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CHAPTER 1

Viral and Bacterial Diseases of

Valentine Helllin~vay, Jesse Brunner, Rick Speare, and Lee Berger

I. Introduction B. Erythrocytic C. Lucke Tumour Herpesvirus II. Viral Diseases D. Herpes-like Virus of Skin A. Ranaviruses E. Calicivirus 1. and Molecular Epidemiology F. Leucocyte 2. Biology III. Bacterial Diseases 3. Clinical Signs and Pathology A. Bacterial Septicaemia ("Red Leg") 4. Epidemiology B. Streptococcosis 5. Resistance to Infection C. Chlamydiosis 6. Transmission and Spread D. Mycobacteriosis 7. Diagnosis 8. Management IV. References 9. Discussion

1. INTRODUCTION A T least six groups of viruses have been reported to affect amphibians, including ficaliciviruses, herpesviruses, and iridoviruses (Johnson and Wellehall 2005). Only ranaviruses are known to cause widespread mass mortality and have been studied in detail; hence a review of this group of viruses forms the m~ority of this chapter. Various strains of ranavirus are found worldwide and some appear to have spread recently (Hyatt et al. 2000). Indicative of the broad host range of ranaviruses and their potentially devastating effects, ranaviral disease was listed by the World Organization for r\.nimal Health (OIE) as an internationally notifiable disease in 2008. Although their impacts 011 populations of declining species are a concern, there is currently no evidence that they have caused permanent declines or extinctions (Daszak et al. 2003). Nevertheless, because of their potential impacts on nai've populations, as well as OIl species that are facing multiple threats, it is important that the risk of spreading these pathogens is minimized (Cunningham et ai. 2007 a). There have been few investigations into other viruses. Apart from Frog Erythrocytic Virus (FEV), their impact on wild populations has not been studied. Lucke tumor herpesvirus has been well described, but the other viruses found associated with disease in amphibians have been reported in single papers with little or no experimental work. Their significance as pathogens of amphibians is therefore largely unknown. In addition other viruses, not reviewed here, such as arboviruscs (including West Nile Virus), and an adenovirus, can infect but their pathogenicity to amphibians is low or unknown (Densmore and Green 2007). 2964 AMPHIBHN BIOLOGY There are no substantiated reports of bacteria causing outbreaks in wild frogs, and cases of bacterial disease were rare during large surveys for disease in the United States and Australia (Berger 2001; Green et at. 2002). Bacterial diseases, including septicaemia, are associated with significant mortality in captivity and are associated with poor husbandry. For details OIl prevention, management and treatment of bacterial diseases in captivity see Wright and Whitaker (2001). Zoonotic bacteria carried by wild and captive amphibians with minimal effect on themselves, but which are potential risk to humans (e.g., Salmonella and Leptospira), are not included in the present review.

II. VIRAL DISEASES

A. Ranaviruses

A recent spate of research on ranaviruses was stimulated by the inlerest in global amphibian declines (Chinchar 2002). It built OIl earlier work that illitially arose out of the discovery of ranaviruses in Lucke tumor research (Granoff et al. 1969), then mortalities (Langdon 1989), and subsequently their possible use as a biological c011trol agent for the cane toad (B'llfo marinus) in Australia (Speare 1990; Pallister et at. 2007). Ranaviruses are significant infectious agents that can cause great mortality in free-living amphibian popUlations (Cunningham et a1. 1996) although they are not currently believed to be responsible for amphibian declines (Daszak et al. 2003). Amphibian ranaviruses are enveloped icosahedral DNA viruses in the family (Hengstberger et ai. 1993). Isolates causing disease have been found in wild and cultured amphibians in Australia (Speare and Smith 1992), the Americas (Wolf et at. 1968; Zupallovic et al. 1998b; Majji et al. 2006), Asia (He et al. 200 1; Zhang et al. 2001; Weng et at. 2002), and Europe (Cunningham et al. 1996). These include Tadpole edema virus, Frog virus 3, Rana catesbeiana virus Z, Ambystollla tigrinum virus, Bohlc , and UK ranavirus.

In North America, ranavinlses are responsible for massive mortality in amphibian larvae and recent metamorphs, while die-offs rarely occur in adults (Green et at. 2002). These ranavirus-induced mortality events often occur dming summer and involve hundreds to thousands of moribund and dead larvae within a few days (Green et al. 2002). Additionally, adult amphibians can be chronically infected carriers, maintaining infection in a population ('tVolf et at. 1969; Brunner et at. 2004; Robert et al. 2007). In contrast, ranaviral disease in the United Kingdom typically causes massive, synchronous annual mortality of adult frogs (Dnlry et at. 1995). Molecular work suggests there has been recent spread of ranaviruses both locally and globally. For instance, the strains that occur in the United Kingdom and in captive-breeding facilities worldwide may have originated from North America (Hyatt et al. 2000)

1. TaxonolllJ and jVIoleculaT Ej)idemiolog)'

Currently there are six commonly recognized species of ranavirus (lCTVdB Management 2006), three of which were isolated from amphibians and the others from fish. Species of ranavirus are differentiated on the basis of genetic sequences, particularly the sequencing regions of the major (Mao et al. 1997, Hyatt et al. 2000), but also by restriction [i'agment length polymorphism (RFLP) profiles and by DNA hybridization (Hyatt et al. 2000), virus protein profiles, and the range and specificity of the host (Hyatt et at. 2000, ICTVdB Management 2006). Howevel~ while isolates of the same species are largely homologous, or even identical ill MCP sequence (~ 95% sequence identity), they can be quite distinct in RFLP profiles (Hyatt et al. 2000; M

