed in Lake Huron’s Chinook salmon. In the case of SRW chinook salmon, prevalence was much lower and intensity was relatively higher when compared to the LMRW salmon. The stocking of chinook salmon in Lake Huron is a relatively new event that started in the 19903, unlike in Lake Michigan, where chinook salmon have been stocked since 1967 (Dexter and O’Neal, 2004). The recent Chinook salmon introduction in Lake Huron has most likely contributed to the relatively low R. salmoninarum infection prevalence observed in this study. Renibacterium salmoninarum infection prevalence and intensity in returning feral chinook salmon seem to fluctuate among years, although a reliable decrease can be observed since the start of this study in 2001. However, the unexpected surge in prevalence recorded in the 2004-LMRW salmon is alarming. A similar increase in R. salmoninarum prevalence was observed in the Lake Michigan stock of Hinchenbrook coho salmon, a strain of coho salmon that is especially susceptible to R. salmoninarum. Further studies are needed in forthcoming years to monitor R. salmoninarum infection levels in Lake Michigan salmon stocks. 113 Although Ml-adapted and Hinchenbrook strains belong to the same species and residing in the same watershed, they exhibited marked differences in R. salmoninarum prevalence and intensity. There are no published reports on R. salmoninarum infection in the Hinchenbrook strain from New York, from which it was imported, yet this strain is known in New York for its marked growth, high survival and return rates (John Shachte, personal Communication). The susceptibility of the Hinchenbrook strain to R. salmoninarum may be related to its recent introduction into Lake Michigan where BKD is enzootic. The decrease in R. salmoninarum prevalence over the years is a good indication of a beginning of adaptation of the strain to its new environment. When the Ml-adapted strain was first introduced from the Pacific Northwest, BKD-related epizootics were reported along the shores of Lake Michigan (MacLean and Yoder, 1967). Adaptation in R. salmoninarum-contaminated environments has been reported in the Arctic char and the brown trout in Iceland (Jonsddttir et al. 1998). Genetic make up of the two strains may have also played a role in the difference in R. salmoninarum susceptibility. Winter et al. (1980) reported the presence of genetic basis for differences in susceptibility to R. salmoninarum among of steelhead trout strains. Further, Beacham and Evelyn (1992) also reported the presence of differential susceptibility to R. salmoninarum in a number of chinook salmon strains. Other important factors that may have contributed to differences between the two strains is their diverse migration patterns in Lake Michigan (Dexter and O’Neal, 2004). 114 Based only on the data of this study, it is difficult to determine whether such high levels of R. salmoninarum are associated with BKD-related mortalities. The eruption of BKD in R. salmoninarum infected fish is influenced by a number of factors including changes in habitat and forage fish availability. As reported from other fish species and pathogens, changes in the spatial distribution of fish and increased density of the fish population can affect the frequency of contact between infected and non infected migrating fish which will be translated to rapid spread and progression of infection (Reno, 1998). For example, the 1989 BKD epizootic in chinook salmon was associated with a sharp decline in forage fish availability (Holey et al.1998). Combining the results of 2002 and 2004 kidney Q-ELISA data (Figure 9), males tend to have an equal or slightly higher R. salmoninarum prevalence than females. In the North Pacific USA, where much of Chinook salmon BKD data has been generated, females seem to have a much higher R. salmoninarum prevalence and intensity than males (Evelyn et al. 1986). Most of the studies, however, were performed using experimental infection models. The gradual decrease of prevalence and intensity among both chinook and coho salmon coho salmon spawners could be due to the culling procedures adopted in weirs which could minimized the possibility of vertical transmission through infected females to their offspring. Also, the application of strict hygienic measures in weirs by rinsing the spawner fish in iodophores (Ross and Smith 1972) before collecting eggs or milt, using sterile utensils for egg-milt mixing and storage could have minimized the bacterial load transmitted to eggs and milt in 115 weirs. Moreover, efficient weir practices such as incubating fertilized eggs in clean disinfected trays and incubators as well as hardening of eggs in 2-ppm erythromycin solution (Amos 1977), could have reduced the prevalence and intensity of BKD in the production fish before their release into the Platte River (Maule et al.1996). Results indicated that the 2003 Hinchenbrook coho salmon fingerlings showed higher BKD prevalence (75%) than that of MI-adapted coho (50 %), which appears consistent with the high R. salmoninarum prevalence results of their 2001 parents. As demonstrated by Evelyn et al. (1986), the likelihood of vertical transmission in heavily infected salmon is higher than in lightly infected gamete donors. Moreover, data showed that female MI-adapted coho salmon feral spawner showed slightly higher R. salmoninarum prevalence than males of the same strain in the 2002 and 2004 samples. Female coho salmon are usually stressed with the relatively large size of their egg-laden ovaries that occupy more than 70 % of the fish body during the spawning season. Interestingly, the data presented in this study demonstrates the ability of feral spawner chinook and coho females to vertically transmit the bacterium through the ovarian fluid (tables 12-13). This fluid surrounds the eggs once they have been released into the body cavity following ovulation (Evelyn et al. 1986). Most of the chinook spawner females that shed R. salmoninarum in their ovarian fluid tested positive in the kidneys (table 13). Only in <2% of the chinook females, R. salmoninarum was shed in the ovarian fluid, but not in the kidneys. There are three explanations for the appearance of this phenotype. First, 116 kidneys are infected in levels that are below the Q-ELISA detection limit. Second, the fish were recovered from a prior R. salmoninarum infection, which left remnants of R. salmoninarum-ECP that are known to be excreted in a slow fashion (Sami et al. 1992). Indeed, R. salmoninarum antigen levels in these fish were extremely low. Last, kidney samples may have given false negative results. Most important, however, was the fact that over 90% of chinook salmon tested in this study from both watersheds were not shedding R. salmoninarum antigens in the ovarian fluid, which is much less than originally thought. As a result, high levels of R. salmoninarum prevalence and intensity in hatchery fingerlings cannot be attributed to vertical transmission alone. Moreover, the slow multiplication of R. salmoninarum would not allow the infection to develop in < 6 month old juvenile chinook salmon fingerlings to levels such as those observed In the fingerlings of 2002 and 2003. Therefore, it is likely that horizontal transmission plays a role in spreading infection among hatchery-propagated fish. There is no doubt, however, that the exposure of offspring to the immunosuppressive R. salmoninarum-ECP can predispose the fish to infection with R. salmoninarum or other pathogens. Data also demonstrated that over half of Hinchenbrook females and males shed R. salmoninarum along with the gametes as opposed to 12% in females and 5% males of the Ml-adapted strain. This extreme difference can account for the higher prevalence and intensity of R. salmoninarum in the Hinchenbrook strain as compared to the Ml-adapted strain. On the contrary, a higher percent of infected adult Hinchenbrook coho salmon did not shed R. salmoninarum despite 117 the high levels of R. salmoninarum intensity in their kidneys (Group 2 in table 13). By combining fish in Groups 1 and 2 of table 14, it became clear that a very high percent of coho salmon shed R. salmoninarum-free gametes, a matter that may lead to a reduction of R. salmoninarum infection incidence in the future. Group 4 on the contrary, are fish that shed R. salmoninarum antigen along with the gametes despite their non-detectable R. salmoninarum levels in the kidneys. Group 4 and group 3 are probably the cause of the continuous presence of R. salmoninarum across generations. High portions of the Hinchenbrook females shed R. salmoninarum in their coelomic fluid were tested positive in the kidneys. Only in <2% of the Hinchenbrook and MI adapted coho females, R. salmoninarum shed in the coelomic fluid, but not in the kidneys. It has also been demonstrated that males shed R. salmoninarum in their milt, sometimes in high concentrations, and thereby may contribute to the spread of R. salmoninarum into eggs through the micropyle during fertilization. In addition, the potential exposure of the embryo to immunosuppressive R. salmoninarum- ECP from the milt cannot be ignored (Hamel 2001). It should be noted that only 10 out of 53 infected LMRW males shed R. salmoninamm antigen in their milt, while the remaining males were able to keep their seminal plasma below the Q- ELISA detection limits. There is a handful of papers that addressed the role of males in the transmission of R. salmoninarum in chinook and coho salmon. The studies of Evelyn et al. (1986) and Rocky et al. (1991) suggested that the role of males in infecting eggs is minimal. Data of this study, however, contradicts other reports and demonstrates that males are capable of shedding R. salmoninarum 118 more than females of the same stock. Further, we strongly recommend that the testing and culling policy, currently applied to females only, be expanded to include males. The BKD testing of both feral spawners and their hatchery raised juvenile fingerlings demonstrates that the current testing and culling programs have been partially successful in reducing R. salmoninarum transmission. This study also demonstrates that some hatchery practices were more effective than others in controlling the spread of R. salmoninarum and that a reliable improvement in the reduction of R. salmoninarum prevalence within the three hatcheries involved in this study has been achieved. The aforementioned assumption coincided with that of Maule et al. 1996 who reported variations in R. salmoninarum prevalence among hatcheries in fingerlings derived from the same stock. 