Abstract
Tularemia is a Holarctic zoonosis caused by the gamma proteobacterium Francisella tularensis, and is considered a vector-borne disease. In many regions, human risk is associated with the bites of flies, mosquitoes, or ticks. But, the biology of the agent is such that risk may be fomite related and large outbreaks can occur due to inhalation or ingestion of contaminated materials. Such well documented human risk factors suggest their role in the enzootic cycle as well. Many arthropods support the growth or survival of the agent, but whether arthropods (ticks in particular) are obligately required for the perpetuation of F. tularensis remains to be demonstrated. As with most zoonoses, our knowledge of the ecology of F. tularensis has been driven with the objective of understanding human risk. In this review, we focus on the role of the arthropod in maintaining F. tularensis, particularly with respect to longterm enzootic persistence.
Keywords: Francisella tularensis, tularemia, ecology, arthropods, natural foci, maintenance
“Tularemia is a specific infectious disease due to Bacterium tularense and is transmitted from rodents to man by the bite of an infected bloodsucking insect or by the handling and dissecting of infected rodents by market men or laboratory workers.” [42]
1. Introduction.
During plague surveillance in 1909, an epizootic in ground squirrels from Tulare County, California yielded bacteria that did not have the characteristic “safety pin” morphology of plague bacilli [96]. The bacterium was quickly cultivated and named “Bacterium tularense” [97]. Edward Francis of the U.S. Public Health Service, investigating an outbreak with human cases presenting with ulceration, lymphadenopathy, and fever in Utah residents bitten by deer flies incriminated “B. tularense” as the etiologic agent and proposed the name “tularemia” for the disease [42]. His comprehensive investigations included isolating the agent from flybitten humans, from jackrabbits, and from ground squirrels. Francis also provided experimental evidence for transmission of tularemia by the bites of deer flies, mouse lice and bed bugs [42]. Parker and colleagues isolated “B. tularense” from the Rocky Mountain spotted fever vector, Dermacentor andersoni [111], and the related American dog tick, D. variabilis, was incriminated as the source of a human infection in Minnesota [57], thereby formally incriminating ticks as a risk to humans other than the known deer flies. Francis requested that each state’s department of health report any case of tularemia and determined that >90% of >6000 tularemia case reports from 1924–1935 were associated with exposure to cottontail rabbits or hares [48], mainly as a result of market production of rabbit meat but also due to rabbit hunting. His specific mention of laboratory workers in his pithy summary of tularemia is because all 6 of the USPHS staff working on the newly recognized infection became infected [83], including Francis himself. The ease with which laboratory workers became infected by manipulating cultured bacteria or infected animals (the agent was easily propagated by serially transferring infected tissue homogenates to uninfected rodents) became notorious. British bacteriologists, after receiving reference cultures from Francis, became infected and decided to cease work with “B. tularense” because of its great hazard [138].
Very soon after Francis’ seminal work, Hachiro Ohara in Japan described 10 cases of an acute febrile disease that had been acquired during the skinning of wild rabbits [47]. The disease had been noted in the Fukushima area for 20 years but had not drawn attention by clinicians. Rabbit die-offs had been frequently noted by villagers. Definitive proof of rabbits as a source of infection was provided when Ohara’s wife volunteered to be exposed: she acquired tularemia after tissues from a dead rabbit were rubbed on the back of her hand. The clinical details provided by Ohara agreed “even in minor details with the details of tularemia” [47], sera sent by Ohara to Francis in the U.S. agglutinated American “B. tularense” strains, and fresh tissues from a Japanese case sent to Francis produced typical tularemic lesions in laboratory rodents.
Tularemia has had a long history in the former Soviet Union and much knowledge remains in their literature, sadly in Russian and thus less accessible to most Western workers. Pollitzer [125] provides a comprehensive review of the historical Soviet epidemiological literature and the reader is directed to that extraordinary book. To summarize from that authority, tularemia was first definitively identified in the Soviet Union when in 1929 Zarkhi, a clinical researcher in Sverdlosk, sent his own serum to McCoy at the U.S. Public Health Service. Zarkhi had suffered what he suspected was tularemia after necropsying guinea pigs inoculated with bubo contents from patients of a water rat-associated outbreak of a mystery disease. Pollitzer pointed out that the Soviet scientists retrospectively made the connection between outbreaks of “Siberian ulcer” in the 18th and 19th centuries (which was originally considered to represent cutaneous anthrax) and tularemia given the low (2%) mortality associated with some outbreaks of Siberian ulcer; the case fatality rate for anthrax would be much greater. Interpretation of historical outbreaks suggested that tularemia had long afflicted people throughout the vast Soviet Union from west to east and north to south, and thus the infection was very old and not recently introduced, for example, with the liberation by the Soviet fur industry of up to 80,000 muskrat from 1928–1945 [27]. Muskrats have been associated with tularemia outbreaks across the Holarctic.
2. Characteristics of the causative agent.
The genus Francisella comprises gram negative coccobacillary, non-spore forming, aerobic/microaerophilic bacteria in the Order Thiotrichales. Isolates with growth or biochemical characteristics similar to those from humans suffering from tularemia have been made from marine and freshwater fish, brackish water and other environmental sources, and ticks. Non-tularemia patients, often immunocompromised, have also yielded novel isolates that classically group with Francisella spp. Whole genome analyses demonstrate that there are at least a dozen distinct species [24]. Three subspecies of F. tularensis are currently recognized: tularensis, holarctica, and mediasiatica. Differences in distribution, ecology, biochemistry, and virulence led to the seminal classification of tularemia into distinct types [107]. Type A organisms (now known as F. tularensis tularensis) are prevalent in North America but not in Eurasia, are frequently transmitted by ticks, and may cause severe disease. Type B (F. tularensis holarctica; F. tularensis palaearctica of some older literature) causes episodic outbreaks (epizootics) in beavers, muskrats, and arvicoline rodents in either North America or Eurasia, may be isolated from water or soil, and may cause a milder disease [74,114]. F. tularensis subsp. mediasiatica was isolated from rodents in Central Asia but there are no reports of human cases. F. tularensis mediasiatica has apparently been isolated from diverse ticks from most metastriate genera as well as Ixodes persulcatus [149]. F. novicida has been considered a subspecies of F. tularensis but this bacterium is a distinct species [79]. F. novicida is an opportunistic pathogen, mainly of immunocompromised or elderly individuals exposed to environmental sources; isolates have only been made from salt or brackish water, never from animals or arthropods. However, it is highly virulent for experimental rodents, causing typical tularemia and can be acquired by feeding, survive transstadially, replicate within and be transmitted by the bites of D. andersoni [132].
Genetic typing methods confirmed the phenotypic distinctions and identified distinct lineages within Type A and Type B. Multilocus variable number tandem repeat analysis split the former into A.I. and A.II. Virtually all isolates from the eastern and central U.S. were A.I. and those from west of the 100th meridian were A.II. Whole genome sequencing demonstrates that there are 3 lineages of A.I.[17], with A.I.12 being the most widely distributed, suggesting an adaptive advantage over the others. Four major lineages are apparent across the Holarctic Type B isolates [144] with considerable diversity of subpopulations/genotypes even within endemic counties in Sweden [76]. Newer typing methods using single nucleotide polymorphisms are consistent with MLVA but lineages are designated slightly differently (e.g. A.I. is A1).