Frog Virus 3 (FV3), the type ranavinls, was isolated from aclinically infected leopard tl:ogs (Rana pijJiens) collected in the United States in 1962 (Granoff et al. 1965). Since then, FV3 or FV3-like viruses, such as Tadpole edema virus (TEV) , Rana wtesbeiana vims Z (RCV­ Z), and UK Ranaviruses (RUK, BUK), have been associated with amphibian mortality in North America (\Volf et al. 1968, ·Wolf et al. 1969, Petranka et al. 2003, Greer et al. 2005, Bank et al. 2007, Majji et al. 2006, Schock et at. 2008), South America (Zupanovic et al. 1998a, 1998b), the United Kingdom (Drury et at. 1995), and Southeast Asia (Kallachanakhan 1998, Zhang et at. 200 I). The second distinct amphibian ranavirus species to be discovered was Bohle Iridovims (BlV), isolated from newly metamorphosed ornate burrowing frogs ( onwtus) in Queensland, Australia (Speare and Smith 1992; Hengstberger et at. 1993). It remains the only isolate of this species although subsequently ill wild Litoria caentlea had positive PCR [or BI\~ but the virus could not be isolated (Cullen and Owens 2002). Antibodies against ranaviruses were detected in cane toads throughout most o[ their range in Australia at an overall prevalence of 2.7% (range 0-18%). The identity of the ranavirus that induced the antibodies is unknown since the test is not species specific and no vinlses were isolated from any cane toads (Zupanovic et al. 1998b). Lastly, the Ambystoma t?:grinnrn virus (ATV) was isolated from a threatened sub-species of (Ambystoma tigrinum stebbinsi) in southern Arizona, USA in 1995 aancovich et al. 1997). Similar ATV-like vimses have been isolated from many locations in western North America (Bollinger et al. 1999; Jancovich et ai. 2005; Ridenhour and Storfer 2008), but not elsewhere. Ranaviruses can cause aclinical infections in resistant , which may bcilitate the spread of disease via the inadvertent movement of infected animals (Robert et al. 2(07). The tracle of amphibians for food, research, and as pets has likely played a role in the movement of pathogens such as ranaviruses both within and among- continents (Cunningham and Langton 1997; Jancovich et rtl. 2005; Galli et at. 2006; Picco and Collins 2008). Phylogenetic analyses of ATV isolates based on sequence from the MCP and DNA methyltrallsferase genes, as well as two non-coding regions, suggest a single introduction and radiation of these salamander rallaviruses, with little genetic divergence among isolates « 1.1 %), but a rather complex phylogeography aancovich et al. 2005). Nested-clades analyses suggest long-distance dispersal. One clade encompassed isolates from southern Arizona to Saskatchewan, as well as isolates from the bait trade and one from the axolotl (Ambystoma mexicanum) colony at Indiana University (Jancovich et al. 2005). ATV has been frequently isolated from tiger salamander larvae used as fishing bait (Picco and Collins 2008) and so at least some of these dispersals are probably due to moving infected bait. An analysis of concordance betl'{een the phylogenies of ATV and the tiger salamander host showed an overall lack of congruence, but ·when three isolates of presumably anthropogenic origins \vere excluded, the trees of the host and virus were identical, indicating co-evolution between host and parasite (Storfer et al. 2007).

Interestingly, the UK ranavirus from common frogs (Rana temporana), RUK, is phylogenetically similar to the FV3-like viruses from North America which, in addition to the [act that animals with signs of ranavirus infection were not observed before the mid- 1980s, sug'gests a recent introduction of the virus into the UK (Hyatt et 01. 2000; Cunningham et at. 2007a). Recently an FV3-like virus was identified during mortality events in natural populations of the endemic Ateiognatlms patagoniclls in Argentina (Fox et at. 2(06). It showed 100% identity with the original FV3 isolate across 500bp of the MCP gene, which is consistent with a recent introduction from North America.

2. Biology

Ranavirllses are composed of lineal~ double-stranded DNA encoding - 100 (Williams et af. 2(00) encapsulated in an icosahedral particle -130 nm in diameter 2966 AMPHIBIAN I3IOLOGY with an internal lipid membrane. The capsid mayor lIlay not be enveloped (Braunwalcl et al. 1979) but both forms are infective (Chin char 2002). Ranaviruses cause disease involving multiple organs and tissues in fish, amphibians, and reptiles (Chinchar 2002). The virus attaches to an as yet unidentified, but apparently widely distributed, receptor on host cells. Enveloped virions enter via receptor-mediated endocytosis, losing their envelope and releasing their nucleoprotein core. If the virus is naked, it enters the cell via fusion between the internal lipid membrane and the plasma membrane (Chinchar 2002). Early events in virus replication occur in the cell's nucleus, including transcription of early viral mRNAs and replication of copies of one-unit to two-unit lengths of the viral genome. Late viral mRNAs seem to be transcribed in the cytoplasm (Chinchar 2002). Viral assembly occurs at distinct assembly sites in the cell and the newly formed virions either bud off from the cell or, more commonly, accumulate in the cell until the cell lyses (Goorha and Granoff 1978). The machinery and metabolism of infected cells are rapidly diverted into viral replication (MUlti et al. 1985a,b; Willis et al. 1985; Goorha and Granoff 1999; Chinchar 2002). Ranavirus particles are environmentally resistant and can remain infectious for long periods in certain environments. Studies of a fish ranavirus (EHNV) showed that it remained infective after drying for over 100 days at 15 DC (Langdon 1989). Heating to 60DC for 15 minutes or 40D C for 24 hours inactivated the vints. Brunner et al. (2007), howevel~ found that A'TV was rendered non-infectious when dried ill pond substrate and viral titres declined dramatically in ATV-spiked pond water. Ultraviolet radiation from UV water­ sterilizers killed BlV rapidly at high flow rates (Miocevic et al. 1993). FV3 replicates optimally in culture between 12°C and 32D C, although it can replicate to some extent both below and above this range (Goorha and Granoff 1974). BIV had a thermal limit of 33D C, above which it would not grow. It was capable of infecting fish and mammalian cell lines (if maintained at < 34°C) but. not insect cell lines in vitro (Speare and Smith J 992). The Venezuelan Rallavims replicated readily at temperatures ranging from 18°C to 30°C (Zupanovic et al. 1998b).

3. Clinical Signs and Patholog)1 The gross pathology of ranaviruses appears similar to that associated with bacterial septicaemia. Since opportunistic or resident bacteria can often be cultured from dead or sick frogs, it appears that many ranaviral outbreaks have been misdiagnosed as septicaemia (Green 2001; see also "Bacterial septicaemia 'red leg'" in the "Bacterial Diseases" section below). For a more thorough treatment of ranavirus pathology see Wright and Whitaker (2001). Frog Virus-3: Frog virus-3 (FV3) was found while searching for a viral cause of the Lucke tumour ill Rana pipiens in the United States (Granoff et al. 1969). Subsequently, much work was carried out on the morphology and life cycle of FV3 in the laboratory, and experimentally it was shown to cause oedema, necrosis, haemorrhage, and death in embryos, tadpoles, and recent metamorphs (Granoff 1989). During experimental infections, metamorphic toads developed haemorrhages, accompanied by massive oedema, in the ventral skeletal musculature, stomach, and intestines (Came et al. 1968). In addition, tadpoles of the Italian agile frog (Rana latastei) exposed to FV3 sometimes became emaciated (Pearman et al. 2004). Mortality in embryos can occur 3-12 days post-exposure with 40- 70% survivorship of tadpoles (TIveedell and Granoff 1968). Clinical signs include depigmentation, skin sloughing, and spinal curvature. Generally, the lesions caused by FV3 appear to be milder thall those caused by Tadpole oedema vints (Green 2001). Tadpole Edema Virus: Tadpole Edema Vints (TEV) was first isolated from oedemic Rana catesbeiana tadpoles from West Virginia, USA in August 1965 (Wolf et al. 1968, 1969). Molecular evidence suggests that TEV is a strain of FV3 (Hyatt et at. 2000). Acute fatal disease was reproduced with experimental transmission to tadpoles and adults, although pathogenicity varied among host species (Wolf et aL. 1968). Terminal changes in tadpoles are obvious oedema, particularly in the ventral regions, and haemorrhaging along the body HEMINGWAY ETAL: VIRAL AND BACTERIAL DISEASES OF AMPHIBIANS 2967 and hind limbs (Fig. 1) (Green 2001). Internally, haemorrhages and necrosis typically extend into the stomach, intestines, and skeletal muscles, and may include the mesonephros, bladder, liver, lungs, and spleen (Green 2001). The highest titres of the virus occur in the stomach (Clark et al. 1969; Green 2001). UK Ranavirns: v\lhile molecular studies suggest UK ranaviruses are strains of FV3 and lIla)1 have originated in North America (Hyatt et aL. 2000), theses viruses are not hig'hly pathogenic to embryos and tadpoles (Cunningham et at. 1996, Cunningham et at. 2007a). There are several distinct "syndromes" associated with the UK ranaviruses including an "ulcerative syndrome," "haemorrhagic syndrome," and "ulcerative and haemorrhagic