119 Salmon species and source Date collected Number of fish tested Chinook salmon spawners October, 2001 60 from LMRW October, 2002 63 October, 2003 60 October, 2004 120 Chinook salmon spawners October, 2002 59 from SRW October, 2003 34 October, 2004 560 Michigan adapted coho October, 2001 38 salmon spawners from October, 2002 165 PRW October, 2003 60 October, 2004 120 Hinchenbrook coho salmon October, 2001 49 spawners from PRW October, 2002 56 October, 2003 48 October, 2004 120 Table 10. Details of samples collected from spawning chinook and coho salmon returning to egg-take weirs throughout the period from 2001-2005. LMRW: Little Mansitee River Weir SRW: Swan River Weir PRW: Platte River Weir 120 Rearing Date Egg-take Weir Number hatchery Collected of fish tested Wolf Lake State March 2002 Little Manistee River 60 Fish Hatchery Weir March 2003 Little Manistee River 60 Weir March 2004 Little Manistee River 60 Weir Swan River Weir 60 March 2005 Little Manistee River 60 Weir Swan River Weir 60 Platte River March 2002 Little Manistee River 65 Weir State Fish Weir Hatchery March 2003 Little Manistee River 60 Weir Swan River Weir 60 March 2004 Little Manistee River 60 Weir Swan River Weir 60 March 2005 Little Manistee River 60 Weir Swan River Weir 60 Thompson March 2003 Swan River Weir 60 State FISh March 2004 Swan River Weir 60 Hatchery March 2005 Swan River Weir 60 Total 965 Table11. Chinook salmon juvenile fingerlings collected from Michigan state fish hatcheries in the period from 2002-2005. 121 Fish species # of tested body Renibacterium % Q-ELISA positive titers and source fluid samples salmoninarum High Medium Low prevalence Chinook 60 ovarian Fluid 6/60 1/60 1/60 4/60 salmon form (10 %) (1.5 %) (1.5 %) (7 %) LMRW so Milt 10/60 8/60 2/60 0/60 (63.5 %) (13 %) (3 %) (0%) Chinook 280 ovarian Fluid 18/280 11/280 2/280 5/280 salmon from (6.4 %) (4 %) (0.7 %) (1.78 SRW %) Michigan 60 ovarian Fluid 7/60 5/60 1/60 1/60 adapted coho (11.7 %) (8.3 %) (1.7 %) (1.7 salmon from %) PRW 60 Semen 3/60 0/60 0/60 3/60 (5 %) (0 %I (0 %l (5 %) Hinchenbrook 60 ovarian Fluid 30/60 15/60 3/60 12/60 coho salmon (50 %) (25 %) (5 %) (20 from PRW %) 60 Semen 33/60 4/60 9/60 20/60 (55 %) (6.7 %) (15 %) (33.3 %) Table 12. Renibacterium salmoninarum prevalence and intensity in ovarian fluid and milt of the 2004 chinook and coho salmon spawners. Data in this table was generated using a polyclonal antibody-based quantitative ELISA (Q-ELISA) performed on kidney tissues. Prevalence was determined by % of Q-ELISA positive samples of the total number of samples tested. Intensity was considered high if the antigen concentration 21; medium if the antigen concentration = 0.20-0.99; and Low if the antigen concentration = 0.10 to 0.19. SRW: Swan River Weir. PRW: Platte River Weir. 122 Fish Group LMRW SRW Females Males Females 1. Kidneys 8. Gametes negative 28/60 7/60 240/280 (46.7%) (11.7%) (85.7%) 2. Kidneys + & Gametes - 26/60 43/60 22/280 (43.3%) (71.7%) (7.9%) 3. Kidneys + & Gametes + with 5/60 10/60 13/280 same Renibacterium salmoninarum (8.3%) (16.6%) (4.6%) anfigenlevel 4. Kidneys - & Gametes + with very 1/60 0/60 5/280 low Intensity (1.6%) (0 %) (1.8%) Table 13. Renibacterium salmoninarum prevalence in kidney and gametes of the 2004 chinook salmon spawners. Data in this table was generated using a polyclonal antibody-based quantitative ELISA (Q-ELISA) performed on kidney tissues. Prevalence was determined by % of Q-ELISA positive samples of the total number of samples tested. Intensity was considered high if the antigen concentration 21; medium if the antigen concentration = 0.20-0.99; and Low if the antigen concentration = 0.10 to 0.19. 123 Fish Group Hinchenbrook Michigan Adapted Females Male Females Male 1. Kidneys 8| Gametes 10/60 15/60 40/59 45/60 "99mm (17%) (25%) (68%) (75%) 2. Kidneys + 8. 17/60 15/60 11/59 11/60 Gama” ' (28%) (25%) (19%) (18%) 3. Kidneys + 8. 32/60 25/60 6/59 1/60 $2,323,321? ’3'“ (53%) (42%) (10%) (2%) salmoninarum antigen level 4. Kidneys - 8. 1/60 5/60 1/59 2/60 3:133: :it“; "h my (2% ) (8%) (2%) (3%) Table 14. Renibacterium salmoninarum prevalence in Kidney and gametes of the 2004 coho salmon spawners (Shedding agreements possibilities between kidney and gametes). Data in this table was generated using a polyclonal antibody-based quantitative ELISA (Q-ELISA) performed on kidney tissues. Prevalence was determined by % of O-ELISA positive samples of the total number of samples tested. Intensity was considered high if the antigen concentration a; medium if the antigen concentration = 0.20-0.99; and Low if the antigen concentration = 0.10 to 0.19. 124 Gamete Donors Fingerlings tested 8 month following Fish e -take strain Year Renibacterium Year Hatchery Renibacterium salmoninarum salmoninarum prevalence prevalence Little 2001 81.7 % Total 2002 PR 62.0 % Total Manistee 43.3 % high 0.0 % high Chinook 8.3 % medium 0.0 % medium 30.0 % low 62.0% low WL 100.0 % Total 100.0 % high 0.0 % medium 0.0 % low 2002 63.5 % Total 2003 PR 100.0 % Total 0.0 % high 17.0 % high 6.3 % medium 8.0 % medium 57.1 % low) 75.0 % low) WL 92.0 % Total 0.0 % high 50.0 % medium 42.0 % low 2003 20.0 % Total 2004 PR 0.0 % Total 1.7 % high 0.0 % high 1.7 % medium 0.0 % medium 16.7 % low 0.0 % low) WL 35.0 % Total 2.0 % high 6.7 % medium 27.0 % low 2004 67.0 % Total 2005 PR 5.0 % Total 2.5 % high 0 % high 7.5 % medium 0 % medium 57.0 % low 5 % low) WL 10.0 % Total 0.0 % high 0.0 % medium 10.0 % low Table 15. Renibacterium salmoninarum infection prevalence and intensity among the Little Manistee River chinook salmon feral spawners and their corresponding hatchery raised fingerlings throughout the period from 2001 to 2005. Data in this table was generated using a polyclonal antibody-based quantitative ELISA (Q-ELISA) performed on kidney tissues. Prevalence was determined by % of Q-ELISA positive samples of the total number of samples tested. Intensity was considered high if the antigen concentration 21; 125 medium if the antigen concentration = 0.20-0.99; and Low if the antigen concentration = 0.10 to O. 1 9. Note: PR (Platte River State Fish HatcherY). WL (Wolf Lake State Fish Hatchery). TH (Thompson State Fish Hatchery). 126 Fish strain Gamete Donors Fingerlings tested 8 month following eggiake Year Renibacterium salmoninarum prevalence Year Hatchery Renibacterium salmoninarum prevalence Swan River Chinook 2002 45.7 % Total 5.0 % high 1.7 % medium 39.0 % low 2003 PR 92.0 % Total 0.0 % high 50.0 % medium 42.0 % low TH 0.0 % Total 0.0 % high 0.0 % medium 0.0 % low 2003 35.3 % Total 2.9 % high 0.0 % medium 32.3 % low 2004 PR 0 % Total 0.0 % high 0.0 % medium 0.0 % low WL 35.0 % Total 3.3 % high 0.0 % medium 31.7 % low TH 0.0 % Total 0.0 % high 0.0 % medium 0.0 % low 2004 13.7 % Total 4.1 % high 1.6 % medium 8.0 % low 2005 PR 8.3 % Total 0.0 % high 0.0 % medium 8.3 % low WL 10.0 % Total 0 % high 1.7 % medium 8.3 % low TH 2.0 % Total 0.0 % high 0.0 % medium 2.0 % low Table 16. Renibacterium salmoninarum infection prevalence and intensity among the Swan River Weir chinook salmon feral spawners and their corresponding hatchery raised fingerlings throughout the period from 2001 to 2005. Data in this table was generated using a polyclonal antibody-based quantitative ELISA (Ct-ELISA) performed on kidney tissues. Prevalence was determined by % of Q-ELISA positive samples of the total number of samples tested. Intensity was considered high if the antigen concentration a; 127 medium If the antigen concentration = 0.20-0.99; and Low if the antigen concentration = 0.10 to 0.19. Note: PR (Platte River State Fish Hatchery), WL (Wolf Lake State Fish Hatchery), TH (Thompson State Fish Hatchery). 128 Little Manistee River Weir 100%- 8 80%r I: % 60%- 5 E 40%- 20% ml D Low 2001 2002 2003 2004 I Medium I th 100%. Swan River Weir 80%- at O 5 50%- E 40°/ 0. E 20%. 0%. 2001 2002 2003 2004 Figure 7. Prevalence of Renibacterium salmoninarum in feral chinook salmon spawners collected from two of Michigan weirs between 2001 and 2005. Data in this Figure was generated using a polyclonal antibody—based quantitative ELISA (Q- ELISA) performed on kidney tissues. Prevalence was determined by % of Q-ELISA positive samples of the total number of samples tested. Intensity was considered high if the antigen concentration 21; medium if the antigen concentration = 0.20-0.99; and Low if the antigen concentration = 0.10 to 0.19. 129 Michigan Adapted Coho salmon 60% [3 Low 5”“ I Medium l I High Prevalence s :1 2001 2002 2003 2004 Hinchenbrook Coho salmon Prevalence 2001 2002 2003 2004 Figure 8. Renibacterium salmoninarum prevalences and intensities in feral spawner, coho salmon strains returning to Platte River Weir throughout 2001-2004 Data in this Figure was generated using a polyclonal antibody-based quantitative ELISA (Q- ELISA) performed on kidney tissues. Prevalence was determined by % of Q-ELISA positive samples of the total number of samples tested. Intensity was considered high if the antigen concentration 21; medium if the antigen concentration = 020-099; and Low if the antigen concentration = 0.10 to 0.19. 130 Little Manistee River Weir . , . 1 .. I ’7‘ ( a“ I 3’ A’s 436 '6’» 4”? 100 Prevalence qr D Low I Medium I I-Igh 100,, Swan River Weir Prevalence 20%1 1096a Figure 9. Prevalence of Renibacterium salmoninarum in feral chinook salmon spawner males and females collected from two of Michigan weirs between 2001 and 2005. Data in this Figure was generated using a polyclonal antibody-based quantitative ELISA (Q- ELISA) performed on kidney tissues. Prevalence was determined by % of Q-ELISA positive samples of the total number of samples tested. Intensity was considered high if the antigen concentration 21; medium if the antigen concentration = 0.20—0.99; and Low if the antigen concentration = 0.10 to 0.19. 131 Michigan Adapted Coho salmon Prevalence 56 Female-02 Male«02 Female-04 Male-04 I High I Medium El Low Hinchenbrook Coho salmon too» 90%4 80% 70% 80% 50% 40% 30%- 20% 10921 A. . - Prevalence 0]. 4 Female-02 Male-02 Female-04 Male-04 Figure 10. Renibacterium salmoninarum prevalence and intensity in females and males of coho salmon spawners returning to Platte River Weir throughout the period from 2002-2004. Data in this Figure was generated using a polyclonal antibody-based quantitative ELISA (Q- ELISA) performed on kidney tissues. Prevalence was determined by % of Q-ELISA positive samples of the total number of samples tested. Intensity was considered high if the antigen concentration 21; medium if the antigen concentration = 0.20-0.99; and Low If the antigen concentration = 0.10 to 0.19. 132 Michigan Adapted Coho salmon Prevalence [- High a Medium 1:) Low ] Hinchenbrook Coho salmon Prevalence s a! 0 A 0 '° 0 ‘° 4) 4) 4) “to.“ “2% “5% “a. “a “e e, 0.4, g, ‘4 “v, $0.4, Figure 1 1. Renibacterium salmoninarum prevalence and intensity of infection in gamete donor feral spawner coho salmon strains versus their corresponding 18-month juvenile fingerlings throughout 2001-2004. Data in this Figure was generated using a polyclonal antibody-based quantitative ELISA (Q- ELISA) performed on kidney tissues. Prevalence was determined by % of Q-ELISA positive samples of the total number of samples tested. Intensity was considered high if the antigen concentration 21; medium if the antigen concentration = 0.20-0.99; and Low if the antigen concentration = 0.10 to 0.19. 