3. Evolution of Francisella.
The genus Wolbachia was erected by Marshall Hertig to describe bacteria that he and Burt Wolbach (who described the rickettsial etiology and pathology of Rocky Mountain spotted fever) found in the reproductive tract of Culex pipiens in 1924 [60]. Subsequently, a variety of endosymbiotic intracellular bacteria, most identified only by microscopy of stained smears of arthropod tissues, were considered “wolbachia”. Wolbachia persica was isolated from Argas arboreus ticks collected from an Egyptian heron rookery [140] based on its morphological similarity and presence in Malpighian tubules and reproductive tissues. W. persica was pathogenic for guinea pigs, mice and chicks, but not rats or rabbits. Molecular phylogenetic analyses clearly demonstrated that W. persica was not a rickettsial agent but was closely related to F. tularensis [102,103] and not to W. pipientis, the bacterium first identified by Hertig and Wolbach. W. persica has been formally reclassified in the genus Francisella [85]. Francisella-like endosymbionts (FLE) have been identified from most tick genera [32, 53, 71,103, 133, 137, 141, 142]. Early analyses suggested that tick-FLE associations were ancient [103] and thus F. tularensis may have evolved from FLEs. However, co-speciation between Dermacentor spp. and their FLEs was not detected [137] and critical virulence genes for F. tularensis such as type IV pili, LPS, and the type VI secretion system are present but have become pseudogenes in the FLEs [51]. Accordingly, FLEs were acquired by ticks from a virulent F. tularensis-like ancestor. If F. tularensis did not originate with ticks, the presumed central role of ticks for maintaining this infection requires critical analysis.
4. Epidemiology of tularemia.
Tularemia is endemic throughout most of Europe, northern and central Asia and North America. Type B is found in most of Europe, Asia and North America. Type A is found exclusively in North America; there is one report of its identification in Europe but this finding remains enigmatic. F. tularensis mediasiatica has been identified in limited portions of Central Asia. Although tularemia was not previously thought to be present in the southern hemisphere, in 2011 3 human cases were identified in Tasmania, and isolates made from ringtail possums (Pseudocheirus peregrinus) were determined by sequencing to group with Type B strains from Japan (sometimes referred to as biovar japonica)[33].
The clinical presentation of tularemia is varied, with 6 classical forms having been described: ulceroglandular, glandular, oculoglandular, oropharyngeal, typhoidal, and pneumonic. Such presentations generally relate to mode of acquisition; oculoglandular and oropharyngeal, for example, are the result of conjunctival contamination and ingestion, respectively. Ulceroglandular presentation, with ulceration at the site of an arthropod bite or other portal of infectious entry as well as proximal lymphadenopathy, or glandular presentation with regional lymphadenopathy, are the most common, comprising 50–65% of all American cases [40, 154]. The other common form, typhoidal, has an acute onset with sore throat, high fevers, chills, and enteric symptoms. No ulcer or portal of entry is evident, nor is there lymphadenopathy. Pneumonic tularemia may comprise primary inhalational tularemia with a respiratory portal of entry [129], exemplified by laboratory accidents [109] in the years before universal laboratory adoption of biosafety cabinets; and by large agriculturally-related outbreaks [28]. However, pleuropneumonia is a common finding in advanced typhoidal tularemia [8, 21,41], and in 10–20% of ulceroglandular cases. Pneumonic tularemia, presumably primary inhalational, is becoming increasingly reported in the U.S. and in some sites may be more common than ulceroglandular [117]. In Europe, ulceroglandular and glandular presentations comprise 50–70% of reported cases (e.g., [37, 92].
In Europe and across Russia and the Federation of Independent States (due to the seminal contributions of Soviet scientists, “Soviet Union” will be used herein), the epidemiology of tularemia is diverse, reflecting the diversity of the land, fauna, and people [61]. Mosquitoes are strongly associated with tularemia in Sweden [136]. Oropharyngeal tularemia is the most commonly reported form in some countries (Bulgaria, Kosovo, Norway, Serbia and Turkey), thought to be due to contamination of water or food by rodents. Hunting, mainly of hares, is the source of ulceroglandular or glandular infections in the Czech Republic, France, Germany, Slovakia, and Spain. Ticks are not considered as a common source of infection in Europe [61].
In the Soviet Union, 6 epidemiological scenarios were recognized [93]: (1) Meadow-field type, with the vole Microtus arvalis as amplifying host and D. reticulatus the vector and interepizootic reservoir. Risk to people was associated with agriculture and contamination of drinking water. (2) Steppe type, with diverse rodents and hares and the vector D. marginatus; agricultural activity and contaminated water. (3) Forest type, with the vector I. ricinus and its main subadult hosts (Myodes spp., Apodemus spp.); people were infected during hunting hare as well as by tick bites. (4) Floodland-swamp type. Arvicola terrestris, the water rat, was the critical amplifying host, with Dermacentor, Rhipicephalus and Ixodes ticks as vectors. Mosquitoes may also infect water rats. Humans become infected by hunting water rats. (5) Foothill-brook type. Water rats are also the main host, with Ixodes apronophorus as the vector. (I. apronophoros also plays an important role in maintaining Omsk hemorrhagic fever virus in the same sites; [80]). People get infected by the contamination of running water during the summer by water rats. (6) Desert river type. Hares and gerbils and R. pumilio are thought to maintain infection, with risk exclusively to hunters. These Eurasian epidemiologically-based scenarios demonstrate the possible great diversity of enzootic cycles that may characterize F. tularensis elsewhere.
5. Rabbit fever.
The perception that Type A tularemia was due to lagomorphs was largely the influence of Francis himself and also of William Jellison of the Rocky Mountain Laboratories, who compiled and interpreted the existing literature on tularemia biology in a seminal monograph [73]. Jellison argued that human risk and geographic distribution of North American tularemia was strongly associated with cottontail rabbits [75, 113]. Cottontail rabbits are very susceptible to infection by Type A, dying within 7 days, and are large enough animals to attract attention when there is an epizootic, making them good sentinels for transmission activity. Furthermore, because of their value as food, their populations were a focus of attention by local residents and by state game management divisions: 25,000,000 rabbits were killed annually with a value of $5,000,000 during the 1920s [59]. Then too, tularemia cases were common in the northcentral states where there was a tradition of rabbit hunting [155]. Tularemia incidence in the U.S. started to diminish in the 1960s [18], perhaps as a result of a loss in popularity of rabbits as food and of hunting in general.
In Japan, tularemia risk is mainly associated with rabbits [104]. 93% of 1358 cases analyzed from 1924–1994 were considered to have been due to rabbit exposure. In addition, a large spike in the incidence of tularemia from 1945–1955 was attributed to soldiers resettling in their homes eating rabbits as a source of protein in economically challenging postwar times; the incidence started falling dramatically with robust growth in the Japanese economy.
Rabbits or hares clearly have an important role in the epidemiology of tularemia, either as the direct (meat or hunting) or indirect (contamination of the environment by carcasses) source of human infection, or draw attention to epizootics by easily noted die-offs.
6. Ecology of tularemia: general comments.
Tularemia usually comes to our attention as a result of epizootics (spillover from local amplification with clusters of human cases) but endemic tularemia is underappreciated. The Midwestern U.S. reports a fairly constant (limited interannual variation, no more than 2 fold) number of cases each year (largely tick-transmitted), as does the island of Martha’s Vineyard, Massachusetts (about equal numbers of tick transmission and inhalation) [94]. Sweden also has constant annual numbers of mosquito-transmitted infection [36] and that country and Finland report more tularemia cases than any other [61]. In other countries, clinical reporting might be less of a priority and thus it is possible that other countries than Sweden sustain a similar degree of tularemia endemism. Reported cases, however, reflect only an effective epidemiological bridge from an enzootic cycle (endemic transmission) or epizootic (spillover from massive time-limited amplification of the enzootic cycle).
The classical theory of natural nidality [116] posits that most zoonotic agents exist in longstanding foci that comprise optimal physical (weather, geology) and biological (fauna, flora) associations and that humans only become aware of their existence when they intrude. A scenario for F. tularensis perpetuation may comprise a system (metapopulation) of small “natural foci”, each with a prevalent variant and mode of transmission. This fundamental tenet of the ecology of vector-borne agents asserts that such pathogens are perpetuated within specific sites, often on the order of tens of square meters in area, and that transmission may be continuously detected there for decades or longer. Humans become exposed by stumbling into such a natural focus or when transmission risk becomes more homogeneously distributed over a wide area due to many such foci coalescing as a result of local amplification and spillover. We identified one such natural focus on Martha’s Vineyard and demonstrated that infected American dog ticks were found mainly in a 260m diameter site along a longterm transect and that the most genetic variability of F. tularensis along the transect was to be found in ticks in that microfocus [54]. Great genetic diversity was apparent on Martha’s Vineyard as a whole, as much at the time as that described for all existing global isolates [52]; F. tularensis exists there as a metapopulation of isolated microfoci [55]. How such microfoci remain genetically discrete on an island of about 1000 square kilometers is unclear.