Fig. 1. Ventral view of a moribund larval California reel-legged frog (Ra.na draytonii) with oedema and petechial haemorrhages in the hind legs and inguinal region typical of TEV infection. Photograph by Valentine Hemingway.

syndrome" (Cunningham el al. 1996). '·Vhile these syndromes are associated with infection by the bacterium Aeromonas hydrojJhila, Cunningham et at. (2007a) demonstrated that bacteria were not the cause. Frogs with the "ulcerative syndrome" have skin ulcerations and, to a lesser extent, necrosis of the legs, while systemic haemorrhages, particularly in the myoskeletal, digestive, renal, and reproductive organs, lungs, and pancreas characterize the "haemorrhagic syndrome" (Cunningham et al. 1996, Green 2001). Frogs with either or both syndromes were thin and some experienced lethargy (Cunningham et al. 1996). Histological lesions t.ypical of "ulcerative syndrome" include epidermal thickening, and epidermal necrosis, as well as necrosis, granulocytic inflammation, congestion, and haemorrhage in internal organs (Cunningham et al. 1996). Experimentally infected Rana temporaria died six to eight days post-infection (Cunningham et al. 2007b). Bohle hidovirus: The only virus to be isolated from Australian fi'ogs, Bohle iridovirus (BIV), was first found in Limnod)'ywstes OTTlatus that died during metamorphosis in captivity (Speare and Smith 1992). The frogs had been collected as tadpoles from a temporary pond at Bohle, a suburb of Townsville, Queensland. BIY and FV3 appear to be closely related (Hcngstberg'er et al. 1993). Clinical signs of the Bohle iridovirus were oedema of subcutaneous tissue, especially around the jaw and head, and a swollen abdomen due to ascites (Fig. 2). Subcutaneous haemorrhages OCCUlTed on the ventral abdomen, inguinal areas. and lower jaw (R. Speare, unpublished data). Typical pathology in natural and experimental infections included severe renal, pulmonary, hepatic, splenic, and haernopoietic 2968 AMPHIBLAK BIOLOGY necroses and haemorrhages. RanavirLls immunoperoxidase stained many cdl types in live]~ lnng, spleen and, in particula]~ fibrocytes in extensive areas of swollen, necrotic dermis and glomeruli (CulicH et al. 1995, L. Berger and R. Speare, unpublished data). In experimental infections, high mortality rates in juvenile frogs typically occurred within 5 to 25 days, depending on dose and type of exposure, but adults were less susceptible (Cullen and Owens 2002). Chronic cases were detected by peR (Cullen and Owens 2(02). Ambysloma tigrinwn Virus: Experimental infections of Amb)'stoma tigrinH.1Il virus (ATV) in tiger salamanders caused 40 to 100(1c· mortality within lWO to three weeks (Brunner et at. 2(05). Infecled animals may show haemorrhaging ill internal organs as well as white skin polyps, skin sloughing \vith mucus and ulcers, bloody mucus from the cloaca, and lethargy, and may refuse food, while others may die without clinical signs (Fig. ;;) Uancovich et al.

fig. 2. 1fetamorphs of Limnodp1Gstes on/alus with a,cites. This frog died from Bohle lriclovirus during the original outbreak [rom which the virus was first. isolated. Photograph by Rick Speare.

1997; Chinchar 2002). Further, infected lung, skin, and liver cells are larger than are uuiufectcd cells Qancoyich et al. 1997). Infected animals may be able to maintaiu chronic, sublethal or aclinical infections, likely contributing to maintenance of infection in the population (Brunner et al. 2004). Mortality ill wild populations occurs primarily ill larvae in the northern part of their range and in larvae and neotonic adults ill the southern part of the salamander's range U. Brunner, ullpublished clata). Croatian Ranavims: A ranavirus-like agent called "viral haemorrhagic septicaemia of frogs" was found in dying captive Rana escuJenta from Croalia that had lethargy, oedema, haemorrhages, and skin necrosis (F~jan et al. 1991). Rana catesbel:ana V1:rus Z: A ranavirlls similar to other ranaviruses, sllch as FV3, was isolated from cultured R. catesbe'iana tadpoles in the USA (M<~tii et (Ii. 2006). Rana catesbeiana virus Z (RCV-Z) appears to be much more pathogenic than FV3, causing mortality in 50- 100% of exposed tadpoles (M'Wi et (d. 2006). Similar to other ranavirllses, symptoms HEMIl\GWAY ET AL: VIR.·\L AND BACTERL..... L DISEASES OF AMPHIB!A:-.JS 2969 included oedema in the abdolllell, haemorrhaging in venrral regions, and lethargy (ivlajji et al. 2006).

Venezuelan Ranavirlls: Seven ranaviruses with strong similarities 10 BIV and FV3 were isolated from wild-caught Bnla lIlarillllS and Lepudactyills spp. in Venezuela (Zupanovic et at. 1998b). I nlected animals had no external lesions or internal symptoms (Zupanovic el ai. 1998b).

Fig. 3. Moribund ATV·iniectecl lan'a! tiger salamander (Ambystomll tigritlwn) wiLh oedema of the hinel legs and with petechial haemorrhages 011 the jaw. inguinal region. legs. and tail. Photograph by .Jesse Blllllller.

4. Epidemiology IlIlpacts on PojuLiations: While the first ranaviruses were isolated in the 1960s (Granoff et al. 1965; V..'olf et al. 1968), it was !lot ulltil the 1990s that ranavirllses were recognized as causing lllass mortality in wild populations of amphibians (AT\.'; J a!lcovich et al. 1997; RUK: Drury et al. 1995). Ranavil'llses have since been identified as the agents of Ulas:> mortality events around the world. :'-.10st outbreaks of amphibian ranavirl.lses have heen reponed from North America and the L niled Ki!lgdolll, although this may represent a bias ill reporting l'ather thall the actual distributions. Ranavirus-associated die-offs arc characterized by a rapid onset with massive mortality involving' nearly all of the individuals in a ponel (Green et al. 2002); entire cohorts can be killed (Petranka et at. 200:); Brunner et al. 2004). Die-otIs also tend to recll1' in the same ponds or wetlands for several years in a row (Green et al. 2002; Cunningham et at. 2007a; Petranka et al. 2007; Greer and Collins 2008). Whereas ranaviruses tend to cause recurrent mortality, they are not associated with catastrophic amphibian declines (Green et al. 2002; Daszak et al. 2003).