133 CHAPTER FIVE PREVALENCE, SHEDDING AND SPREAD OF RENIBACTERIUM SALMONINARUM IN BROOK TROUT (SAL VELINUS FONTINALIS) WITH SPECIAL EMPHASIS ON THE ASSOCIATED DISEASE EPIZOOTICS IN MICHIGAN. ABSTRACT In order to determine the status of BKD in hatchery and wild populations of brook trout in Michigan, (Renibacterium salmoninarum) R. salmoninarum prevalence and intensity were detennined in representative samples from adult hatchery raised and wild stocks as well as their offsprings from 2001 through 2005. The hatchery raised adult Iron River brook trout presented higher BKD prevalence than the wild Cherry Creek strain. Generally, the BKD prevalence and intensity in hatchery and wild brook trout strains gradually decreased throughout the period from 2001 to 2004. The critical role played by hatchery practices to control the spread and minimize the prevalence of BKD among Michigan brook trout populations was discussed. Although most of the previous studies reported an insignificant male role in transmission of Renibacterium salmoninarum (R. salmoninarum), yet our results clearly demonstrated that males shed along with their gametes more R. salmoninarum than females. Number of BKD outbreaks among hatchery-reared brook trout populations has increased dramatically throughout the period of late spring of 2003 to the 134 early fall of 2004. The affected brook trout populations have been assessed using various diagnostic tools, such as clinical examination, Q-ELISA, culture, histopathology, and immunohistochemistry. The possible causes that lead to the initiation and progression of such outbreaks have been fully investigated. Although Q-ELISA, nested PCR, and culture results for all of the examined cases were positive, some of these cases were either barely within detection limits or demonstrated negative results in histopathological and immunohistochemical examination. This result is not surprising, as some of the specimens were preserved in formalin for a relatively long period (i.e. enough to affect the IHC power) even after performing improved antigen retrieval methods. Also, representative samples of 3-year-old broodstock exhibiting chronic forms of the disease had meager amounts of antigen remaining within their system, with trace amounts being present in the antigen antibody complexes in granulomas that occupied large portions of the kidney tissues. These were sequentially presented as a very light antigen score using the IHC (1+). 135 INTRODUCTION Brook trout (Salvelinus fontinalis) is an indigenous salmonid species in the Great Lakes (Coon 1999) that has been artificially propagated and stocked in Michigan’s public waters for years (Dexter and O’Neal, 2004). Two strains of brook trout, the Assinica and Iron River strain, are being used by used by Michigan Department of Natural Resources (MDNR) for supplementing resident stream populations where there is a deficiency of natural recruitment (Dexter and O’Neal, 2004). Assinica and Iron River brook trout are the two main strains of brook trout that are being reared and stocked in Michigan. Assinica brook trout are characterized by better survival and growth than domestic stocks (Gowing 1986). Iron River Brook trout are considered a pure native strain that is originally from the Iron River in Michigan’s Upper Peninsula (Driver 1995). Unlike the Assinica strain, Iron River brook trout are slow to reach maturity and are characterized by a very slow growth rate because of their wild characteristics (Dexter and O’Neal 2004). Fish health poses major challenges to development and progress of the brook trout restoration in the Great Lakes basin. Among these health challenges, Bacterial Kidney Disease, caused by Renibacterium salmoninarum (R. salmoninarum), is an eminent threat due to the enzootic nature of the pathogen within Great Lakes waters (Eissa 2005-Chapter 3). Moreover, affinity of R. salmoninarum for the kidneys, which possesses an essential lymphoid function and its obligate intracellular nature, makes this pathogen and its soluble antigens 136 a major threat to the host by suppressing the fish immune system (Ellis 1999; Fredriksen et al. 1997; Grayson et al. 2002). A considerable number of studies have been performed on brook trout in the USA which indicated that brook trout is the most susceptible salmonid to BKD (Belding and Merrill 1935; Snieszko and Griffin 1955). However, most of these studies involved the use of experimental infection, while a relatively few were concerned with natural BKD infection (Allison et al. 1958; Mitchum et al. 1979; Mitchum and Sherman 1981). For example, Bullock et al. (1971 ); Mitchum and Sherman (1981) reported that brook trout mortalities from BKD are higher than that of the brown trout. Interestingly, the first report of BKD in the USA occurred in brook trout at a Massachusetts State fish hatchery (Belding and Merrill, 1935). During the late 19403 and early 19503, R. salmoninarum infection caused mass mortalities in brook trout at the federal hatcheries in Berlin, New Hampshire, Cortland, and New York (Snieszko and Griffin, 1955). Mitchum et al. (1979) determined the prevalence of BKD in dead and live brook trout collected from a small lake and stream system in southeastern Wyoming, USA, where BKD epizootics had been observed since 1972. They found that prevalence among dead fish and live fish at upstream stations was 100% and 83%, respectively. In Michigan, the first case of BKD was discovered in 1955 in brook trout yearlings at the Oden and Marquette state hatcheries, where eggs were originally imported from a hatchery in New England in which BKD had been endemic for many years (Allison, 1958). Since the first report of the disease in 1955, none of 137 the published studies have reported any data about the recent occurrence of BKD outbreaks, prevalence, or magnitude of the disease in brook trout in Michigan or in the Great Lakes basin. Thus, the aim of the current research was to investigate the status and magnitude of BKD in brook trout in Michigan by assessing the R. salmoninarum prevalence in the hatchery raised brook trout populations in Michigan. The role- played by the male and the shedding of the bacteria along the gamete are also investigated. Moreover, a number of recently erupted BKD outbreaks among brook trout populations in Michigan were also investigated. 138 MATERIALS AND METHODS Fish. To investigate the prevalence and intensity of R. salmoninarum infection among brook trout (BKT) populations in Michigan waters, a total of 628 adult brook trout were collected from the hatchery raceways of Marquette State fish hatchery (MSFH) and the Cherry Creek water stream outside the hatchery in Marquette, Michigan, from 2001-2004. MSFH is the primary facility for brook trout broodstock that are used for the production of fingerlings to be stocked in both inland and Great Lakes waters. Kidney tissue samples were collected from a total of 567 hatchery-raised brook trout broodstocks (529 Iron River strain (IR-BKT) sample, 38 Assinica strain (AS-BKT) sample) and 61 adult Cherry Creek wild brook trout (CC-BKT) (Table17). Following approximately 18 months of egg incubation and fish rearing in the Marquette State Fish Hatchery, MDNR releases fingerlings in the spring of each year. Between 2002-2005, a total of 420 kidney tissues of pre-stocking fingerlings were collected and analyzed for the presence of R. salmoninarum prior to release into the basins of Lakes Michigan (table 17). The sacrifice of broodstock was accomplished by exposing the fish to an overdose of MS-222 (tricaine methane sulfonate, Finquel- Argent Chemical Laboratories, Redmond, WA). Following gamete collection, the abdominal cavity was cut open to examine individual intemal organs for signs of BKD, followed by collecting about one gram of tissues from anterior, posterior and middle kidney 139 sections. Attention was given not to cross contaminate samples and dissecting tools were replaced with sterile ones following dissection of each fish. Fingerlings were sacrificed by immersion in an overdose of MS-222. In order to ensure that the sample is representative, as much tissue as possible was harvested from each kidney using sten'le dissection tools. A total of 200 coelomic fluid samples were collected using sterile transfer pipette from the egg/ovarian fluid mixture, transferred to 5 ml sterile polypropylene tubes, and kept on ice until processed at the laboratory at Michigan State University, East Lansing, MI. Also, a total of 200 semen samples were collected directly from the middle stream of semen into sterile 10-ml polypropylene tubes. Fingerlings were sacrificed by immersion in an overdose of anesthesia using MS-222 (tricaine methane sulfonate, Finquel- Ardent Chemical Laboratories, Washington). A number of BKD outbreaks of involving brook trout were recorded between 2003 and 2004. In late May of 2003, a total of 72 Iron River brook trout fingerlings with a recent history of mortalities were submitted to the Aquatic Animal Health Laboratory (AAHL) at Michigan State University from the Marquette State Fish Hatchery (MSFH) in Michigan. A course of treatment was prescribed and then followed by the collection of another 60 samples for post treatment analysis. In Mid July 2004, a total of 9 adult three year-old Assinica brook trout were submitted to the AAHL from the MSFH during an onset of broodstock losses. In Mid September of 2004, a total of 30 brook trout yearlings were submitted to the AAHL from Cedarbrook Fish Farm in Harn’sville, Michigan that were experiencing increased mortalities. 