Mathematical models suggest that “The maintenance of indirectly transmitted infections do not require the very large host populations that are needed for directly transmitted microparasite infections” [95]. Given the virulence of F. tularensis for rodents or lagomorphs, with the majority of infected animals dying rapidly, some indirect factor (vector, fomite) is required for the bacterium to persist over ecological time. It seems unlikely that long term persistence is due to direct contact between infected and uninfected vertebrate hosts, although this mechanism certainly has the capacity to dramatically amplify transmission during an epizootic given that excreta can be infectious and cannibalism of animals dying from tularemia may result in new infections. Without a persistent reservoir in a vector or fomite, or chronic infection of a longer lived vertebrate, generation of susceptible hosts by immigration or recruitment would need to at least equal that of the removal of infected hosts through death.
Is there a main theme for perpetuation (ticks and rabbits, for example) with regional ecological differences being variations on that theme? Even with the limited literature, it is not a good assumption that the ecology of Type A is similar to that of Type B. Soviet scientists described at least 6 different kinds of natural foci: floodplain/swamp; meadow/field; forest; steppe; water/river; and desert floodplain [106]. F. tularensis Clades A.I. and A.II. are genetically and generally geographically distinct, suggesting that they occupy different ecological niches or were isolated during glaciation [78]. It may be that the diverse sublineages of Type A and Type B [81, 151] might each have differing requirements for maintenance. On the other hand, both A.I. and A.II. were isolated from lagomorphs in one discrete site in a Utah fly-transmitted outbreak, demonstrating co-circulation [118]. This finding does not preclude more than one kind of natural focus within a geographically discrete area.
6.1. Associations with arthropods.
Although tularemia is considered a vector borne disease, an obligate role for arthropods, hematophagous species in particular, in maintaining F. tularensis in nature is not axiomatic. Ticks are considered as main vectors and likely reservoirs for F. tularensis in North America and much of Eurasia [73, 116], but ticks have not been incriminated as relevant to the enzootic cycle in Scandinavia, which reports more tularemia cases than any other country in Europe (although this is due in part to the likely high proportion of cases that are reported). It is possible that many kinds of arthropods, perhaps even nonhematophagous species, may contribute the perpetuation of F. tularensis over the long term in natural foci.
6.2. Associations with vertebrates.
F. tularensis has been isolated or detected from a very large number of animals, including amphibia, birds, rodents, lagomorphs, carnivores, and ruminants [22, 67]. Virtually all of these are considered incidental hosts, although if they die of sepsis due to F. tularensis and there is an appreciable bacterial burden in their tissues, they may contribute to short term maintenance and perhaps over the long term if decomposing tissues can remain infectious under certain conditions. The carcass of a mouse dying of most of the main tularemia lineages may have 9–11 log colony forming units (cfu) within the spleen or liver [100]. Interestingly, rats (Rattus norvegicus) can recover from infection and viable bacteria may be recovered from their tissues for at least 2 weeks after recovery [30, 31] and their role as possible enzootic reservoirs should be critically examined given their global distribution and abundance. Other animals, such as the carnivores or raptors, are typically poorly susceptible to disease (seroconverting with infection) and are excellent sentinels given their scavenging and predator roles [15]. An exception is the domestic cat, which is commonly infected (as many as 12% are seropositive in some sites [91]), suffers disease, not infrequently fatal, and in fact serves as an occupational risk to their owners and to veterinarians [84]. Given the abundance of feral cats [87], at least in the U.S., their potential role in maintaining natural foci should be analyzed further.
Some evidence suggests the possibility that some strains (lineages) of F. tularensis are specifically associated with certain mammals. The prevalence of human cases in the U.S. overlaps with the distribution of cottontail rabbits [113], and Type A strains were most likely to have been isolated from these hosts [81]; A.I. strains came from eastern cottontails (Sylvilagus floridanus) and A.II. from desert cottontails (S. audubonii). However, there does not seem to be any specific relationship between a vertebrate species and lineages of Type B [124]. Of course, existing F. tularensis strains do not represent a random sampling and reflect convenience samples from clinical cases or those from outbreak investigations. Efforts should be made to isolate additional strains from a greater selection of vertebrate species before any conclusions can be made.
6.2.1. Type B ecology: driven by rodents?
Tularemia in Eurasia and non-rabbit or tick associated infection in North America seem to have a strong environmental basis, acquired from agricultural activities such as hay threshing; from water contaminated by muskrats or water voles; hunting hares; or during the trapping of furbearers [3, 61,116, 134, 145]. A large typhoidal (=pneumonic) tularemia outbreak in Castilla y Leon, Spain was associated with farm and harvest activities, as well as contact with voles [3]. A prior large outbreak in the same region had been due to hunting hares, and subsequent genetic analyses of strains isolated from both outbreaks demonstrated strong similarities [7]. The outbreak of 2007–2018 and a lesser one in 2014 coincided with irruptions of common voles, Microtus arvalis [89] in Castila y Leon. American, Soviet, and Swedish workers have long recognized harvest activities and rodent irruptions as major risks for tularemia [68, 77, 114]. Experimental studies with American voles suggested the possibility that some infected animals developed a chronic nephritis and bacteruria that could serve as a protracted source of environmental contamination [12], a finding that was confirmed for voles that were orally infected [108].
7. General comments on tularemia vector studies.
Rodents are exquisitely sensitive to infection by F. tularensis, dying within the week of a sepsis that is characteristically identified by gross lesions on necropsy [30]. Tularemic pathology includes prominent, often caseous lymphadenopathy and readily visible “pinpoint white spots” on the surface of the liver and spleen, representing necrotic foci with masses of bacteria. Thus, early transmission studies either allowed potential vectors to feed on a rodent, or homogenized vectors and inoculated the homogenates into rodents, then waited for a characteristic rapid death and easily scored gross pathology. Good confidence can be placed in these assays even today in the times of ultrasensitive molecular diagnostic methods. Definitive assays rely on recovery of the agent by cultivation, or its safer surrogate (necropsy of tularemic animals is hazardous and propagation in vitro is even more so), evidence of bacterial DNA by PCR. PCR, however, must be done with stringent contamination control to prevent false positives, and usually fails to discriminate viable bacteria from DNA remnants. Strong evidence for viability is thus presented with results from animal inoculation or cultivation but PCR or immunofluorescence methods may have other interpretations. Accordingly, studies from the older literature can be considered to have used sound diagnostic assays and should not be discounted due to their “age”. However, older experimental studies used challenge strains that were uncharacterized and even whether they comprised Type A or B is not clear; exceptions are [29, 64] who used strain “Sm” which is the current Type A standard, Schu.
There is much literature on field surveys for F. tularensis in vector arthropods but other than definitively establishing the presence of a transmission cycle, sometimes very little can be concluded from such data. Removal of hematophagous arthropods from a host rarely allows for any conclusive evidence of vector competence because infection may be present in freshly ingested blood as opposed to having been retained from a previous bloodmeal. Nest parasites such as mites or fleas or lice, of course, must frequently feed on a host and many do not survive long without a bloodmeal. The critical question for the enzootic cycle is whether bacteria remain viable within such arthropods, live or dead, in the absence of the host, implying that a new host acquiring them (or eating them, or becoming exposed to their products, such as “flea dirt”) could become infected. PCR is almost exclusively used today to detect microbial agents during vector surveys, but the specificity of the primer sets used for detecting F. tularensis varies. The great diversity of Francisella spp. that is now known may confound interpretation of some of the previously reported prevalences reported from tick surveys, particularly those that used PCR primers that have not been directly tested against newly recognized Francisella spp. [24].