Green et al. (2002) found that t he majority of amphibian clie-offs (25 of 44 investigated) in the United States were caused by iridoviruses, presumably ranavirLlses. ATV has a wide distribution in North America, having been isolated from tiger salamallliers during clie­ ofIs throughout the western cordillera and central plains (Bollinger et al. 1999; Green et al. 2002; Jancovich et al. 2005). Similarly, FV3-like viruses have been associated with amphibian die-atE; - generally il1\'olving anurans but also spotted salamander larvae (Ambyslollla fl1Ilculatum) and adult eastern spotted newts (NotuphthallllllS vil'ie/esa17s) (Petranka et al. :!003; DllffiJS et al. 2008) - across North America (Mao et at. 1999; Green et al. 2002; Petranka et al. 2003; Greer et a1. 2005; Gray et al. 2007; Duffus et at. 2008; St. Amour et al. 2008; Schock et al. 2008). FV3-like ranavirus caused recurrent, catastrophic die-off's of larval Atnbysloma macldatullZ and Rana s),lvalica in a network of natllral and constructed ponds and wetlands in North Carolina fi'OIll 1997, when they were first detected (although monitorillg had begun in 1994), until at least 2006 (Petranka et al. 2003, 2007). In most years well over half of the 2970 A\II'HIBL-'..:-.J HIOLOGY ponds surveyed experienced die-offs. Juvenile recruitment was dramatically affected by these die-offs, as well as by droughts, which led to a reduction in breeding activity in later years (Petranka fli al. 2007). Populations or both species, howeveI; remained extant in this complex. It is worth noting that die-offs and amphibians with signs consistent with ranavims infection have not been observed in other ponds and wetlands in the region (Harp and Petranka 2006), suggesting that outbreaks of FV3 can be highly localized.

Populations of Ilmbystoma tigrinutn nebulosllln in northern Arizona and the endangered A. tigrinum stebbinsi in southern Arizona have experienced recurrent, catastrophic die-of(s since at least the mid-1980s (Collins et al. 1988); these events were later attributed to the ranavirus, ATV Gancovich et al. 1997), yet these population persist (Greer and Collins 2008). At the level of a pond, however. ranavirus epidemics lllay canse local extinctions; tiger salamanders were apparently extirpated in some ponds in Saskatchewan after 3 to 4 years of ATV-related die-offs (Carey et al. 2003). Unlike An,: which has only been found in central and western North America (J ancovich et a1. 2005), and BlY, which has been detected in the wild only once, in Queensland, Australia (Speare and Smith 1992; Hengstberger et a!. 1993), FV3 is globally distributed. FV3-like viruses have also been reported from dead and moribund arnphibiam in captive populations in North America (Robert et al. 2007; Miller et al. 2008) and in frog farms in Brazil and Cruguay (Galli et at. 2006), TIlailand (Kanachanakhan 1998), and China (Zhang et al. 1999). The most extensive amphibian ranavirus epidemics have occurred in the United Kingdom since the mid 1980s, where FV3-like ranaviruses have caused annllal IIlass die­ offs of cOlllmon frogs (Rema temporaria) and common toads (Buj() bufo) in garden-ponds across much of the cOllntry, but focused in the south and east (Drury et ai. 1995; Cunningham et al. 1996; CUIlningham (it rd. 2007a,b). FV3-like l'anaviruses were the putative cause of these die-offs (Drury et al. 1995; Cunningham et al. 2007a) affecti.ng tens of thousands of frogs across the United Kingdom but, again, there is little evidence of population declines (Daszak et al. 2003). Still, as Daszak et a1. (2003) argued, I he potential for ranavi t'IIses to impact amphibian populations should not be discoullted. 'There are at least two reasons why populations may remain extant, or even abundant, in the face of high ranaviral mortality. First, natural mortality of tadpoles is normally very high due to predatioll and to drying of ponds but only a small fraction of the individuals need to survive in order for adequate recruitment to occur. Rallaviruses may, therefore, cause only compensatory mortality, with little added effect on long-term population dYllamics. Secondly, many affected species are rather co III III OIl and widespread. COllSequently, local populations lllay be rescued by immigration from other ponds and the rnetapopulation would persist. Of course habitat loss and alteration of habitat would undermine this effect.

Life stages: 1\·lost die-offs caused by ranaviruses involve larvae or recent metamorphs inhabiting permanent water (Speare and Smith 1992;.J ancovich et al. 1997; Green et al. 2002; Petranka et al. 2003; Fox eL al. 2006). Several studies involving experimental exposures have shown that larvae are much more susceptible to BIV and FV3-like viral infections than arc adults ('vVolf ei al. 19G8; Clark et al. 1969; Cullen and Owells 2002; Galltress et aI. 2003; but also see Cullell et al. 1995), and the patterns of mortality in the wild bear this out. The ranavirnses in tbe United Kingdom are the exception: larvae are affected, but most of the mortality is observed ill adult frogs and toads (Cunningham et ai. 1996; Cunningham ei aL. 2007a).

Range in Host Taxa: The three species of amphibian ranClviruses have a broad range in host taxa. Overall, the array of hosts of ranaviruses under ecologically realistic conditions remains poorly resolved hut, potentially, it is important to the epidemiology of ranaviruses in amphibian communities. Several of the amphibian ranavirlls are capable of infecting hosts from three vertebrate classes: Amphibia. Pisces and "RepLilia". BIV was highly pathogenic HEl"!l:-.J(;WAY ET AL: VIRA.L AND BACTERIAL DISE:\SES OF Al'-oJPHIBIA;'\lS 2971

[or mammaliall cells in vitro, but presumably in vivo protection is provided by t he host's body tcmperature being above the maximum for replication of BTV (Speare and Smith 1992).