140 Clinical examination. Fish were euthanized using an overdose of MS 222 (tricaine methane sulfonate) (Finquel- Argent Chemical Laboratories, Washington). Fish were then externally examined for the presence of any lesions, parasites, or abnormal growths on the skin or gills. Fish were dissected and examined internally for any lesions, swelling, or color changes in the kidneys other internal organs and viscera. Sample processing. Kidney samples representing the anterior, posterior and middle sections of the kidney were transferred in sterile 7.5 cm x 18.5 cm Whirl Pak® bags (Nasco, Forte Atkinson, and WI), kept on ice, and were softened as much as possible through multiple cycles of physical pressure. The homogenized kidney tissues were diluted in 1:4 (w/v) Hank’s Balanced Salt Solution (HBSS, Sigma Chemical Co, St. Louis, MO) then stomached for 2 minutes at high-speed in a Biomaster Stomacher-80 (Wolf Laboratories Limited, Pocklington, York, UK). In the case of ovarian fluid, 1 ml from fluid sample was diluted 1:2 (v/v) in HBSS for Q-ELISA testing. In the case of milt samples, 1ml from each semen sample was diluted 1:2 (v/v) in HBSS for Q-ELISA testing. Measurements of Renibacterium salmoninarum antigen using the Quantitative Enzyme-linked Immunosorbent Assay (Q-ELISA). Aliquots of 250 pl volume of each samples were transferred into 1.5 ml safe-lock microfuge tube to which an equal volume of 0.01 M phosphate buffered saline-Tween 20 141 (0.05 %) (PBS-T20) (Sigma) with 5 % natural goat serum (Sigma) (Olea et al., 1993) and 50 pl CitriSolv solution (Fisher Chemicals, Fairlawn, New Jersey) (Gudmunsdottir et al., 1993) were added. The mixture were thoroughly mixed by vortexing then incubated at 100 °C on heat blocks with rotary shaker for 15 minutes and followed by 2 hours of incubation at 4 °C. After incubation, the mixture was centrifuged at 60009 for 15 minutes at 4 °C. The aqueous supernatant of each sample was carefully collected and then transferred to a 1.5 ml microfuge tube for Q-ELISA testing. The Q-ELISA method used in this study is that described in details by Pascho and Mulcahy (1987) and Alcorn and Pascho (2000). The positive negative threshold absorbances are calculated according to the method described by Meyers et al. (1993) .The positive-negative cutoff absorbance for the kidney homogenate was 0.10. The tested positive samples were assigned the following antigen level categories: low (0.10 to 0.19), medium (0.20-0.99) and high (1.000 or more) (Pascho et al., 1998). Intensity of infection among certain group of fish is expressed by percent of fish with high titers of R. salmoninarum soluble antigens using Q-ELISA. Nested PCR. _A DNeasy tissue extraction kit (Qiagen-Valencia, CA, USA) was used for the extraction of DNA from 100pl aliquots of kidney tissue homogenates. The DNA was extracted according to the manufacturer's instructions, with a few minor modifications from the method described by Pascho et al. (1998). The tissue pellets were obtained by centrifugation at 6000 g for 20 minutes at 4 °C and the pellets were incubated with lysozyme buffer 142 consisting of 180 pl of 20 mg lysozyme (Sigma), 20mM Tris-HCI, pH 8.0; 2 mM EDTA (Sigma) and 1.2 % (v/v) Triton X 100 (Sigma) at 37 °C for 1 hour. The nPCR method and primers recommended by Pascho et al. (1998) were employed with slight modifications to the volume of DNA (5 pl for first round and 2 pl for second round PCR reaction), water, and master mixes (45 pl for first round and 48 pl for second round nPCR reaction) .The controls were composed of a PCR mixture containing no DNA template reagent (negative control), positive R. salmoninarum and positive tissue control. A volume of 10 pl of the nPCR product and controls were mixed with 2 pl of 6X loading dye (Sigma) and used on a 2 % agarose gel (Invitrogen Life Technologies, Carlsbad, CA). Each electrophoresis gel included a 1kbp DNA ladder with 100 bp increments (Invitrogen). Gels were run in 1 X Tris Acetate Buffer (1 X TAE) gel buffer (Sigma). Gels were visualized under the KODAK EDAS Camera System and UV Trans-illuminator. Samples were considered positive when a 320 bp band was detected. Molecular confirmation of the purified bacterial isolates was also conducted using nPCR according to the method described by Chase and Pascho (1998). Histopathology. Kidney tissues fixed in 10 % neutral buffered formalin solution were processed and embedded in paraffin. Five-micron sections were routinely stained with Hematoxylin and Eosin (HE) using the method previously described by Prophet et al. (1992). Slides were evaluated and given a score of 0, +1 , +2, or +3 based on degree of pathological alterations. 143 lmmunohistochemistry (IHC). The methods used in the IHC were adopted from Jansson et al. (1991) and Evensen et al. (1994). In brief, tissue sections of kidney from BKT with clinical signs were used for immunohistochemical evaluation of the expression R. salmoninarum soluble antigens. IHC staining was performed on automated immuno-stainers. Paraffin embedded tissues that had been fixed in formalin for less than 48 hours were deparaffinized in xylene, rehydrated in graded ethanol, and rinsed in distilled water. Endogenous peroxidases were neutralized with 3% hydrogen peroxide for 5 minutes. Antigen retrieval was achieved by incubating slides in a citric buffer antigen retrieval solution in a steamer (Black 8. Decker, Towson, MD) for 20 min, and non-specific immunoglobulin binding was blocked by incubation of slides for 10 min with a protein-blocking agent (Dako, Carpinteria, CA). Using the Dako autostainer (Dako, Carpenteria, CA), slides were incubated for 30 minutes with a goat anti- Renibacterium salmoninarum antibody (Kirkegaard & Perry Laboratories) at a dilution of 1:100. A streptavidin-lmmunoperoxidase staining procedure (Dako, Carpinteria, CA) was used for immunolabeling. The immunoreaction was visualized with ABC (Dako, Carpinteria, CA). Sections were counterstained with Mayer’s hematoxylin. Tissues that had been fixed in formalin for more than a year were immunostained using the protocol described above as well as the following method to enhance antigen retrieval. In this particular protocol deparaffinization, antigen retrieval, and immunostaining of formalin-fixed paraffin embedded tissues were performed on the Bench Mark Automated Staining I44 System (Ventana Medical Systems, Inc.) using the Enhanced V-Red Detection (Alk. Phos. Red) Detection System (Ventana Medical Systems, Inc.) and a goat anti-Renibacterium salmoninarum antibody (Kirkegaard & Perry Laboratories) at a dilution of 1:100. Antigen retrieval was achieved using the Ventana Medical Systems Retrieval Solution CC1 (Ventana Medical Systems) for 60 min followed by digestion with and Protease 3 for 4min (Ventana Medical Systems). Sections were counterstained with haematoxylin. Positive IHC controls included a kidney from a trout with strong Renibacterium salmoninarum soluble antigens expression to which the appropriate antisera were added. For negative controls the primary antibodies were replaced with homologous non-immune sera. Statistical Analysis. Because of the nature of data collected in this chapter required basic statistical description, data analysis was primarily relied on descriptive statistics. For year to year and brook trout strains comparisons, the data was tested for normality and then student t test (parametric) or Mann- Whitney Rank Sum Test was (with an alpha level = 0.05). 145 RESULTS A. Prevalence of R. salmoninarum infection in captive and wild brook trout stocks. Renibacterium salmoninarum antigens were detected in the kidneys of Marquette State Fish Hatchery captive broodstock and fingerlings as well as Cherry Creek brook trout. The prevalence of R. salmoninarum in the Iron River broodstock exhibited a steady decline from 87% in 2001, to 80% in 2002, to 60% in 2003, and to 43% in 2004. Similarly, the intensity of R. salmoninarum in the Iron River brook trout (expressed by the percent of fish showing high titer of R. salmoninarum antigen) exhibited a comparable decline. The percent of fish with high R. salmoninarum antigen levels decreased from 17% in 2001 to 7.5% in 2004 (Figure 12). Assinica brook trout Broodstock (BS AS-BKT) were tested only in 2003 and 2004. The results demonstrated a decrease in prevalence from 80 % in 2003 to 25% in 2004 (table 18). However, the intensity of the R. salmoninarum infection in the BS AS-BKT did not exhibit a similar decline. In the case of Cherry Creek brook trout (CC-BKT), samples were collected in the falls of 2001-2004. Prevalence of R. salmoninarum in CC-BKT decreased from 80% in 2001 to 67% in 2003. The intensity of R. salmoninarum showed no consistent pattern (table 18). The prevalence of R. salmoninarum in lR-BKT fingerlings between 2003 and 2005 were comparable to the parents and consistent with the high prevalence in 146 the gamete donor broodstock, although 2004 showed a significantly low prevalence. However, the intensity of R. salmoninarum antigens in BKT fingerlings was higher than those detected in their parents during 2003 (48% vs 17% in their parents) before sharply declining in subsequent years (table 18). The prevalence of R. salmoninarum in 2005-AS-BKT fingerlings was lower (28%) than those of their parent BS AS-BKT-2003. Similarly, the prevalence of R. salmoninarum in 2005-AS-BKT fingerlings was much lower than that of the 2005- IR-BKT fingerlings (28% vs 45% in lR-BKT fingerlings). The intensity of the R. salmoninarum infection in the AS-BKT fingerlings showed a decline, which was similar to the prevalence through the time of testing. To compare the prevalence and intensity of R. salmoninarum in males and females BKT, two hundred pairs of lR-BKT broodstock were tested in 2004. Results indicated that the prevalence of R. salmoninarum infection was higher in the kidney tissue of the females than males (48.5% in females vs 37.5% in males). Similarly, the intensity of R. salmoninarum infection was clearly higher in the females (11% in female vs. 4 % in male). The shedding of the bacterial antigen along with the gametes was tested in broodstock IR-BKT in 2004. Data shown in Figure (13) illustrated that R. salmoninarum antigen shed with the gametes in both males and females IR—BKT. The prevalence of individuals that shed the bacterial antigen along with the gametes is lower in males than in females (10% in milt vs 15% in ovarian fluid). Also, the intensity of samples with high R. salmoninarum antigen was much higher in females (2.5%) than in males (0.5%). The majority of the females (20 out of 30) that shed the antigen in their 147 ovarian fluids exhibited similar levels of R. salmoninarum antigens in their kidneys. However, 9 females shed the R. salmoninarum antigen along with the ovarian fluid without detecting R. salmoninarum antigen in the kidneys and one female shed the antigen at a low level in the ovarian fluid and tested negative for the kidney tissue. Likewise, the majority of male shedders (13 out of 20) had similar levels of R. salmoninarum in their kidneys with only 7 fish shed the antigen without detected titer of R. salmoninarum antigen in the kidney. 8. BKD outbreaks among hatchery-raised brook trout. A number of BKD outbreaks erupted among hatchery-raised brook trout during 2003 and 2004: 1. Iron River Brook trout. A major BKD outbreak has been observed in May, 2003. In this outbreak mortalities reached up to 50%. Externally, all fish submitted for clinical examination had heavy infestations of skin monogenean trematodes, sessile ciliates and Trichodina spp. lntemally, the majority of fish exhibited typical signs of BKD, such as enlarged kidneys with whitish gray discoloration and the presence of multiple creamy-whitish nodules scattered throughout the kidney tissues (Figure. 