7.1. Fleas.
During the first investigations of the biology of F. tularensis by McCoy and Chapin [97], fleas were implicated as maintenance vectors. Both “Ceratophyllus acutus” (Diamanus montanus) and C. fasciatus were experimentally infected by feeding on tularemic guinea pigs and ground squirrels, but infectivity for more than a day or two after feeding was not tested. In addition, although “100 fleas” removed from a guinea pig that had died of tularemia were placed in a clean cage with a healthy squirrel, resulting in death of the squirrel, it was not clear whether that squirrel acquired infection by flea bite or by ingesting groomed fleas. Of course, either mode may be effective in enzootic maintenance. Experimental evidence suggests that fleas (Xenopsylla cheopis and Diamanus montanus) may acquire bacteria from infected mice and retain viable infection for more than a month [128], but did not transmit by feeding. Earlier studies [115] with 3 additional fleas, including Pulex irritans, demonstrated survival for only a day and no transmission. Larval fleas fed cultivated F. tularensis could retain infection for no more than 3 days and did not become infected by feeding on dried blood that had been spiked with culture [62]. Surveys of diverse flea species demonstrated natural infection [58, 152 and others summarized in 135] but on the other hand, early surveys for plague in the western U.S., using the technique of inoculating flea homogenates into rodents, rarely found F. tularensis [5], suggesting that fleas were a very minor contributor to the maintenance of this infection, at least in the American West. Hence, the published information on the role of fleas as enzootic vectors remains inconclusive.
7.2. Lice.
The rabbit louse (Haemodipsus ventricosus) transmitted to experimental rabbits but transfer of lice from an infected animal to an uninfected animal needed to occur within 3 hours otherwise infection appeared to have been lost [45], although a few rabbits became infected with lice that had been held for 2–3 days. Francis was very careful to exclude the possibility that infection was due to contamination with secretions or excreta of dying rabbits by placing hair with lice from the dying donor onto naïve rabbits and placing the rabbit within newly cleansed trash cans. Briefer but similar experiments by Francis’ team using Polyplax serratus also demonstrated transmission even a week after lice had been removed from the infected hosts. Francis was careful to not state that infection was due to bites by the lice (recognizing that mice will groom and eat lice), but simply pointed out that mouse infestation led to transmission under conditions that excluded a healthy mouse’s contact with the excreta of infected mice. Price [126, 127] experimentally infected human body lice (Pediculus humanus corporis) by feeding them on rabbits that had intravenously received a large dose of cultivated F. tularensis just before serving as host, as well as a cohort infected by introcoelomic inoculation. Serial sections of infected lice were examined to determine the course of infection over time. Interestingly, there was relatively little multiplication of bacteria in those infected by feeding (ingestion of 6 log cfu and measurements of not much more than 6 log cfu days thereafter). Those inoculated with 3 logs cfu demonstrated 3 log multiplication within 4 days, with quick progression to mortality. Price suggested that when bacteria remained confined to the gut, lice were more likely to survive but that nutritional factors in the hemolymph allowed for rapid multiplication and toxicosis quickly leading to louse death. Given the host specificity of most lice, the fact that new hosts become infested only by very close contact (lice do not persist in fomites), and the very short life of lice in the absence of a host, at most lice can help to amplify infection during an epizootic but would not maintain the agent once all the hosts for that louse species died. Of course, the lice themselves would soon become locally extinct if their hosts were not present.
7.3. Bedbugs.
Bedbugs (Cimex lectularius) were fed on infected mice and guinea pigs, and 3 modes of transmission were confirmed by Francis and Lake [44]: (1) by interrupted feeding (bug removed from infected animal before repletion and allowed to reinfest a naïve animal); (2) by bite after as many as 71 days (infection by bite ensured by allowing bugs to feed on mouse tails; and (3) by allowing mice to eat bugs infected as many as 100 days previously. The possible role of cimicids or triatomines as potential interepizootic hosts has not been explored.
7.4. Flies.
Tularemia was first described as a nosological entity by Francis because of a deer fly transmitted outbreak in Utah. Using field collected Chrysops discalis, Francis successfully transmitted infection by the bite of flies that had fed for short durations (“interrupted feeding”) on an infected guinea pig or rabbit and hours to days later were fed on uninfected guinea pigs, which died of typical tularemia [46]. His team subsequently assayed flies that had fed on infected guinea pigs on a daily basis, injecting fly homogenates into uninfected guinea pigs. “Up to 5 days the flies remained constantly infected” but Francis argued that infection tended to become lost by day 10 after infection and thus there was likely no replication. Hence, flies were considered to be mechanical vectors. Pavlovsky [116] clearly recognized the vector role of tabanid flies and in fact equated their role in tularemia maintenance with their role in that for anthrax: that flies would aggregate on moribund animals and spread the infection by contaminated mouthparts and interrupted feeding on new hosts. Soviet workers incriminated numerous species in the genera Tabanus, Chrysops, Stomoxys, and Haematopota [135, cited in 49]. Interestingly, reports of fly transmitted tularemia are very rare other than in the American west, and indeed Jellison [72] went so far as to state that the only species of any importance as a vector was C. discalis. From our own work, F. tularensis DNA may rarely be found in C. vittatus in our Martha’s Vineyard site and we know of an ulceroglandular case acquired from a deer fly bite on Nantucket (unpublished). It is likely that fly-transmitted infection may be found in most endemic sites but that human ulceroglandular cases are automatically considered to be a result of tick bite in the absence of dermal exposure to contaminated materials.
7.5. Mosquitoes.
Philip and colleagues [122] first examined the possible transmission of F. tularensis by bite, using local species of Aedes as well as A. aegypti. Mosquitoes were infected by feeding on tularemic guinea pigs. No mosquito transmitted by bite during a second bloodmeal, but a small proportion did so after interrupted feeding (this was interpreted as mechanical transmission). Swatting infected mosquitoes onto the skin of guinea pigs also transmitted infection. The excreta deposited after an infectious bloodmeal was infectious when inoculated into guinea pigs. They also noted that F. tularensis survived in dead mosquitoes for at least 4 days, and speculated that this could serve as a means to contaminate bodies of water, reminiscent of Manson’s classic findings with filariasis [25]. Soviet workers regarded mosquitoes as tularemia vectors but of minor importance to the maintenance of natural foci compared to that of ticks and tabanids [116].
Mosquitoes are strongly implicated as vectors in Sweden, given that tularemic ulcers are most frequently found on the upper back, neck, and ears of case-patients [36], where mosquitoes are more likely to feed. In addition, the agent has been isolated from mosquitoes there [105], and mosquito larvae collected from endemic sites that were allowed to develop and emerge as adults in the laboratory contained F tularensis DNA [88]. Host seeking mosquitoes collected from endemic Swedish sites yielded 18 of 791 positive for F. tularensis holarctica DNA [147]; infection was detected in Culex, Aedes, Anopheles, and Coquilletidia spp. In a definitive experiment, second instar A. aegypti larvae were exposed to 7 log cfu of Type B, then washed and allowed to develop to adults. A quarter of the adult mosquitoes contained F. tularensis DNA, and of those that did, the homogenates from a third of them infected mice when intraperitoneally inoculated, demonstrating that virulent bacteria were transstadially passed [9]. Larval Culex quinquefasciatus readily fed on biofilms of F. tularensis holarctica, but their pupation was delayed and emergent adult mosquitoes were smaller than those feeding on the control dog biscuit slurry [90]. Additional studies are needed on the vectorial capacity of mosquitoes for F. tularensis, particularly to clarify the mode of transmission; to date studies have generally failed to transmit by bite and the leading hypothesis is that people become infected by swatting a feeding mosquito and contaminating their skin. Short lived antibody to mosquito salivary [86] or gut proteins might be sought in tularemia patients to further confirm mosquito transmission. Although experimental mosquito related transmission rates appear to be small, the sheer abundance of mosquitoes in nature would compensate for low probability events. Given the evidence that humans acquire infection from mosquitoes, it is a certainty that other animals do as well in enzootic sites.