B1V was first isolated [1'0111 the ornate burrowing frog (Lililllodynastes omatus), but has since been found to infect other captive or experimental hosts, including Bufo marinlls, Litoria terraereginae, L. caem/ea, L. albngutatta, C)'ClOrtlflfl b'revipes, and L. latojJalmata, as well as the native barramundi fish (Lates calcarifer) and reptiles (Owem 1994; Cullen et al. 1995; Ariel 1997; ClIllen and Owens 2002; Moody and Chinchar 2002; Williams et al. 2005). Juvenile L. termereginae, L. caemlea, and L. latopalllZata were highly susceptible to BI\.~ while larval L. lerraereginae and adults of L. cnemlea and other species were less susceptible. Ylortality varied with dose and route (Cullen et at. 1995). Frog Virus 3-like viruses are also infect.ious to frogs, salamanders, , and reptiles. Mao et al. (1999) found apparently identical FV3-like viruses in sympatric three-spine sticklebacks (Gastemsteus aeulealus) and a tadpole of the northern reel-legged frog (Rona aurora), and Johnson and Jacobson (200<1) isolated a ranavirus identical in MCP sequence from a captive (Geochelnn latynota) and an ill southern leopard ti'og (Rana utricnlaTia) in the tortoise's enclosure. FV3-like viruses commonly infect both frogs and salamanders under natural conditions. III the 19605 TEV, an FV73-like virus isolated from Rana calesbeiallrl, was found in tadpole of Bllfo (LlIleriuLr/us, B. U'oodflO'llSii Jowleri, and Spea inleTirtonlalla (\Volf et al. 1968, 1969). More recently, Pet.ranka et al. (2003) reported FV3-like viruses from s),lIlpatric Amb)lstoma IIUlcnlatwn and RCl1Ia sylvatica ill North Carolina, and Duffus et at. (2008) found apparently idelltical FV3-like viruses in larvae of Pseudacris spp., I-fyla versicolO1' and ambystolllatid salamanders in south-central Ontario. Schock et al. (2008), however, found that while Ambystom£l llgrimun, R(ma ~)'l'uatica, R. jJipie1l5, and I-f)'la regilla cOllld be experimentally infected with both FV3 and An: in at least one pond, strains o[ ATV and FV3 were co-circulating in distinct host species. Raila temporaria United Killgdom virus (RU K) has beell reported in the (Rana temjJomria) (Cunningham eL af. 2006) and a similar virus, Bufo bufo United Kingdom virus (BUK), has been found to infect both the common toad (Bufo bufo) and (experimentally) the common frug (Cullningham et al. 20071».

A.TV may have the most restricted array of hosts. Based 011 experimental challenges of the northwestern ~alalllander (;lmb),stom,(J, gTClcile) and the easterIl newt (Noto/Jht/wlm'lls Vi1'idpsCPIIS), as well as Rana pll)iens and R. catesbeiana and three species of fish (Gambusia affilli~, Lepomis (~fJinis, and Oncorh),llchlls lIl)kiss) with ATV-SRV (an isolate from A. figI'm/Wi stebbinsl in the Sail Rafael Y.llley in southern Arizona), J

5. Resistance to Infection Amphibians may fight ranaviral infections via both acquired and innate immunity. A first line of defence includes antimicrobial pepticles of the skin (Erspamer 1994) which have been shown in some species to be effective against rallavirus in vitro (Chinchar et ai. 2001; Rollins-Smith et ai. 2002). Antibodies specific to ranavirus are also produced, although their efficacy appears to be species specific (Chinch'll' et al. 1984). There seems to be a distinction between anurall and caudate immune responses to ranaviral infections. Rana catesbeiana tadpoles that recovered after exposure to FV3 or RCV-Z appeared to be protected from future lethal infection with RCV-Z (Majji et af. 2006). Brunner and Schock (unpublished data) found that surviving an experimental exposure to ATV does not provide protection HEMINGWAY ET AI.: VIRAL AND BACTERIAL DISEi-\.SES OF MIPHIBIr'u"JS 2973 against later exposures (i.e., no immune memory). Cotter et al. (2008) found that although experimentally infected Ambystoma mexicanwn mounted an impressive immune response, they lacked the production of lymphocytes by the spleen that are associated with the ability of adult Xenojms to clear ranaviral infections (Robert et al. 2005; Maniero et ai. 2006). This may be an important function in species that are able to clear ranaviral infections. The ontcome of infection varies greatly with genetic identity of individuals as well as with life hist.ory stage (Brunner et al. 2005; Pearman and Garner 2005). Survivorship when infected with ranavirus also appears to be related to dosage. When groups of tadpoles of the Italian agile frog (Rana latastei) were exposed to different dosages of FV3, the animals that. received the lowest dosage survived the longest (Pearman et al. 2004). Duffus et al. (2008) found that when tadpoles of the (Rana sylvatica) were exposed to increasing dosages of FV3, there was a corresponding increase in the proportion of infected tadpoles. Brunner et al. (2005) demonstrated that the proportion of tiger salamanders (Ambystoma tigrinmn) that became infected with ATV increased with dose of inoculum, as did mortality, whereas time to death was reduced. Dose varies with route of exposure and this lllay play an important role in the outcome of infection (Cullen and Owens 2002; Brunner et al. 2005).

6. Transmission and Sjn'earl Local transmission of l'anavirus can occur via several direct and indirect routes. "While a variety of laboratory studies have demonstrated that ranaviruses can be t.ransmitted via indirect routes, i.e. fomites, soil, contaminated water (Pearman et o,{, 2004; Duffus et at. 2005; Harp and Petranka 2006; Brunner et al. 2007), it appears that more direct contact, i.e. touching, bit.ing, , necrophagy, may be required for transmission in a natural setting (Jancovich et al. 1997, Brunner et al. 2004, 2007; Pearman et al. 2004; Parris et al. 2005; IIarp and Petranka 2006).

The rate and outcome of infection seem to vary with the route of exposure. For example, when infected tadpoles of the wood frog (Rana sylvatica) were introduced into a tank with uninfected tadpoles, mortality was upwards of 98%, 'while tadpoles exposed only to water aud sediment from a site 'with an active ranavirus die-off did not experience a catastrophic die-off and individuals primarily developed aclinical ranaviral infections (Harp and Petranka 2006). Movement of water or sediment via fomites or aclinically infected animals between sites may facilitate the spread of ranaviruses (Harp and Petrallka 2006). One of the most important issues in epidemiology and conservation is whether transmission scales with host density (McCallum et at. 2001; de Castro and Bolker 2005). \'Vhen transmission is density-dependent, pathogens can (at least theoretically) drive the population only so low because at some threshold transmission becomes so rare that the pathogen fades from the population. If, howevel~ transmission continues unabated even as the host population declines, thCll extinction is possible. The evidence from ranaviruses is mixed. In a controlled environment, when infected Rana s)llvatica tadpoles were placed in a pool \"ith healthy tadpoles, more than 98% of the tadpoles died, regardless of initial tadpole density in the pool (Harp and Petranka 2006) .. In contrast, Greer et al. (2008) found that infection rates in naIve tiger salamander larvae increased with the density of ATV­ infected hosts to which they were exposed, although not in a strictly density-dependent manner. Interestingly, gTeater densities of infected larvae led to an earlier death for the newly exposed larvae. Necrophagy and cannibalism of infected animals are also potentially important routes of direct transmission. Necrophagy, in particular, seems to be a density-independent form of transmission; infected carcasses are a steady source of infection regardless of host density. Transmission by necrophagy and cannibalism is common in host species such as Arnbystollla tigrinum, Rana sylvatica, and R. latastei (Pearman et al. 2004; Harp and Petranka 2006; Brullner et al. 2007) and infections acquired by these routes seem to be more lethal. AMPHIBL'l.N BIOLOGY

CEldpoles of R. lataslei that fed on carcasses of FV3 infected tadpoles became intected and were more likely to die than were tadpoles in close proximity to infected carcasses but without direct contact (Pearman ei al. 2004). Rana sylvatica tadpoles allowed to consulIIe infected tadpole carcasses died sooner than did those exposed to infected carcasses but not allowed to eat them (Harp and Petranka 2006).