14). Kidney samples were tested for R. salmoninarum using the nPCR, Q-ELISA and culture. Results indicated that R. salmoninarum was present in all samples using each of the three techniques. All tested fish had high concentration of R. salmoninarum antigens in the kidney tissue by Q-ELISA. Examination of the histopathological slides of affected kidneys revealed the presence of typical granulomatous reactions with a necrotic 148 center that was surrounded by a fibrous capsule, with a mixture of epithelioid macrophages, lymphocytes, and frequent giant cells. Gram-positive coccobacilli were observed within the necrotic tissue as well as other layers of the granuloma. When immunohistochemical (IHC) procedures were performed on the paraffin- waxed kidney sections, high positive results (scored 3+) where bacterial cells taking the dark red IHC staining were heavily distributed within the blue background of the kidney tissues (Figure 15 & 16). The Iron River brook trout fingerlings in the hatchery raceways were treated with 2.25% Aquamycin-100 in food. The fish were fed Erythromycin between 75 and 150 mg/kg of fish weight to comply with lnvestigational New Animal Drug (INAD) specifications and mortalities gradually decreased until subsiding completely at the completion of treatment. In early June of 2003, a total number of 60 erythromycin treated IR-BKT fingerlings were further examined post treatment. Results showed 4 of 60 fish (6.7 %) still had clinical BKD lesions. Kidneys of the examined fish were tested for the presence of R. salmoninarum antigens using Q-ELISA. Results indicated that R. salmoninarum antigens had sharply declined to 18.3 %, with only 5 % demonstrating the high titer of the antigens. Culture from post treatment fish showed that only 4 out of 60 fish (6.7 %) were positive. 2. Assinica Brook trout. In mid July of 2004, mortalities in the 3 year old Assinica brook trout stocks in MSFH continued for a month before representative samples were submitted for investigation. Random samples from fish in affected raceways were externally examined, where skin scraping revealed heavy infestations with monogenean (Gyrodacty/us sp.). A total of 9 clinically affected 149 fish were examined, where 7 out of 9 fish (77.8 %) exhibited heavy monogenetic trematodes, sessile ciliates and fungal hyphae. lntemally, 5 out 9 fish (55.6 %) exhibited grayish discoloration of the kidneys, with the presence of white abscess-like nodules scattered throughout the kidneys. Kidney samples from the 9 fish were further tested using nPCR, Q-ELISA and culture. All samples were positive when tested using nPCR, while a total number of 7 out of 9 (77.8 %) fish were culture positive and 3 out of 9 fish (33.3 %) were Q- ELISA positive (1 high, 1 medium, 1 low). When submitted for histopathology, 75 % of the kidney samples exhibited moderate muItI-focal granulomatous reactions (scored 1+) and 25 % exhibited severe multi-focal granulomatous reactions (Scored 3+) (Figure 18). The reactions were characterized by the presence of typical granulomas, accompanied by a mixture of epithelioid macrophages, lymphocytes and occasional giant cells. Interestingly, the granulomatous reaction replaced 50-60 % of the renal parenchyma (Figure 18). Centrally, the lesion was composed of eosinophilic, caseous debris, surrounded by marked sheets, nests, and laminated foci of epithelioid macrophages mixed with lymphocytes. The periphery of the lesion was surrounded by mature fibrous connective tissue associated with more destruction of the renal parenchyma (Figure 17). Despite the fact that most of the samples showed the presence of typical granulomatous inflammation with varying severity (1+ to 3+ scores), the results of the IHC technique performed on the paraffin-waxed lesions were negative (Figure 18). The only sample with a typical granulomatous reaction exhibited very few bacterial cells when the 150 antigen retrieval technique was performed on the paraffin embedded blocks of the same samples (Figure 19). 3. Private Brook Trout Farm. In Mid September of 2004, mass mortalities occurred in the brook trout yearlings of a private Brook Trout Farm. Mortalities continued for two weeks. External parasitological examination of fish gills and skin revealed the presence of large numbers of monogenean trematodes and sessile ciliates. lntemally, 12 of 30 fish (40 %) showed pale gray, whitish discolorations and swelling of the kidneys, with multiple abscess-like nodules scattered all over the kidneys. Typical colonies of R. salmoninarum were observed after 2 weeks on MKDM from a total of 18 out of 30 fish (60 %), which was later confirmed with nPCR. Q-ELISA showed that 18 out of 30 fish (60%) were positive for R. salmoninarum antigens, with an intensity of 67% (expressed by percent of fish with high titers of R. salmoninarum soluble antigens using Q- ELISA). 151 DISCUSSION For decades, brook trout has been known for its high susceptibility to R. salmoninarum infection (Snieszko and Griffin 1955; Mitchum and Sherman 1981). Brook trout infected with R. salmoninarum either naturally or experimentally, suffer from high mortalities (Belding and Merrill 1935; Snieszko and Griffin 1955; Mitchum et al. 1979). Data obtained in this study demonstrated a high prevalence and intensity of R. salmoninarum infection in both hatchery raised and wild stocks. This concurs with previous reports. For example, Mitchum and Sherman, 1981, recorded a relatively high prevalence and severity of R. salmoninarum infection in wild and hatchery raised brook trout populations (58 %, 45 % respectively). A general trend of declining prevalence and intensity of R. salmoninarum in IR-BKT broodstock was observed over the period of this study. This trend might be explained by the improvement of hatchery hygienic practices. Among these practices are the prophylactic erythromycin phosphate administration and hardening of eggs in erythromycin containing water. Evelyn et al. 1986 and Lee and Evelyn (1989) found that intramuscular injection of broodstock with erythromycin phosphate dramatically minimized the vertical transmission of R. salmoninarum. Also, Rinsing of broodstock in iodophores solution before collecting gametes could minimize the R. salmoninarum on the eggshell (Ross and Smith 1972). Maule et al. (1996) 152 described similar observations that lead to remarkable decrease of R. salmoninarum prevalence among other salmonid species. Although the Assinica strain demonstrated inconsistent R. salmoninarum infection prevalence when compared to the Iron River, yet Iron River strain showed higher intensity than Assinica strain. The Assinica strain is known for its superior survival and growth (Gowing 1986), and these characteristics could play a vital role in the general defense of the fish against severe infections with R. salmoninarum. In addition, variable susceptibility of fish strains to different diseases is not unusual. For example, some strains of steelhead showed variable susceptibility to R. salmoninarum (Winter et al., 1 980). Wild populations of BKT (CC-BKT) showed a comparable prevalence to that of the hatchery reared BKT. The fact that Cherry Creek supplies the hatchery with water and that BKT exists in this water may explain the similarity in infection levels. Analysis of the data of R. salmoninarum prevalence and intensity of infection among the Iron River brook trout pre-stocking fingerlings indicated that fingerlings from 2003 exhibited the highest prevalence and infection intensity (approaching 100 %). The 2003 pre-stocking fingerlings are the offspring of the 2001 Iron River brook trout parent stocks that also exhibited high BKD prevalence (83 %). Vertical transmission have probably played a major role in this high incidence of infection, particularly that erythromycin prophylactic administration was not implemented in 2001. On the contrary, 153 the 2004-2005 Iron River and Assinica brook trout offspring showed relatively lower R. salmoninarum prevalence and intensity, although they originally hatched from fertilized eggs collected from 2002-2003 parents with relatively high R. salmoninarum prevalence and intensity. This could only be explained by the strict hygienic measures adopted by the hatchery starting from 2002. Data obtained from the Q-ELISA testing of gametes indicated that the R. salmoninarum was shed with the gametes in both males and females (10% in males versus 15% in females), with a higher intensity in females than males. These results suggest a contribution of the male in the vertical transmission of R. salmoninarum to the offspring, in addition to the role played by females. Allison (1955) was the first to report vertical transmission in the brook trout, albeit with circumstantial evidence that gametes from infected adults resulted in infected offspring. Our data agreed with Wiens and Kaattari (1989), which were able to detect the R. salmoninarum antigens in the milt of infected males. However, the studies of Klontz (1983) and Evelyn, et al. (1986) demonstrated that males play an insignificant role in the vertical transmission of R. salmoninarum. However, the data may be complicated by discrepancies between levels of R. salmoninarum in the ovarian fluid and their levels in the kidney of corresponding individual fish. BKD outbreaks were associated with severe clinical signs and high mortalities in BKT in Michigan. The frequent occurrence of BKD epizootics in hatchery raised brook trout populations during 2003 and 2004 without affecting other salmonids, such as the lake trout residing in the same 154 hatchery, presumptively indicates that brook trout has higher susceptibility to R. salmoninarum infection when compared to other char and trout species. Although brook trout (Salvelinus fontinalis) are known for their high susceptibility to R. salmoninarum infection (Snieszko and Griffin 1955; Mitchum and Sherman, 1981), reports of the disease in this species were scarce in Michigan. Data indicated that the clinical picture and the magnitude of the mortalities described in the current study coincide with previous reports about BKD-associated epizootics in brook trout in the United States (Belding and Merrill 1935; Snieszko and Griffin 1955; Mitchum et al. 1979). Outbreaks described in the current study were frequently coupled with external parasitic infestations. It is not clear whether the external parasitic infestation initiated or resulted from the BKD outbreaks. However, it seems that many factors were involved in influencing mortalities associated with the outbreaks. First, the rise in water temperature, along with the heavy density in the hatchery raceways, favors the external parasites (Mo 1997; Rintamaki and Voltonen 1994). Heavy external parasitic infestations open portals of entry within the skin and gills of fish and facilitate the horizontal transmission of the R. salmoninarum in water via the skin and gills. It is well documented that the bacteria can survive in water and feces for up to 21 days (Austin and Rodger 19803; Balfry et al. 1996). Also, a number of authors have hypothesized that water and feces indirectly act as reservoir for the transmission