The role of mosquitoes may be specific to some natural foci. Over 9000 mosquitoes were screened with negative results from a site in the Czech Republic where as many of 2% of host seeking ticks that were concurrently collected yielded F. tularensis isolates [69].
7.6. Mites.
Mesostigmatid mites (Hirstionyssus, Laelaps, Eulaelaps, Haemolaelaps) were found by Francis and Lake [45] and Soviet workers cited in [49] to be naturally infected by F. tularensis. Painstaking studies done by Cluff Hopla for his doctoral dissertation [63] demonstrated the likely role of hematophagous mites in maintaining F. tularensis. Using Ornithonyssus bacoti, the tropical rat mite, Hopla determined that protonymphs acquired infection from septic mice, bacteria were transstadially passed into the nonfeeding deutonymph, and could be transmitted by the adult mite to clean mice. Clear evidence of transovarial transmission was also provided, although by only about a fifth of the adult mites feeding on infected mice. Transmission was not by bite but rather required grooming and eating the mites by the mice. Assays for infection comprised both mouse inoculation as well as cultivation on glucose blood agar. Cultivation allowed for estimation of bacterial burdens, which on average were greater than 6 log cfu per mite even after “prolonged fasting”. Given the great diversity of blood feeding mites, some effort should be made to better describe the vector-pathogen associations in the laboratory and in nature.
7.7. Soft ticks.
Davis [29] determined that Ornithodoros turicata and O. parkeri could remain infected by F. tularensis for over 600 days, but failed to transmit infection by bite. Detailed studies of infected O. moubata, O. parkeri, O. hermsi, and O. turicata, including infection with a known Type A strain (Schu) found viable bacteria for 450 days and demonstrated viable F. tularensis in rectal secretions, coxal fluid, as well as transmission by bite [20]. Contamination by coxal fluid appeared to be the most likely means of transmission inasmuch as O. hermsi, which does not secrete liquid coxal fluid during feeding, was the least competent vector. No evidence of infection related mortality was reported, despite numerous bacteria colonizing virtually every tick tissue. The fact that soft ticks can maintain viable infection for such extended durations suggests that they may help maintain a tularemia natural focus where they are endemic (southern, southcentral, and western U.S.; central Asia).
7.8. Hard ticks
There are many American reports of the vector competence of the ixodid ticks Dermacentor variabilis, D. andersoni, D. parumapertus, Amblyomma americanum, and Ixodes scapularis were all competent for F. tularensis [2, 11, 64, 65, 66, 111, 123]. Soviet workers, particularly Petrov and Dunaeva [119] and Petrov [120, 121], cited in [10], demonstrated intense multiplication and survival of the agent as long as 700 days within D. reticulatus. Balashov [10] stated that ticks are “the most effective natural vector and reservoir” given the many demonstrations of transmission by feeding, intensive multiplication of the bacterium, long survival within ticks with no loss of bacterial viability or virulence, and frequent detection of infection in surveys of host seeking ticks. The multiyear life cycles of most ixodid ticks make them a logical candidate for longterm persistence of F. tularensis natural foci.
The competence of D. variabilis for F. tularensis was measured in two exemplary modern studies [130, 131] which set the standard for any future work. Realistic doses (100cfu) were used to infect mice. Two Type A (A1b, A2) and one Type B strains were compared. Experimental ticks were from a longstanding laboratory colony with precise provenance, and known to be specific pathogen free. Uninfected cohorts were generated from the same tick batches for comparison with the infected ones. Sample sizes were such that statistical comparisons were adequately powered. Assays for infection were definitive: cultivation of the agent from individual ticks. The methods were presented in such detail that the studies could be replicated by other laboratories. The experiments demonstrated that A2 strains caused nymphs to die quickly, but not adult ticks. Infection affected nymphs infected by all 3 strains in some way, either by reducing body size, attachment or feeding success. The A1b strain was not transmitted to mice by infected nymphs, and transmission was poor for A2 and B strains (8%−12% success). Mice could become infected by eating the infesting infected nymphs. Although adult D. variabilis never feed on rodents, this host restriction was overcome by confining ticks to capsules on mice and of those female ticks that fed and were shown to have contained infection, transmission occurred 58%−89% of the time. Accordingly, the competence of one characterized strain of D. variabilis differed depending on the infecting F. tularensis type, but all 3 types were transmitted by bite of adult ticks and 2 by that of nymphs. F. tularensis was inferred to have been transmitted within one day of attachment by infected ticks based on the observation that some mice were diseased within 4 days of repletion; this was calculated using a known prepatent period of 3 days, and a feeding duration of 7 days for female dog ticks.
Many surveys of host-seeking ticks have been published. As with many other tick borne infections, there is no standardization of assays; with PCR assays, specificity should be demonstrated to prevent detection of FLEs or environmental Francisella spp. Sample sizes are often such that confidence intervals around the estimated prevalence are very wide. Hence, it can be difficult to compare published prevalence estimates. Two very detailed surveys for F. tularensis infection in host-seeking ticks provide examples of what would be most informative. Nearly 8000 D. reticulatus were sampled from a natural focus in the Czech Republic during 1995–2013 [70]; 64 F. tularensis isolates were recovered by mouse inoculation for a minimum infection rate of 0.83%. The bacteriological gold standard is isolation of the agent. Our published [52,55] and unpublished observations of the Martha’s Vineyard natural focus during 2001–2011 comprise PCR detection in ticks (median of 1572 host seeking adult D. variabilis tested each year) with a median annual prevalence of about 3.1% (range 0–5.2). Two gene targets were used (fopA for the initial screen and tul4 for a confirmatory assay) and a large proportion of those samples with specific DNA were genotyped [52,55]. Detection of genetic material, however, does not establish viability.
7.8.1. Transovarial transmission.
The literature conflicts with respect to the inheritance of F. tularensis by ticks. Three reports [64, 65, 112] demonstrated inherited infection and that this infection would pass transstadially to the adult when larvae and nymphs were fed on uninfected hosts. Parker and Spencer [112] definitively demonstrated inheritance of the progeny of 2 of 15 female D. andersoni feeding on infected rabbits; the evidence comprised transmission by bite of larvae or nymphs. Another 6 of the 15 were suggestive of inheritance but typical infection (death of the host) was not demonstrable; infection was inferred only by transfer of splenic material from the rabbits fed on by the progeny to uninfected animals. Calhoun and Alford [23] found host seeking A. americanum larvae to be infected (by inoculating animals with homogenate pools). In contrast, Soviet workers suggest that any demonstration of transovarial infection was due to contamination of eclosed larvae by secretions of an infected female tick [121] and dismiss the possible contribution of inheritance by the tick as a means of F. tularensis perpetuation [116]. Bell [11] failed to demonstrate inheritance in D. variabilis. More recent analyses [50] did not find transovarial transmission from female D. reticulatus and I. ricinus, with bacteria appearing to die within previtellogenic oocytes. They noted that 17%−30% of all engorging female ticks died or did not lay eggs. It may be that the efficiency of the process may vary among strains of F. tularensis and could even be associated with tick genetic background (co-adaptation of vector and pathogen).