Larvae of Amb~)'stoma tigrinum nebnlosulil were also easily infected with ATV when allowed to eat tissue from dead, infected larvae, but they also were easily infected via contact with mucous from infected larvae or with a short "bump" with infected larvae (Brunner ei al. 2007). All of these modes of direct contact are common in amphibian larvae and it is likely that all of these behaviours contribute to ranaviral transmission in the wild. T'ransmission through indirect roules has also been demonstrated in the laboratory. Langdoll (1989) showed that ranaviruses conld survive in a laboratory for over 90 days. In addition, several studies have found that lanrae could become infected with rall(tvirus when exposed to water that previously housed infected larvae anel/or sediment from a ranavirus die-off site or when inoculated with ranavirus (Brunner et al. 2004; HaIV and Petranka 2006; Duffus et al. 2008; Brunner et al. 2(07), although ranavimses seem to decay in pond water (Brunner el al. 2007). Harp and Petranka (2006) found that the tadpoles exposed to water and sediment from a die-off site experienced only a low mortality rate, and were instead aclinically infected. They hypothesized that this may be a mode of maintaining infection in the population, as well as potentially moving it to other sites with migrating, infected amphibians. Spread of ranaviruses between sites may be clue to movement of water. sediment via fomites. or sublethally or aclinically infected animals (Harp and Petranka 2(06). Most understanding of transmission of ranavirns originates, however, from experiments in the laboratory, leaving Olle to extrapolate how the dynamics of transmission play out in a natural and more complex setting. For a discussion of long-distance, ant hropogenic spread of ranaviruses, see Section 2 "Taxonomy and Molecular Epidemiology".

7. Diagnosis The current routine techniques for diagnosing ranaviruses ill amphibians include immunohistochemistry, viral isolat iOll from tissues and cell culture, and ELISA and PCR. SlIblethal or aclinical infections lllay only be detectable by cell culture or PCR. Immunohistochemistry: Wax-embedded tissue sections can be labelled "vit h an Clnti-ranaviral immunohistochemical marker so as to visualize infection within tissues (see Cunning-ham et al. [2008] for a detailed description). Variations Oll this technique include immunofluorescence and iUlIllllllociccLron microscopy (Zupanovic et at. 1998b). Cell Culture: Rallaviruses can be grown tt'om fresh or frozen tissues in various fish (e.g. EPC and FHM), mammalian, or amphibian cell lines (Hengstberger et al. 1993) as long as those cells grow at ectothermic temperatures « 25°C). Often samples from amphibian tissues only show cytopathic effects after two or three passages (Brunnel~ ullpublished clata). The species of the cultured ranavirus can be identified by sequencing a portion of the major capsid protein gene using a technique described by Marsh et al. (2002). ELISA: Enzyme-Linked ImmunoSorbent Assay (ELISA) is used for detection of anti­ ranaviral antibodies in amphibian sera. Both Whittington et al. (1997) aud Zupanovic et aL (l998b) provided detailed descriptions of this technique. peR: Polymerase chain reactions (peR) IIsing primers designed to ampliry portions of the major capsid gene have become the most common method of detecting ranaviruses. For instance, the MCP4 and MCP5 primers described by Mao et al. (]996) amplify an approximately 500bp region of the Mep gene in all known ranavirLlses. Quantitative real­ time PCR reactions have also been developed (Mao et al. 1996; Brunner 2004). Galli et al. HDn~GWAY ET IlL: VIRAL AND BACTERHL DISEASES OF A;\IPIIIBL\:-./S 2975

(2006) provided a useful description of sample extraction and PCR procedures. Various tissues have been Llsed to detect rall

8. l\tlanagement Given recent declines in amphibian populations worldwide and the impact novel pathogens have had on naIve populations, it is essential to avoid spreading pathogens or artificially increasing rates of infection. Disinfection of equipmenr used in handling captive and wild amphibians anel effect ivc quarantine guidelines are key to effectively managing these risks. Since ranaviral disease has been listed by the OlE as a globally notifiable disease, the international legislative requirements will result in a greater focus on surveillance and quarantine for ranaviruses. Control Options: Control of ranaviruses within a site that is already infected may be particularly difficult given the possibility that aclillically infected animals may maintain infection in a popUlation (Brunner et al. 2004; Robert et al. 2007). There are no vaccines available for ranaviruses and, given the logistical difficulties and expenses associat.ed 'with developing and distIibuting a vaccine, it seems unlikely that one will be fortllcoming. Culling amphibian populatiollS would also be dilIicult given the secretive nature of' many amphibian species, and likely ineffective if transmission is not density dependent (Creer et al. 2008). Currently there are no known treatments for ranaviruses. The only method for their control, therefore, is to limit human-influenced spread of the pathogen. Disinfection: Whether working with captive or wild amphibians, it is essential to minimize the risk of amplifying transmission of pathogens or of exposing' animals to new strains. Much of the risk can be managed through carehll disinfection of potential fomites hoth between sites and between animals. At the level of the sire, it is important to disinfect waders, boots, boats, float tubes, nets, seines, traps, vehicle tyres and undercarriage, and any other equiplIlent tilal comes in contact with the water.

Before disinfecting equipment, it lIlust be scrubbed clean to permit all surfaces to contact the decontamination solution. Several common disinfectants (70% ethanol, 70% isopropyl alcohol, lO% household bleach) appear to be effective in inactivating ranavimses if applied liberally for sufficient time, and when used in conjullction with mechanical scrubbing; for IIlore detail see Brunner and Sesterhen (2001). In particlllal~ a dilute solution of bleach is effective, has broad spectrum, is inexpensive, and oxidizes quickly (Speare el aI. 2004; D. Green personal cOllllllunication). Ethanol (70%) is ef1ective against the fish ranavirus, EHNV (Lallgdoll 1989) and can inactivate ranavirnses if given sufficient time or if used to flame equipment (Brunner and Sesterhen 2001; Brunner unpublished data). Because ethanol is relatively expensive. it is generally used only on forceps, scissors, and other instruments. Quatermuy compounds are also effective and have the advantage of being less corrosive than bleach, but they require careful rinsing to remove soapy residues. Any disinfectant must be applied for the specified amount of time (Speare et af. 200<1) to be effective. Finally, if using a chemical disinfectant, the equipment call be rinsed with sterile wateI; thus lowering the potential for release of the chemical into the habitat and decreasing the wear on equipment. All instruments and tools thal come into contact with animals should be disinfected between each . Each animal should be handled with new, disposable gloves, and 2976 A1'.IPHIBL~ BIOLOGY gloves should be changed between each animal. A new or disinfected bag or container should be used to hold each animal individually. Collectively, these procedures will help lower contact rates between the animals and avoid a positive bias when tesling for prevalence of infection. In the laboratory, several other options are available for decontaminating equipment. Autoclaving or exposure to UV light are effective in killing viruses, again when the equipmcnt is first scrubbed and the method is applied for the specified amount of time (Speare et al. 2004). In addition, any water or other materials contacting captive animals must be disinfected, using bleach or autoclaving, before disposal. III commercial fi'og enterprizes, if water is circulated by pumps, potential ranaviruses can be killed by use of commercial UV sterilizers (minimullI cffective dose of UV is 2.6 x 104 uW.sec/crn2) which are effective at high flow rates and even up to 70% turbidity (Miocevic et al. 1992). Refer to Speare pi al. (2004) or Kast and I-Iauna (2008) for more details on disinfecting equipment. Note that ranavinlses arc more resistant than is the amphibian chytrid Batmchoch):lTiwn dendrobatidis: guidelines for killing this fungus may not be adequate for rallaVlrus. QllOWlIline Guidelines: There are several published quarantine guidelines intended to decrease the risk of introducing pathogens into a captivc setting or of releasing captive, infected animals. Detection of rall