of R. salmoninarum from infected fish to other fish (Bullock 1975; Mitchum and Sherman 1981). Alternatively, the gradual increase of 155 water temperature during the time of the outbreaks was assumed by some authors to initiate the progression of BKD infection (Belding and Merrill 1935; Snieszko and Griffin 1955; Smith 1964; Sanders et al. 1978). The sequence of BKD infections is usually associated with the production of R. salmoninarum soluble antigens, which are known to suppress the immune response of infected fish (Fredriksen et al. 1997; Turaga et al. 1987; Wiens and Kaattari 1991, Ellis 1999), which drive the host to become vulnerable to infection with other bacteria and parasites. The development of the disease in the 2003-2004 outbreaks was documented using both histopathology and IHC. Examination of kidney sections stained with H&E indicated the presence of severe granulomatous reactions, with typical granuloma components where the organism could be detected both intra-cellularly and extra-cellularly using the Gram stain. Previous records of histopathology support these pathologic pictures of the kidney lesions during both experimental and natural BKD infections (Wood and Yasutake 1956; Young and Chapman 1978; Bruno 1986; Sami et al. 1992). In case of the Iron River BKT mortalities, IHC stained slides indicated the presence of an intense distribution of bacterial cells and their antigens within the kidney tissues, as well as within the granulomas, which confirms the assumption that the severe progression of the disease is associated with high bacterial metabolic activities (Evenden et al.1993, Bruno 1986, Sami et al.1992). Similar findings were reached by Hoffman et al. (1989); Jansson et al. (1991); Evensen et al. (1994) and Lorenzen et al. (1996). 156 Some discrepancies were observed between histopathological findings (positive with different scores) and IHC results (negative results of some of positive histopathological section). The histopathological findings ranged from mild multi-focal histiocytic inflammation (scored 1+), which appeared negative using the IHC stains to severe granulomatous reaction replacing more than 60 % of the kidney parenchyma (scored 3+). These kidney sections were negative when tested using regular IHC procedures and turned into very mild positive after improved antigen retrieval procedures were performed. Histopathological and IHC findings confirm the assumptions that the milder irritation over longer period of time might resulted in typical granuloma in one case, mild inflammation in others and negative results in the rest. The Assinica BKT kidney samples were preserved in buffered formalin solution for more than 1 year which is reported to be crucial factor in reducing the sensitivity of IHC techniques for many antigens and epitopes (Sompuram et al., 2004). This long time preservation in buffered formalin solution could resulted in denaturation of the soluble antigens (p57 protein) and formation of Methylene bridges, both inter- and intra-molecularly which will ultimately alter the physical characteristics of the kidney tissues and also induces masking of the antigens (p57) (Evensen et al., 1994). These deleterious effects of formalin might be a good cause for the inability to detect the bacterial cells within the affected kidney tissues using IHC, although they were positive with other techniques like Q-ELISA, culture, and nPCR. An enzymatic digestion and heat treatment methods (antigen retrieval methods) (Evensen et al., 157 1994) were used intensively to retrieve the masked antigens from the IHC processed tissues. Unfortunately the antigen retrieval methods were only able to retrieve extremely few R. salmoninarum soluble antigens within a typical granulomatous reaction of kidney tissue. One important disadvantage of the antigen retrieval method using heat treatment is the unexpected dissociation of the major soluble antigen (p57), which is known to be heat labile (Evensen et al.1994). In conclusion, this study supports the previous reports, which emphasized that brook trout are highly susceptible to R. salmoninarum infection. In addition, this study shed the light on the possible contribution of a number of factors to development of BKD epizootics in Michigan hatcheries, such as the seasonal changes and the presence of external parasites. Further, the possible role of males and females in shedding the bacterium and its soluble antigens was fully discussed. 158 Brook trout strain and life Date Collected Number of stage fish tested Iron River broodstocks October, 2001 54 October, 2002 45 October, 2003 30 October, 2004 400 Assinica broodstocks October, 2003 30 October, 2004 8 Iron River 18 month old pre- March, 2002 60 stocking fingerlings March, 2003 60 March, 2004 60 March, 2005 60 Assinica 18 month old pre- March, 2003 60 SIOCRIHQ fl“99'“"95 March, 2004 60 March, 2005 60 Table 17. Details of samples collected from brook trout broodstocks throughout the period from 2001-2004 and pro-stocking 18-month-old fingerlings collected throughout the period from 2002-2005. 159 Parent stocks (Gamete 18 months old pre-stocking Strain donorSI finge_rli_ngs Year Renibacterium Year Renibacterium salmoninarum salmoninarum prevalence prevalence Iron 2001 87.0 % Total 2003 98.0 % Total River 16.7% high 48.0 % high 50.0 % medium 35.4 % medium 20.4% low 14.6 % low Iron 2002 80.0 % Total 2004 20.0 % Total River 15.55 % high 0.0 % high 13.3 % medium 10.0 % medium 51.1 % low 10.0 % low Iron 2003 60.0 % Total 2005 45.0 % Total River 10.0 % high 0.0 % high 0.0 % medium 12.5 % medium 50.0 % low 32.5 % low Assinica 2003 80.0 % Total 2005 27.5 % Total 0.0 % high 0.0 % high 10.0 % medium 2.5 % medium 70.0 % low 25.0 % low Table18. Renibacterium salmoninarum infection prevalence and intensity among brook trout broodstocks and their corresponding 18 months pro-stocking fingerlings throughout the period from 2001 - 2005. Data In this table was generated using a polyclonal antibody-based quantitative ELISA (Q-ELISA) performed on kidney tissues. Prevalence was determined by % of Q-ELISA positive samples of the total number of samples tested. Intensity was considered high if the antigen concentration 21; medium if the antigen concentration = 0.20-0.99; and Low if the antigen concentration = 0.10 to 0.19. 160 Iron River Brook trout IR-BKT-01 IR-BKT-02 IR-BKT-03 IR-BKT-IM ‘°°°"‘ Cherry Creek Brook trout 9070‘ 8070‘ 70%- 60%- 8 50% ,5; 40%- .,>, 30% OL- 20% 10%) CC-BKT-M CC-BKT-02 CC-BKT-03 Figure 12. Prevalence and intensity of Renibacterium salmoninarum among the adult brook trout collected through 2001-2003 Data in this Figure was generated using a polyclonal antibody-based quantitative ELISA (Q-ELISA) performed on kidney tissues. Prevalence was determined by % of Q-ELISA positive samples of the total number of samples tested. Intensity was considered high if the antigen concentration a; medium if the antigen concentration = 0.20-0.99; and Low if the antigen concentration = 0.10 to 0.19. lR-BKT: Iron River Brook trout CC-BKT: Cherry Creek Brook trout This figure Is In color 161 I High I Medium I Low 100% - 90% a 80%: 70%* 60% ‘ 50% - 40% ‘ 30% 1 20%: 1 0%‘ 0% ‘ Prevalence Figure 13. Renibacterium salmoninarum Prevalence and intensity in kidneys and gametes of the Iron River brook trout broodstock in from Marquette State Fish Hatchery. Samples were collected during the fall spawning season of 2004. Data in this Figure was generated using a polyclonal antibody-based quantitative ELISA (Q-ELISA) performed on kidney tissues. Prevalence was determined by % of Q-ELISA positive samples of the total number of samples tested. Intensity was considered high if the antigen concentration 21; medium if the antigen concentration = 020-099; and Low if the antigen concentration = 0.10 to 0.19. This Figure is in color 162 Figure 14. An Iron River Brook trout fingerling with Bacterial Kidney Disease. The kidney is swollen with multiple creamy- whitish nodules (N). The above case is from an outbreak of Bacterial Kidney Disease that killed thousands of hatchery raised Iron River brook trout fingerlings in May 2003. This Flgure Is in Color 163 Figure15. Kidney tissue of Iron River brook trout fingerling exhibiting heavy Renibacterium salmoninarum infection. Kidney section was stained using an anti-Renibacterium salmoninarum antibody based streptavidin -immunoperoxidase immmunolbeling (Magnification 400). Sections were counterstained with Mayer’s hematoxylin (Blue background) Rs: Renibacterium salmoninarum soluble antigens with the red staining affinity. Tu: Non-affected kidney tubules with blue counterstaining affinity. This figure is in color 164 Figure 16. Kidney tissue of Iron River brook trout fingerling exhibiting heavy Renibacterium salmoninarum infection after enhanced antigen retrieval procedures using Alkaline Phosphatase Red and goat anti- Renibacterium salmoninarum antibody. Sections were counterstained with Mayer’s Hematoxylin (Blue background) (Magnification 400). This case is from an outbreak of BKD that killed thousands of hatchery raised Iron River brook trout fingerlings in May 2003. Rs: Renibacterium salmoninarum soluble antigens with the red staining affinity. Tu: Non-affected kidney tubules with blue counterstaining affinity. The marked increase in dark red dots (retrieved bacteria) distribution within the kidney tissue after the antigen retrieval compared to the picture in figure 16. This figure is in color 165 Figure 17. Hematoxylin and Eosin stained slide of kidney showing a severe granulomatous reaction that is replacing kidney tissues of a 3 years old Assinica brook trout. Notice the fibrous capsule (FC) surrounding the entire granuloma (Magnification 100). The case is from an outbreak of BKD that killed captive 3 years old Assinica brook trout in mid September 2003. This figure is In color 166 is C. . . ‘0 .. _ ‘3 ,9 'I .‘c i I &. v.‘ u ‘. ' O. ‘t . 4. re A. ' " ' ‘~ . . , . . _ I . v _ ‘ ~ - ‘ ‘ e -,f- . . , . . v u ' . -. <. . . . . , . : . . ‘ a : g . ’o’ I t ‘ ‘ I. l . . .. .' ,._ M, .. L;"\J:‘.*16:'.r \ 52‘s ’2" #0:. 