7.8.2. Paradox of fitness effects due to infection.
Philip and Jellison [123] first reported that ticks infected by the agent of tularemia were likely to die or fail to oviposit. A recent thorough analysis [130] clearly documents that infection of D. variabilis by Type A diminishes nymphal survival; infected nymphs were generally smaller and took twice as long to feed to repletion as uninfected nymphs. Interestingly, these negative fitness effects were not seen with adult dog ticks [131]. Type B-infected nymphal D. marginatus or D. variabilis die more rapidly than do uninfected ticks [130] and in fact only 2% of all D. marginatus feeding as larvae on infected animals developed to the adult stage [120, 121]. Host seeking adult D. variabilis from our Martha’s Vineyard site that died faster in captivity were more likely to contain F. tularensis DNA than those living longer [56]. Diminished longevity of ticks would impact reproduction, which implies that vector competence for Type A should be selected against, yet, at least in our Martha’s Vineyard natural focus, dog ticks containing F. tularensis DNA have been found every year for more than 15 years (unpublished). Like Rickettsia rickettsii, which is also generally a lethal infection for D. andersoni [102], the continued demonstration of infected tick vectors in the field suggests that despite F. tularensis negatively affecting fitness, there is some as yet unidentified compensatory effect that maintains the enzootic vector-pathogen relationship. For example, F. tularensis genotypes or lineages might be specifically coadapted to local tick populations and the elegant experiments of Reese et al. [130, 131] should be repeated using diverse D. variabilis colonies and with A. americanum, the two main zoonotic vectors for Type A.
7.8.3. “Allergic klendusity”.
During vector competence studies of D. variabilis, Bell [11] noted that a rabbit fed upon by F. tularensis infected ticks failed to become infected. That rabbit had previously been fed on by uninfected ticks, and he speculated that sensitization interfered with transmission. In a subsequent experiment, it was found that rabbits previously fed on by D. andersoni (usually larval infestation) were half as likely to be infected by F. tularensis infected ticks [13]. Bell designated this “allergic klendusity” (“disease escaping ability”) and that it was due to anti-tick immunity, referring to Trager’s classic experiments [150]. This interference was manifested at the portal of entry, working for the two possible modes of transmission, viz., by bite of infectious tick or by contamination of the bite site with tick feces containing F. tularensis as the tick is feeding. He also suggested that such a mechanism might serve to limit natural epizootics. This paper serves as the seminal observation that is the basis for current efforts in anti-tick vaccines and their promise for protecting against tick-borne infection.
7.9. Diverse experimental arthropods.
Advances in our understanding of and development of arthropod models for innate immunity have led to some interesting infection models of F. tularensis. Drosophila [101, 153], dubia roaches [34], and caterpillars (Galleria mellonella, [6,148]; Bombyx mori [143]) have been experimentally infected by inoculation of cultivated F. tularensis, typically with dose dependent mortality that was more pronounced at mammalian temperatures than arthropod (lower) temperatures, although B. mori survived for at least a week. Antimicrobial peptides such as those in the imd/relish pathway appear to be activated and prevent overwhelming sepsis; flies with that pathway knocked out succumb rapidly to infection [101]. Melanization was inhibited in B. mori inoculated with live F. tularensis but not with dead bacteria, suggesting some active bacterial response or secretion inhibits innate immunity. F. tularensis mutants with critical virulence genes (as determined for mammalian infection) also survived longer, suggesting that at least some known virulence factors apply to both mammals and arthropods. The new experimental hosts confirm what has been known since Francis’ first investigations: that F. tularensis has an extremely wide arthropod host range to include acarines, dipterans, lepidopterans, hemipterans, anoplurans, and siphonapterans and thus the infection should not be considered to be limited to solely vector species.
7.10. Aquatic invertebrates.
Shrimp or snails could retain viable organisms for 20 days [99], and indeed, invertebrates were first described as contributing to F. tularensis survival within water by Soviet scientists: Pavlovsky [116] states that the “tularemia microbe…may be found in the bodies of… mollusks, crabs and crayfish, water bug larvae…” Crayfish have been associated with human infection and F. tularensis apparently infects them [4], suggesting that additional surveys of aquatic invertebrates using modern methods are warranted in known natural foci.
8. Are vectors really required for maintenance?
Although 10–100 colony forming units of Type A are sufficient to produce a lethal infection in most mice with most F. tularensis strains when delivered by aerosol, and 1000 cfu is a typical LD50 for parenteral inoculation [146], LD50 is 6 log cfu for oral infection (gavage). Mice survived oral infection with 4 log cfu [82], suggesting that eating materials contaminated with F. tularensis (via excreta on food, grooming ectoparasites, cannibalizing moribund animals) could maintain transmission during epizootics and perhaps even over the long term within natural foci (e..g, by eating infected starved bed bugs or soft ticks, vide supra). Cannibalism of moribund cagemates is well known as a mode of transmission for Type A in the laboratory [110] as well as Type B [108]. Of particular interest is the possibility that voles became partially immune due to low level infection resulting from cannibalism of tularemic carcasses and that this immunity allows survival of the vole during subsequent infection, increasing the probability for shedding in the excreta [12]. Such immunity suggests a means of regulating the duration of epizootics and for the development of a new endemic focus.
Water-borne tularemia was first described by Karpoff and Antonoff [77], in their description of an outbreak related to drinking unboiled brook water; 43 hay-harvesters had evidence for hyperaemic oral mucosa, tonsils, or conjunctiva. Brook water readily yielded isolates of F. tularensis when inoculated into guinea pigs. In the U.S., cold waters contaminated by muskrat and beaver repeatedly yielded isolates of F. tularensis [74, 114]. Infected carcasses contaminated water and stored in the cold provided tissues that infected animals after two weeks; naturally contaminated mud remained infectious as long as 10 weeks [114]. Surface water and sediment yielded indisputable DNA sequence evidence of contamination with Type B in Swedish endemic sites, even in years with little epidemiological activity [19]. On the other hand, Type B held in lake water for 120 days failed to kill mice at a dose ten times the typical LD50 for that Type B strain [146], implying a loss of virulence that was not protected by the presence of high nutrient levels or freeliving protozoa. About half of rodents immersed in contaminated water became infected with exposure to as few as 100–1000 cfu/mL[116], which seems like heavy contamination but the spleen alone of a mouse dying of tularemia may have 10 log cfu [100]; Pavlovsky [116] estimates that a single dead rodent could infect 500,000 liters of water. Indeed, many have speculated that environmental persistence depends on continual contamination of the environment by dead animals. The persistence of F. tularensis in non-aquatic environments has received little attention; the bacterium has been lyophilized in a protein matrix and remained viable for 4 years in ampules stored on a desktop [98] suggesting the possibility for longterm persistence in natural foci. We speculated that a key factor in the endemic pneumonic tularemia focus of Martha’s Vineyard, in which landscapers comprise a major risk group [38], is the exposure of soils there to oceanic salt sprays [16] that would promote the viability of contaminating bacteria.
Bacterial endobiosis with free-living amoebae or other cyst-forming protozoa could serve to contaminate the environment with viable bacteria for a longer duration than if the bacteria were present in an extracellular or naked form. Although F. tularensis is said to be environmentally resistant, the naked bacteria are fragile and do not survive in the laboratory for more than 2–3 weeks in spring water or saline [16]; in another study, though, Type B survived 70 days in tap water at 8°C [39]. F. tularensis infects amoebas and ciliates in the laboratory [1, 14, 35] and can enter a viable but noncultivatable state [39]. Viable but nonculturable states might imply the possibility of longterm persistence in the environment with reversion to replicating, infectious bacteria.
9. Future directions for research on tularemia ecology.
Some questions will be very difficult to answer, given the difficulty in finding longstanding natural foci and the inability to experimentally manipulate conditions in the field. How long does infection persist in carcasses or remnants thereof when placed within suitable substrate? Does survival vary according to site physiography or even more specific microhabitat requirements (salinity, soil acidity or other chemical attribute)? The classification of F. tularensis as a U.S. federal Select Agent (of interest to biodefense and hence any possession or manipulation is highly regulated by the government)(https://www.selectagents.gov/regulations.html) makes even the most basic of deliberate field experiments impossible to undertake in the U.S. It would be virtually impossible to bury fresh infected mouse carcasses or infected ticks in a field site (a site that was known to be endemic and using a F. tularensis strain derived from that site) and sample them periodically to determine the duration of bacterial viability because of fears that they might be hijacked for nefarious purposes.