9. Discllsslon Although ranaviruses have not been linked to catastrophic amphibian declines, Lhey can cause high levels of mortality ill affected amphibian populatiollS (CullninghallJ et al. 1996). Ranavirus call survive for long periods ill the environment under some conditions (Langdon 1989), they are multi-host pathogens (Schock et al. 2008), and there is little if any regulation on the movemem of amphibians around the globe, all of which increase lhe ability of ranavirllses to emerge in, and have an impact upon, amphibian populations. Given the myriad of other threats to amphibians and the l~lct that amphibians exist in increasingly fragmented populations and so may be less able to rebound after catastrophic mortalily, the potential population-level impacts of ranaviruses should llot be dismissed (Cunningham et rd. 2007a). For example, populations may be unable to recover from infection with Batrachoch),lriulII dendrobatidis (amphibian chytrid fungus), if mortality rates are further increased. Both regulation and enforcement to limit human-initiated movement of amphibian pathogens, includillg ranaviruscs, is imperative if there is to be cOllstraint UPOll the impact of emerging infectious diseases on these sensitive populations.

B. Frog Erythrocytic Virus Frog Erythrocytic Vinls (FEV) was discovered in poplliations of Rarw catesbeialla, R. clamitans and R. septentrionalis in Ontario, Canada (Gruia-Gray et 01. J 989; Gruia-Cray and Desser 1992). FEV is a large (up to 450 mIl in diameter), enveloped, double-stranded DNA vims of uncertain classification within the Iricloviridae. Viral inclusions in the cytoplasm of red blood cells arc seen by light microscopy of blood smears, and a large proportion of cells lIlay be infected. Infected red blood cells change shape from oval to spheroidal, and heavily infected frogs can become anaemic (Cruia-Gray et al. 1989; Gruia-Gray and Desser 1992). A survey showed that infection is more common ill juvenile bullfrogs (30% overall) than in adults (9%), and that il peaked ill Augllst/September (Gruia-Gray and Desser 1992). Infected juveniles were slightly less likely to be recaplured (4%) than were unint"ected juveniles (9%), suggesting that I he virus colllributed to I he mortality of young bullfrogs. FEV is transmitted between frogs by mosquitoes or midges, and is Hot traIlsmitted by watel~ oraily, or by leeches. Similar large virllses have been found in red blood cells of amphibians in Costa Rica, Brazil, South Africa, China and the United StaLes (Bernard d aI. ] 968; de Sousa and Weigl 1976; de Matos et al. 1995; Speare et al. 1991; Alves de Matos and Paperna 1993; \,Verner 1993). c. Lucke Tumour Herpesvirus Lucke tumour herpesvirus (LTHV) has been reported only from the , R(wa pipiens ill lhe United Slales (McKinnell and Carlson 1997). Recently LTHV has been classified as Rana herpesvirus 1 (RaHV-l) (Davison et al. 1999) in the family . Genomic studies indicated that Ral-{\!- 1 belongs to the fish virus lineage of the herpesvinls family rather than to the lineage populated by manmlalian and avian vill1ses (Davison el aI. 1999). This virus induces renal adenocarcilloma in R. j}/piens in the Cnited Stales; lhe tumour was well described by Lucke (l93!J). Its transmissible nature was recognized in 1938 and a virus was initially suggested as the cause due to the intranuclear inclusions (Lucke 1938), a surmise that was later confirmed. 2978 A~IPHIBIA:-J BIOLOGY

Vertical transnllSSlOl1 occurs with eggs becoming infected, but tUlI\ours are slow to develop. Clinical signs in adults are bloating, lethargy and death, which only occur when the tumour is large 01' has metast asized (Anvcr and Pond 1984). Single or multiple white nodules occur in the kidneys and grow into large masses. The tumour is an infiltrating and destructive adenocarcinoma Ol~ less often, it is orderly and adenomatous (Lucke 1931). Although the gross appearance of the tumour remains relatively llnchanged, there are significanl seasonal differences ill its microscopic appearance. Winter tumours display cytopathic characteristics associated with the presence of virus (enlarged nuclei with eosinophilic inclusions) whereas those in summer lack virus (McKinncll 1973). M etasl asis of the cancer also depends 011 temperature. Studies have shown that above 22°C virus replication does not occur and viral particles are not present ill the tumour (Anver and Pond 1984). Surveys of wild Rana plpiens for the Lucke tumour have found prevalences of up to 12.5% (McKinllcll 1969). Since the 1960s. howevel~ lhe prevalence of Lucke renal adenocarcinoma ill Minnesota has decreased. This is thought to be due to the population declines and reduced density of R. pijJiens (McKinuell el al. 1980).

D. Herpes-like Virus of Skin In flaly, up to 80% of a wild population of Rana dalmatina had epidermal vesicles associated with a herpes-like virus, but dead frogs were not fOllnd (Bennati et at. 1994).

E. Calicivirus A calicivirus was isolated £i'om two captive Ceratophr),s OT(lta found dead. Both had pneumonia, while one also hael oedema and the other had lymphoid hyperplasia (Smith et aL 1986).

F. Leucocyte Viruses Polyhedral cytoplasmic DNA virus was found in the cytoplasm of while blood cells of a Mexican Rana catesbrian([ that was lethargic and had small exudative ulcers (Briggs and Burton 1973). The large iridovirus fOllnd ill red blood cells of Bll/O JIl(lrit/lls in Costa Rica also was found in the cytoplasm of reticular cells ill the spleen (Speare et al. 1991).