5“. Figure 18. An ' L' ‘ L ' ' stained Kidney tissue section ( I .' If. .32. Cot ~‘ 3‘ i p as , s I 3t o‘- : ‘h I i", \ v ‘O. with chronic multi-focal granulomatous reaction from a 3 years old Assinica brook trout with absence of bacterial cells or antigen from the affected kidney tissues. Kidney section was stained using an anti- Renibacterium salmoninarum antibody based streptavidin - Immunoperoxidase immmunolbeling (Magnification 400). Sections were counterstained with Mayer’s hematoxylin (Blue background). The case is from an outbreak of BKD that killed captive 3 years old Assinica brook trout in mid September 2003. This figure Is in color Figure 19. An ' h' ‘ h ' ' stained Kidney tissue section with chronic multi-focal granulomatous reaction from a 3 years old Assinica brook trout exhibiting a mild chronic presence of bacterial cells or antigens after enhanced antigen retrieval procedures using Alkaline Phosphatase Red and goat anti-Renibacterium salmoninarum antibody. Sections were counterstained with Mayer’s Hematoxylin (Blue background) (Magnification 400). Rs: Renibacterium salmoninarum soluble antigens with the red staining affinity. This figure is in color 168 CHAPTER SIX FIRST RECORD OF RENIBACTERIUM SALMONINARUM IN SEA LAMPREY (PETROMYZON MARINUS) FROM THE GREAT LAKES BASIN ABSTRACT Bacterial Kidney Disease (BKD), caused by Renibacterium salmoninarum (R. salmoninarum), is a widespread problem with major implications for salmonid fish. The mechanisms by which the bacteria have reached high levels of infection previously unrecorded in the Laurentian Great Lakes are presently unknown. Research involving reservoirs and mechanisms of R. salmoninarum transmission in fish is lacking due to the ecological complexity of heterogeneous habitats and the lack of adequate funding. Surprisingly, we isolated R. salmoninarum from the kidneys of the sea lamprey (Petromyzon mar/nus). The bacterium was cultured from kidneys of 16% and 4% of Lake Ontario lampreys examined in 2003 and 2004 respectively, with bacterial colonies verified via nested polymerase chain reaction (nPCR) and quantitative enzyme linked immunosorbent assay (Q-ELISA). 169 INTRODUCTION Bacterial Kidney Disease (BKD), caused by Renibacterium salmoninarum, (R. salmoninarum) is a serious bacterial disease of salmonines (Fryer and Sanders, 1981) that is widespread in the Great Lakes basin (Hnath and Faisal 2005). Many facts pertaining to disease transmission and reservoirs of infection are currently unknown. The majority of studies conducted thus far suggest that R. salmoninarum exclusively infect salmonids and that carrier fish are responsible for its distribution (Wood and Yasutake 1956; Klontz 1983; Bullock and Herman 1988). However a few studies have indicated that non-salmonid fish species such as Pacific hake (Merluccius productus, Kent et al. 1998) and Pacific herring (Clupea harengus pallasi, Paclibare et al. 1988) may harbor the pathogen. In addition, certain fish, species such as Pacific herring (Traxler and Bell 1988), Sablefish (Anoplopoma fumbria) (Bell et al. 1990), common shiners (Notropis comutus) (Hicks et al. 1986) and fathead minnows (Pimephales promelas) (Hicks et al. 1986) contracted the infection when exposed to R. salmoninarum via intraperitoneal injection. The role that non-salmonid species may play in the spread of BKD has not been investigated in the Great Lakes basin. In the Great Lakes basin, a number of non-indigenous species have invaded the system and caused serious ecologic and economic losses (Lupi 170 and Hoehn 1998). Among these invasive species, is the sea lamprey (Petromyzon marinus), which has been one of the most destructive of the introduced species. The sea lamprey has been incriminated as a major factor contributing to the collapse of the lake trout (Salvelinus namaycush) and the lake whitefish (Coregonus c/upeaformis) fisheries in the Great Lakes during the 19403 and 19503 from which these two fisheries have yet to fully recover despite the advent of sea lamprey chemical control since 1958 (Smith and Tibbles 1980). To further reduce the number of sea lamprey and limit its spread, the Great Lakes Fishery Commission began a large-scale experimental program based on trapping male sea lamprey, sterilizing them, and subsequently releasing the sterile males back into streams where they compete with fertile males for spawning females. Field assessments indicated a decreased hatch rate in streams where this strategy was practiced. Up to 40,000 sterilized sea lamprey are released annually, yielding major success in the areas of implementation, such as the St. Marys River. Currently, males are collected from different areas in the Great Lakes basin, transported into a sterilizing facility in Hammond Bay, Michigan, and then released into selected river systems basin-wide. These transfers of lamprey to different locations may additionally transfer various pathogens concurrently, the probability of which has raised major concerns regarding the possibility of resident fish populations becoming infected. 171 To this end, this current study was initiated to determine if the sea lamprey could be a new host range for R. salmoninarum infection and the possible vector role that may contribute to the spread of Renibacterium salmoninarum. 172 MATERIALS AND METHODS Sea Lamprey (Petromyzon marinas). In the midsummer of 2003, 25 adult sea lamprey were moved from the Humber River and Duffins Creek, Lake Ontario, and presented alive to the Aquatic Animal Health Laboratory (AAHL) at Michigan State University to undergo fish health inspection and thereby ascertain their suitability for transfer to the lamprey sterilizing facility at Hammond Bay, then into the St. Mary’s River, both within the Lake Huron watershed. In midsummer 2004, an additional 118 adult lamprey were caught from Duffins Creek and Humber River, held separately, and brought alive to the AAHL. Until examined, lampreys were maintained alive in well- aerated chilled aquaria. Dissection, sampling and sample processing. Lampreys were euthanized with an overdose of MS 222 (tricaine methane sulfonate, Finquel- Ardent Chemical Laboratories, Washington) and dissected under aseptic conditions. Kidneys were removed aseptically and placed in sterile 7.5 cm x 18.5 cm Whirl-Pak® bags (Nasco, Fort Atkinson, WI) to which Hank’s Balanced Salt Solution (HBSS) was then added at a ratio of 1:4 (weight/ volume) and stomached for 120 seconds using a high-speed Biomaster Stomacher—80 (Wolf Laboratories Limited, Pocklington, York, UK). 173 Bacterial isolation and identification. A100 pl aliquots of stomached kidney tissue were spread onto MKDM (Eissa 2005, Chapter 2). Inoculated plates were incubated for up to 20 days at a sub-ambient temperature incubator adjusted to 15 °C. Incubated plates were checked for colonial growth on daily basis. Isolates were identified according to the standard morphological and biochemical criteria for R. salmoninarum as described by Sanders and Fryer (1980), Austin and Austin (1999) and Bruno and Munro (1986). Biochemical tests included: motility, in motility test medium (BD and Company Sparks, MD, USA), cytochrome oxidase determination on Pathotec strips (Remel, Lenexa, Kansas, USA), catalase with 3 % hydrogen peroxide, esculin hydrolysis using bile esculin agar (Remel), and a DNAse test using DNAse test medium (Remel). Carbohydrate utilization was performed using basal oxidation fermentation media (DIFCO-BD) that was prepared according to manufacturer instructions prior to the addition of individual sugars. Aseptically, 10 ml of filter sterilized (0.45 pm) 10 % sugar solution, was added to autoclaved and cooled (48 °C) basal media to reach a final concentration of 1 % with the exception of salicin, which was made as a 5 % solution to reach a 0.5 % final concentration. Each of the following sugars was added individually to the basal medium arabinose, glucose, lactose, maltose, rhamnose, salicin, sucrose, sorbitol, xylose. All sugars were from Sigma. 174 Nested PCR. A DNeasy tissue extraction kit (Qiagen-Valencia, CA, USA) was used to extract DNA from 100pl aliquots of kidney tissue homogenates. The DNA was extracted according to manufacturer's instructions, with a few minor modifications from the method described by Pascho et al. (1998). Tissue pellets were obtained by centrifugation at 6000 g for 20 minutes at 4 °C and the pellets were incubated with lysozyme buffer consisting of 180 pl of 20 mg lysozyme (Sigma), 20mM Tris-HCI, pH 8.0; 2 mM EDTA (Sigma) and 1.2 % (v/v) Triton X 100 (Sigma) at 37 °C for 1 hour. The nPCR method and primers recommended by Pascho et al. (1998) were employed with slight modifications to the volume of DNA (5 pl for first round and 2 pl for second round PCR reaction), water, and master mixes (45 pl for first round and 48 pl for second round nPCR reaction) .The controls were composed of a PCR mixture containing no DNA template reagent (negative control), positive R. salmoninarum and positive tissue control. A volume of 10 pl of the nPCR product and controls were mixed with 2 pl of 6X loading dye (Sigma) and used on a 2 % agarose gel (Invitrogen Life Technologies, Carlsbad, CA). Each electrophoresis gel included a 1kbp DNA ladder with 100 bp increments (Invitrogen). Gels were run in 1 X Tris Acetate Buffer (1 X TAE) gel buffer (Sigma). Gels were visualized under the KODAK EDAS Camera System and UV Trans-illuminator. Samples were considered positive when a 320 bp band was detected. Molecular confirmation of the purified bacterial isolates was also conducted using nPCR according to the method described by Chase and Pascho (1998). 175 Q-ELISA. The sample preparation and Q-ELISA protocol was adopted from the methods detailed in Pascho and Mulcahy (1987) and Alcorn and Pascho (2000). The positive negative threshold was determined according to the calculations detailed in Meyers et al. (1993). The positive -negative cutoff absorbance for the kidney homogenate was 0.10. The samples that tested- positive were assigned the following antigen level categories: low (0.10 to 0.19), medium (0.20-0.99) and high (1.000 or more) (Pascho et al., 1998). I76 RESULTS Isolation, identification and confirmation of Renibacterium salmoninarum. Renibacterium salmoninarum isolates were retrieved from the kidneys of 4 out of 25 (in 2003) and 5 out of 118 (in 2004) adult sea lamprey from the Duffins Creek/Humber River assemblage. The organism was not isolated from blood samples in 2003 nor 2004 (table 19). Morphologically, all isolates were Gram-positive diplobacilli or coccobacilli. On MKDM agar plates, the isolates produced 1 mm diameter, white, shiny, smooth, round colonies with raised surfaces. In MKDM broth, most of the isolates produced white granular pellets with the exception of two isolates (SL 14 and SLHR 15) that produced uniform turbidity with large white pellets. Biochemically, all the retrieved isolates were non-motile, catalase positive, cytochrome oxidase negative, esculin hydrolysis negative and DNAse negative. The bacteria did not produce acid from any of the carbohydrates that were tested (table 20). These bacterial isolates were identified as R. salmoninarum and they were confirmed using nPCR (Figure 20) and Q- ELISA. Detection of R. salmoninarum in sea lamprey kidneys. Bands of 320 bp, characteristic of R. salmoninarum were visualized using the nPCR technique in four (16 %) out of 25 lamprey kidney samples collected in the mid summer of 2003 (table 19). Using the same technique the organism was detected in 38 (66 %) out of 58 lamprey kidney samples collected in 2004 from the Duffins Creek site (table 19), while positive nPCR was recorded in 3 177 (5 %) out of 60 lamprey kidney samples collected from the Humber River site that year. When the Q-ELISA technique was performed on the 2004 samples, R. salmoninarum antigens were detected in the kidneys of two (1.7 %) of the 118 lamprey and were low in titer (table 19). 