In the U.S., much attention has been focused on ticks; can Type A be enzootic where there are few ticks, as demonstrated for Type B in Sweden? Can a natural focus disappear with continued application of acaricides to reservoirs or to the environment? Long years of antitularemia campaigns by the Soviets rarely attacked just the ticks but relied on human vaccination, rodent elimination and general sanitation [125] but failed to eliminate natural foci.
In this review, we argued that our knowledge of the ecology of tularemia is incomplete mainly because past studies have focused on the zoonotic condition as opposed to identifying the requirements for maintenance. Of course, human exposure (the subject of epidemiology) may provide clues to the mode of perpetuation (ecology) but this is not axiomatic. Zoonotic infections may exist in sites with no implied human risk in the absence of an effective epidemiological “bridge”. Even the very concept that F. tularensis is an obligate vector-borne infection remains to be proven: its ecology may be more like that of Coxiella burnetii, the agent of Q fever (with diverse modes of perpetuation), than of Rickettsia spp.
ACKNOWLEDGMENTS.
Our work on tularemia was supported by National Institutes of Health grants R21AI 53411 and R01 AI064218. We are currently supported by NIH R01 AI 130105 and R01 AI 137424, by the Rainwater Foundation, and by a gift from Catherine C. Lastavica. This is a contribution of the New England Regional Biosafety Laboratory.
REFERENCES
- 1.Abd H, Johansson T, Golovliov I, Sandstrom G, and Forsman M. 2003. Survival and growth of Francisella tularensis in Acanthamoeba castellanii. Appl. Environ. Microbiol 69:600–606 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 2.Allred DM, Stagg GN, Lavender JF. 1956. Experimental transmission of Pasteurella tularensis by the tick, Dermacentor parumapertus. The Journal of Infectious Diseases 99:143–145. [DOI] [PubMed] [Google Scholar]
- 3.Allue M, Ruiz Sopeña C, Gallardo MT, Mateos L, Vian E, Garcia MJ, Ramos J, Berjon AC, Viña MC, Garcia MP, Yanez J, Gonzalez LC, Munoz T, Andres C, Tamames S, Ruiz C, Gómez LA, Iglesias LA, Castrodeza J. Tularemia outbreak in Castilla y Leon, Spain, 2007: an update. 2008. Eurosurveillance 13:1–3. [PubMed] [Google Scholar]
- 4.Anda P, Segura del Pozo J, Díaz García JM, Escudero R, García Peña FJ, López Velasco MC, et al. 2001. Waterborne outbreak of tularemia associated with crayfish fishing. Emerg Infect Dis 7:575–82 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 5.Anonymous. 1941. Tularemia Infection found in Fleas from Prairie Dogs in Wyoming. Public Health Reports 56 (30):1521 [Google Scholar]
- 6.Aperis G, Fuchs BB, Anderson CA, Warner JE, Calderwood SB, Mylonakis E. 2007. Galleria mellonella as a model host to study infection by the Francisella tularensislive vaccine strain. Microbes Infect 9:729–34 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 7.Ariza-Miguel J, Johansson A, Fernández-Natal M, Martínez-Nistal C, Orduña A, Rodríguez-Ferri EF, Hernández M, Rodríguez-Lázaro D. Molecular Investigation of Tularemia Outbreaks, Spain, 1997–2008. Emerg Infect Dis 20:754–761. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 8.Avery FW, Barnett TB. Pulmonary tularemia: a report of five cases and consideration of pathogenesis and terminology. Am Rev Respir Dis 1967;95:584–91. [DOI] [PubMed] [Google Scholar]
- 9.Bäckman S, Näslund J, Forsman M, Thelaus J. 2015. Transmission of tularemia from a water source by transstadial maintenance in a mosquito vector. Scientific Reports 5:7793. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 10.Balashov YS. 1972. Bloodsucking ticks (Ixodoidea)-vectors of disease in man and animals. Miscellaneous Publications of the Entomological Society of America 8:161–376. [Google Scholar]
- 11.Bell JF. 1945. The Infection of Ticks (Dermacentor variabilis) with Pasteurella tularensis. The Journal of Infectious Diseases 76:83–95. [Google Scholar]
- 12.Bell JF, Stewart SJ. 1975. Chronic shedding and tularemia nephritis in rodents: possible relation to occurrence of Francisella tularensis in lotic waters. J. Wildl. Dis 11:421–430 [DOI] [PubMed] [Google Scholar]
- 13.Bell JF, Stewart SJ, Wikel SK. 1979. Resistance to tick-borne Francisella tularensis by tick-sensitized rabbits: allergic klendusity. Am J Trop Med Hyg 28:876–80 [PubMed] [Google Scholar]
- 14.Berdal BP, Mehl R, Meidell NK, Lorentzen-Styr AM, Scheel O. 1996. Field investigations of tularemia in Norway. FEMS Immunol. Med. Microbiol 13: 191–195. [DOI] [PubMed] [Google Scholar]
- 15.Berrada ZL, Goethert HK, Telford SR. 2006. Raccoons and Skunks as Sentinels for Enzootic Tularemia. Emerg Infect Dis 12:1019–21. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 16.Berrada ZL, Telford SR. 2011. Survival of Francisella tularensis tularensis in brackish water. Arch Microbiol 193:223–226. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 17.Birdsell DN, Johansson A, Öhrman C, Kaufman E, Molins C, Pearson T, et al. 2014. Francisella tularensis subsp. tularensis Group A.I, United States. Emerging Infectious Diseases 20:861–865 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 18.Boyce JM. 1975. Recent Trends in the Epidemiology of Tularemia in the United States. The Journal of Infectious Diseases 131:197–9. [DOI] [PubMed] [Google Scholar]
- 19.Broman T, Thelaus J, Andersson AC, Bäckman S, Wikström P, Larsson E, Granberg M, Karlsson L, Bäck E, Eliasson H, Mattsson R, Sjöstedt A, Forsman M. 2011. Molecular detection of persistent Francisella tularensis subspecies holarctica in natural waters. International Journal of Microbiology 2011:851946. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 20.Burgdorfer W, Owen CR. 1956. Experimental studies on argasid ticks as possible vectors of tularemia. The Journal of Infectious Diseases 98:67–74. [DOI] [PubMed] [Google Scholar]
- 21.Burke DS. 1977. Immunization against Tularemia: Analysis of the Effectiveness of Live Francisella tularensis Vaccine in Prevention of Laboratory-Acquired Tularemia. J Infect Dis 135:55–60. [DOI] [PubMed] [Google Scholar]
- 22.Burroughs AL, Holdenried R, Longanecker DS, Meyer KF. 1945. A Field Study of Latent Tularemia in Rodents with a List of All Known Naturally Infected Vertebrates. The Journal of Infectious Diseases 76:115–9. [Google Scholar]
- 23.Calhoun EL, Alford HI. 1955. Incidence of Tularemia and Rocky Mountain Spotted Fever among Common Ticks of Arkansas. Am J Trop Med Hyg 4:310–317 [DOI] [PubMed] [Google Scholar]
- 24.Challacombe JF, Petersen JM, Gallegos-Graves LV, Hodge D, Pillai S, Kuske CR. 2017. Whole-Genome Relationships among Francisella Bacteria of Diverse Origins Define New Species and Provide Specific Regions for Detection. Appl Environ Microbiol 83:e02589–16. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 25.Chernin E. 1983. Sir Patrick Manson’s Studies on the Transmission and Biology of Filariasis. Rev Infect Dis 5:148–66. [DOI] [PubMed] [Google Scholar]
- 26.Conlan JW, Chen W, Shen H, Webb A, KuoLee R. 2003. Experimental tularemia in mice challenged by aerosol or intradermally with virulent strains of Francisella tularensis: bacteriologic and histopathologic studies. Microb Pathog 34:239–48 [DOI] [PubMed] [Google Scholar]