III. BACTERIAL DISEASES

A. Bacterial Septicaemia ("Red Leg") Bacterial septicaemia ill amphibians has been termed "red leg" due to the cUEaneOils reddening that occurs on frogs' velltral thighs (Emerson and Norris 1905). This is an unfortunate name since many non-pathologists and non-veterinary cliniciallS appear to think that a frog with any erythema (redness) of the legs has a bacterial disease. It is important to realize that this is a very non-specific sign and it cannot be llsed to diagnose bacterial septicaemia. Bacterial septicaemia must be diagnosed by a combination of histopathology and bacterial culture. SOllle.: massive die-offs in the wild have been atlributed to bacterial septicaemia but the.:se diagnoses are dubious due to a lack of histopathological confirmation and testing for 01 her agents, particularly for ranaviruses and Batmchochytriuni denri)'obatidis, [he amphibian chyrricl (Green el at. 2002). Bacteria (including Aerolilonas hydmphlla) w'ere reported in die-offs in Illytes obstetricans in Ihe Pyrenees mountains ill Spain (Marquez et aL. 1995), in Rana muscosa in Califoruia (Bradford 1991) in Buro boreas boreas in Colorado (Carey 1993) and in tadpoles of Rana sylvatica in Rhode Island, USA (Nyman 1986). These bacteria can be cultured II'om frogs with ranaviral disease and , particularly when the allimals are collected dead (Cunningham el al. 1996; Berger et al. 1998). They can also be isolated frOlll the intestines of healthy amphibians and from the environment (Carr et at. 1976; Bird et al. 1983). For example, Aemtllonas hydmj)hila was ic)uncl in the inteslines of 4G% (102) of' 222 healthy leopard frogs (Hird et at. 1983). Bacteria lllay be prescnt in sick frogs as normal HE!llINGWAY ET ilL: \'lRA.L AND BACTERIAL DISE:\SES OF AMPHIBL\\'S 2979 residents, contaminants, or secondary infections. In addition, reddenillg of the legs can occur ill some amphibians showing clinical ranaviral disease and chytridiomycosis (Cunningham et al. 1996; Berger et al. 1999). During a die-off of Yosemite toads (Bllja mllOTlls) in the 1970s, three of 21 histologically examined toads had evidence of' aCHte septicaelllia, one of which also had chytridiomycosis, and all of which had been toe-clipped about two weeks before, which might have led to the illfection (Green and ShCl'lll

Bacterial septicaemia is, howevel~ a com mOll cause of outbreaks in captive amphibians. A range of bactelia IliaI' be inyolved including AerOlllonas ltylTOjJhila and other gram-negative bacteria or combinations of bacteria, sllch as PSl!lldomol1as spp., Pmte'lls spp., Flavobacterium sp. (Hubbard 1981; "laylor et aI. 1993; Olson et al. 1992). Recently, a new virulent subspecies, I!. h),dmphlla rarwe, was discovered in Ra'l1(l mgulosa f~lrmed in Thailand and dying from septicaemia (Huys et (It. 2003). With bacterial scpticaemia, gross pathological signs include pale skin, petechiation. ulcers, lethargy, oedema, ascites, pale livers, and haemorrhages in the internal organs. Histological examination may show degenerative myopathy and multiple foci of coagulative necrosis with clumps of bacteria. Variable results were obtained from transmission experiments - the disease usually required inoculation of tbe bacteria, or bath exposure and stress (Glorioso el al. 1974; Dusi 1949; SOIllsiri et al. ] 997) althollgh A. hJdrophila mlUle appeared to be more virulent than were other subspecies (Huys et al. 20(3). In most cases, disease probably OCCllrs secondarily to stress caused by poor husbandry such as overcrowding, diny conditions, trauma, temperature changes, and also after transport (Hubbard 1981; Glorioso et aL 1974).

Recent experimcntal ,"vork Ilsing A. h,wlrophila OIl the host, Xenojms laevis, has shown that the amphibian host's genetics is also importallt in determining susceptibility to pathogcllic bacteria (Barribeau et al. 2008). The survival ami growth of X. laevis tadpoles with different meDor histocompalability complexes (MHC), when exposed to A. h,)ldrophila, depended on their MIle haplotypcs with heterozygous tadpoles being intermediate between tadpoles with resistallt and susccplible MHC haplotypes.

B. Streptococcosis A nOll-haemolytic group B StrejJtococCliS caused an outbreak killing 80% of about 100,000 farmed bullfrogs (Rcwa catesbeirma) in Brazil (AlIlborski el (d. 1983). Septicaemia, necrotizing splenitis, and hepatitis with haemorrhages occlllTed in frogs. Viral cultures were negative. The outbreak was associated with overcrowding and stress. "Mortality due to a similar streptococcus occmred in R. cates/Je/ana beillg raised for consumption ill Uruguay (Mazzoni 2001) and in the United States (Mauel et al. 20(2). In the latter instance, the agen twas identified as StTejJtococCIlS iniae, a species that is a pathogen of fish and has zoonotic potential (Lehane and Rawlin 2001).

C. Chlamydiosis ChlmwydojJhila pnenmoniae caused chronic pneulllonia in a wild immuIlosuppressed frog, /vIixojJh)es itemtZls, in Australia (Berger et al. 1999) and in a captive colony of XenojJlls tropicalis in the United States (Reed et al. 2(00). C. pllellillOniae is all important human pathogen. A range of chlamydia 1 species infecting healthy amphibians h'Oll1 Switzerland were iclelltified by PCR (Blumer et of. 2007). Outbreaks of chlamydiosis in captive amphibians can result in fulminant, multisystemic infectioIlS with pyogranulornatus inflammation, causing moderate to high mortality rates in variolls species (Wilcke et al. 1983; I-Iowerth 1984; Honeyman et al. 1992).

D. Mycobacteriosis A llumber of atypical jWycobacteriuln species infect amphibians; j\1.. tuberculosis or lVi. bovis have not been reported. The only report of wild amphibians with mycobacteria was M. dzelonei 2980 A!>IPHIBIAN BIOLOGY subsp abscesslIs isolated fi'om four of 66 Bllfo marlnus and two of 86 B. gmnulosns in a slln:ey of Amazonian amphibians (Mok and Carvalho 1984). None of these animals had histopathological lesions, although experimental intraperitoneal inoculation of 29 toads resulted in the death of five animals frolll mycobacteriosis. Disease due to mycobacteria has been reported ollly in captive amphibians and occurs mainly ill imll1unocompromised animals. Several species have been reported. i\tJ. mar/null! was experimentally shown to cause a chronic granulolllatous non-lethal disease ill illllllullocornpetcnt leopard frogs (Ral/a pip/ens) whereas frogs iIllll1unocompromised with hydrocortisone developed all acute lethal disease (Ramakrishnan ()l al. 1997). AM. ulcemns­ like species £Iud IV!. leiflanrlii both caused outbreaks in captive XenoJms laevls (TrOll et af. 2004; Codfrey et al. 2007) while iv!. swlp,ai causeci an outbreak ill captive X. tropicab~\ (Chai e{ al. 2006). Infections prilllarily involve the skill, respiratory tract, or intestines. Frogs have been found with single, large tumour-like masses or with disseminated nodules throughout the internal organs. Organs such as liver, spleen, kidney. or testes lIlay become almost completely destroyed by the infection before the animal dies, usually with cachexia (Reichenbach-Klinke anci Elkan 1965). Early granulomas are composed of mostly epithelioid macrophages, which may progress to lorm encapsulated foci with dry caseous centres. Granulomas typically contain large numbers of acid-fast bacilli.

IV. REFERENCES

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