178 DISCUSSION Despite the fact that R. salmoninarum has been described as a salmonid-specific pathogen, it has been isolated for the first time from the sea lamprey (Petromyzon mar/nus) for two successive years (2003 and 2004). The prevalence in sea lamprey is relatively low when compared to the prevalence found in salmonines. Despite the isolation of R. salmoninarum from the kidneys of clinically affected sea lamprey, the bacterium was not isolated from the blood nor any other intemal organs. It appears that sea lamprey R. salmoninarum isolates possess the same affinity for kidney tissues as that of salmonid isolates. The morphological criteria and biochemical reactions of the retrieved sea lamprey isolates coincided with those described for R. salmoninarum (Sanders and Fryer 1980). The size of the detected amplicon band (320 bp) in both kidney tissues and cultured isolates using nPCR was consistent with that published for R. salmoninarum (Pascho et al., 1998; Chase and Pascho, 1998) While all R. salmoninarum isolates obtained in this study were positive with both nPCR and Q-ELISA, tissues from which the isolates were retrieved were not always positive. This discrepancy could be attributed to the presence of tissue inhibitors, present in the sea lamprey that may interfere with PCR or ELISA reactions. As Makos and Youson (1988) reported, the sea lamprey does not have a gall bladder, thus bile salts accumulate in the 179 muscles and kidneys. Biochemically, bile salts act as a detergent, which may contribute, to the inhibition of diagnostic assays. Inversely, in the case of Duffins Creek samples, other than SLDC6, nPCR yielded positive results while no R. salmoninarum was isolated. This finding could be explained by the presence of low numbers of bacteria that could be detected with nPCR, but are less than the threshold that allows their isolation. This threshold has been estimated by 100-colony forming units/gram tissue in salmonids fish (Lee 1989). The nested PCR assay can detect as little as 4-10 bacterial cells/gram tissue (Miriam, et al., 1997). In summary, this study reports the sea lamprey as a host for R. salmoninarum. The role played by Great Lakes sea lamprey in the epizootiology of BKD in the Great Lakes requires further investigations. 180 Sea Site of Type of % Positive % % Positive lamprey collection sample Cultured Positive nPCR Q-ELISA Samples samples samples 2003 Humber/Duffins Kidney (4/25) (4/25) ND SL1-25-03 Lake Ontario 16 % 16 % 2003 Hum ber/Duffins Blood (0/25) ND ND SL1-25—03 Lake Ontario 0 % 2004 Hum ber River Kidney (4/60) (3/60) (2/60) SLHR1-60 Lake Ontario 6.7 % 5 % 3.3 % 2004 Hum ber River Blood (0/60) ND ND SLHR1-60 Lake Ontarion 0 % 2004 Duffin’s Creek Kidney (1/58) (38/58) 0 % SLDC1-58 Lake Ontario 1.7 % 65.5 % 2004 Duffin’s Creek Blood (0/58) ND ND SLDC1-58 Lake Ontario 0 % Table 19. Prevalence of Renibacterium salmoninarum in kidneys and blood of 2003-2004 Lake Ontario sea lampreys using nPCR, Q-ELISA and culture. 181 Isolate ID Culture-based assays Q-ELISA E SL3-03 SL21-03 SL11-O3 SL14-03 SLDC 6-04 SLHR 9-04 SLHR14-O4 SLHR15-O4 SLHR16-O4 + + + 4. + + + + 4.. +++++++++ +++++++++ Table 20. Confirmation of Renibacterium salmoninarum isolates using some culture based assays, serological and molecular assays. Notice: SL3, SL21, SL11 and SL14 were the isolates retrieved from adult sea lamprey in mid summer 2003. DC6 was an Isolate retrieved from adult sea lamprey number 6 collected from Duffins Creek, Lake Ontario. HR9, HR14, HR15 and HR16 were isolates retrieved from adult sea lamprey collected from Humber River, Lake Ontario. Both DC and HR isolate were retrieved from adult sea lamprey collected in the mid summer 2004. Culture based assays: C (catalase), O (oxidase), E (esculin hydrolysis), D (DNAse), CHO (carbohydrate utilization) and M (Motility). Serological assay: (Q-ELISA -Polyclonal antibody based quantitative ELISA). Molecular assay: (nPCR-Nested polymerase chain reaction) 182 Figure 20. Nested PCR assay performed on isolates showing the characteristic 320 bp band of Renibacterium salmoninarum isolates. Notice: SL3, SL21, SL11 and SL14 were the isolates retrieved from adult sea lamprey in mid summer 2003. DC6 was an isolate retrieved from adult sea lamprey number 6 collected from Duffins Creek, Lake Ontario. HR9, HR14, HR15 and HR16 were isolates retrieved from adult sea lamprey collected from Humber River, Lake Ontario. Both DC and HR isolate were retrieved from adult sea lamprey collected in the mid summer 2004. Samples were considered positive when a 320 bp band was detected. L: 1kbp DNA ladder with 100 bp increments 183 CHAPTER SEVEN CONCLUSIONS AND FUTURE RESEARCH CONCLUSIONS Although BKD exists in Michigan since 1955, only little is known about the status and magnitude of the disease in salmonids and water basin of Michigan. The only available information about the disease was from publications in Europe, Canada and Pacific Northwest. Renibacterium salmoninarum, the causative agent of BKD grows slowly in vitro and in vivo and incubation period might extend to up to 12 weeks before obtaining bacterial growth. Further, most of the published studies concerning these issues showed marked inconsistency. Bacterial Kidney Disease is focal in its distribution within the affected kidneys, thus targeting a part of the kidney other than the focus of infection (granulomas) might lead to negative testing results. All the aforementioned factors were the triggering factors that lead me to develop my research on BKD in Michigan salmonines. Initially, in order to overcome the slow growing nature and the longer incubation period of the pathogen, an optimized tissue processing and culture procedures together with a modified growth medium have been developed. The protocol and modified medium have significantly shortened the incubation time and allowed culturing of R. salmoninarum with relative ease throughout the study. These achievements allowed the isolation of relatively large number of R. salmoninarum isolates from both cultured and wild salmonines. These isolates 184 constitute a unique resource for future studies of R. salmoninarum and BKD in the Great Lakes. Findings also demonstrated that R. salmoninarum is widespread in Michigan. Using the analysis of different diagnostic testing patterns produced from different agreements and disagreements in results of diagnostic BKD testing assays (Nested PCR, Quantitative ELISA, and Culture) I was able to track the progress of natural R. salmoninarum infection in some of Michigan’s salmonid stocks. The disagreement in results among the three assays was linked to different phases of R. salmoninarum infection at the time of sampling. The testing results demonstrated the presence of diagnostic testing patterns, with each of the patterns representing a probable stage along the course of R. salmoninarum infection. Data generated in chapter four of this dissertation provided additional evidence that R. salmoninarum infection is enzootic in Michigan watersheds. Lake Michigan’s chinook salmon tend to have overall higher R. salmoninarum prevalence than that in Lake Huron’s fish. Data also indicated that R. salmoninarum infection and intensity in retuming feral salmon seem to fluctuate among years, although a definitive decrease can be observed since the start of this study in 2001. Data of this study demonstrated the ability of both Chinook (Oncorhynchus tshawytscha) and coho (Oncorhynchus kisutch) females and males to shed R. salmoninarum along with gametes. The BKD testing of both feral spawners and their hatchery raised offspring fingerlings demonstrates that 185 the current testing and culling programs have been partially successful in reducing R. salmoninarum transmission. In chapter five, a gradual decrease in R. salmoninarum prevalence in the hatchery raised and wild brook trout (salve/inus fontinalis) was noticed throughout the period from 2001 to 2004. The role-played by hatchery practices in minimizing the spread and prevalence of BKD among Michigan brook trout populations was discussed. Despite the fact that most of the epidemiological studies performed in the past diminished the role played by males in transmission of the R. salmoninarum, yet data presented in this study indicated that males can shed a fair amount of R. salmoninarum and its soluble antigens into the milt which increase the possibilities played by male in spreading the disease. Also, a number of BKD outbreaks involving the brook trout have been investigated using a number of diagnostic techniques through the duration of the study. Analysis of results presented in this chapter confirmed the previously reported assumption that brook trout is highly susceptible to R. salmoninarum infection. Finally, data generated in chapter six indicated that the non salmonid adult sea lamprey is a new host range for R. salmoninarum and might possibly play a role in the dissemination of R. salmoninarum during the process of relocation of adult stages between number of watersheds in great lakes including Lake Michigan and Lake Huron watersheds. 186 FUTURE RESEARCH The data obtained in this dissertation established a solid base for future research on Renibacterium salmoninarum (R. salmoninarum) infection in salmonids and non-salmonid species in Michigan. Further research is required to study the effect of each ingredient of the modified media on growth of the bacteria. Further, the chemical constituents of the R. salmoninarum metablites released in culture media or into in the infected tissue are needed to be identified in detail and wethere there is a dissimilarity or resemblance between In vivo and In vitro production of metabolites. Molecular basis behind the antibiotic resistence of some R. salmoninarum strains should be fully investigated. Shedding of R. salmoninarum in male along with the milt has been proven in the current study. Yet, whether the bacteria are shed in the seminal fluid or passed on within the spennatozoal cells are needed to be elucidated. Concurrent Infections with R. salmoninarum and external parsites or other systemic bacteria as Aeromonas salmonicida and Fla vobacterium sp. were noticed during the current study. The sequential mechanisms of such concurrent infections needed to be fully investigated and addressed. Renibacterium salmoninarum was isolated for the first time from the kidneys of the adult parsitic seas lamprey. This work requires further research to determine the mechanism of infection in lampreys. Also, the possible role palyed by Sea lamprey in spreading the disease to salmonids needs to be illucidated. 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