- 27.Danell K 1978. Ecology of the Muskrat in Northern Sweden National Swedish Environment Protection Board, Solna: (SNV PM 1043), 157 pp [Google Scholar]
- 28.Dahlstrand S, Ringertz O, Zetterberg B. 1971. Airborne Tularemia in Sweden. Scandinavian Journal of Infectious Diseases 3:7–16. [DOI] [PubMed] [Google Scholar]
- 29.Davis GE. 1940. Bacterium tularense: Its persistence in the tissues of the argasid ticks Ornithodoros turicata and O. parkeri. Public Health Reports 55: 676–680. [Google Scholar]
- 30.Downs CM, Coriell LL, Pinchot GB, Maumenee E, Klauber A, Chapman SS, Owen B. 1947. Studies on tularemia. I. The comparative susceptibility of various laboratory animals. J Immunol 56:217–228 [PubMed] [Google Scholar]
- 31.Downs CM, Buchele L, Edgar EP. 1949. Studies on pathogenesis and immunity in tularemia. I. The pathogenesis of tularemia in the white rat. J Immunol 63:117–133. [PubMed] [Google Scholar]
- 32.Duron O, Binetruy F, Noël V, Cremaschi J, McCoy KD, Arnathau C, et al. 2017. Evolutionary changes in symbiont community structure in ticks. Molecular Ecology 26:2905–21. [DOI] [PubMed] [Google Scholar]
- 33.Eden J-S, Rose K, Ng J, Shi M, Wang Q, Sintchenko V, et al. 2017. Francisella tularensis ssp. holarctica in Ringtail Possums, Australia. Emerg Infect Dis 23:1198–201. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 34.Eklund BE, Mahdi O, Huntley JF, Collins E, Martin C, Horzempa J, Fisher NA. 2017. The orange spotted cockroach (Blaptica dubia, Serville 1839) is a permissive experimental host for Francisella tularensis. Proc W Va Acad Sci 89: 34–47 [PMC free article] [PubMed] [Google Scholar]
- 35.El-Etr SH, Margolis JJ, Monack D, Robison RA, Cohen M, Moore E et al. Francisella tularensis type A strains cause the rapid encystment of Acanthamoeba castellanii and survive in amoebal cysts for three weeks postinfection. Appl. Environ. Microbiol 75, 7488–7500 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 36.Eliasson H, Bäck E. 2007. Tularaemia in an emergent area in Sweden: An analysis of 234 cases in five years. Scandinavian Journal of Infectious Diseases 39:880–9. [DOI] [PubMed] [Google Scholar]
- 37.Faber M, Heuner K, Jacob D, Grunow R. 2018. Tularemia in Germany—A Re-emerging Zoonosis. Front Cell Infect Microbiol 8: 40. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 38.Feldman KA, Stiles-Enos D, Julian K, Matyas BT, Telford SR 3rd, Chu MC, Petersen LR, and Hayes EB. 2003. Tularemia on Martha’s Vineyard: seroprevalence and occupational risk. Emerg. Infect. Dis 9:350–354 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 39.Forsman M, Henningson EW, Larsson E, Johansson T, Sandstrom G. Francisella tularensis does not manifest virulence in viable but non-culturable state. FEMS Microbiol Ecol 2000;31:217–24 [DOI] [PubMed] [Google Scholar]
- 40.Foshay L. 1940. Tularemia: a summary of certain aspects of the disease including methods for early diagnosis and the results of serum treatment. Medicine 1940;19:1. [Google Scholar]
- 41.Tularemia Foshay L.. Annu Rev Microbiol 1950;4:313–30 [DOI] [PubMed] [Google Scholar]
- 42.Francis E. 1921. The occurrence of tularemia in nature as a disease of man. Public Health Reports 36:1731–1738.19314784 [Google Scholar]
- 43.Francis E, Lake GC. 1921. Experimental Transmission of Tularaemia in Rabbits by the Rabbit Louse, Haemodipsus ventricosm (Denny). Public Health Reports 36:1747–1753. [Google Scholar]
- 44.Francis E, Lake GC. 1922. Transmission of Tularæmia by the Bedbug, Cimex Lectularius. Public Health Reports 37:83–115.19314809 [Google Scholar]
- 45.Francis E, Lake GC. 1922. Transmission of Tularaemia by the Mouse Louse, Polyplax serratus (Burm.). Public Health Reports 37:96–101 [Google Scholar]
- 46.Francis E, Mayne B. 1922. Experimental Transmission of Tularemia by flies of the species Chrysops discalis. US Pub. Health Serv Hyg Lab Bul 138:8–16. [Google Scholar]
- 47.Francis E, Moore D. 1926. Identity of Ohara’s disease and tularemia. J Am Med Assoc 86:1329–32. [Google Scholar]
- 48.Francis E. 1937. Sources of Infection and Seasonal Incidence of Tularaemia in Man. Public Health Reports (1896–1970) 52:103–13 [Google Scholar]
- 49.Gelman AC. 1961. Ecology of tularemia. Pp 89–108 in Studies in Disease Ecology, ed. May JM. Hafner Publishing Company, NY. 613pp. [Google Scholar]
- 50.Genchi M, Prati P, Vicari N, Manfredini A, Sacchi L, Clementi E, Bandi C, Epis S, Fabbi M. 2015. Francisella tularensis: No Evidence for Transovarial Transmission in the Tularemia Tick Vectors Dermacentor reticulatus and Ixodes ricinus. PLoS ONE 10(8): e013359. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 51.Gerhart JG, Auguste Dutcher H, Brenner AE, Moses AS, Grubhoffer L, Raghavan R. 2018. Multiple Acquisitions of Pathogen-Derived Francisella Endosymbionts in Soft Ticks. Genome Biol Evol 10:607–15. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 52.Goethert HK, Shani I, Telford SR. 2004. Genotypic Diversity of Francisella tularensis Infecting Dermacentor variabilis Ticks on Martha’s Vineyard, Massachusetts. J Clin Microbiol 42:4968–73. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 53.Goethert HK, Telford SR. 2005. A New Francisella (Beggiatiales: Francisellaceae) Inquiline within Dermacentor variabilis Say (Acari: Ixodidae). J Med Entomol 42:502–5 [DOI] [PubMed] [Google Scholar]
- 54.Goethert HK, Telford SR. 2009. Nonrandom Distribution of Vector Ticks (Dermacentor variabilis) Infected by Francisella tularensis. PLoS Pathogens 5:e1000319. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 55.Goethert HK, Saviet B, Telford SR. 2009. Metapopulation structure for perpetuation of Francisella tularensis tularensis. BMC Microbiology 2009;9:147. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 56.Goethert HK, Telford SR. 2011. Differential mortality of dog tick vectors due to infection by diverse Francisella tularensis tularensis haplotypes. Vector Borne Zoonotic Dis 11:1263–1268. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 57.Green RG. 1931. The Occurence of Bacterium tularense in the eastern wood tick, Dermacenter variabilis. Am J Epidemiol 14:600–13. [Google Scholar]
- 58.Green RG, Evans CA. 1938. Role of fleas in the natural transmission of tularemia. Minnesota Wild Dis Invest April:25–28 [Google Scholar]
- 59.Henderson J, Craig EL. 1932. Economic Mammalogy Thomas Charles C., Springfield, Illinois. 397 pp. [Google Scholar]
- 60.Hertig M. 1936. The Rickettsia, Wolbachia pipientis (gen. et sp.n.) and Associated Inclusions of the Mosquito, Culex pipiens. Parasitology 28:453–86. [Google Scholar]
- 61.Hestvik G, Warns-Petit E, Smith LA, Fox NJ, Uhlhorn H, Artois M, et al. 2015. The status of tularemia in Europe in a one-health context: a review. Epidemiology & Infection 143:2137–60. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 62.Hood AM, Molyneux DH. 1970. Survival of Pasteurella Tularensis in Flea Larvae. J Med Entomol 7:609–11. [DOI] [PubMed] [Google Scholar]
- 63.Hopla CE. 1951. Experimental Transmission of Tularemia by the Tropical Rat Mite. The American Journal of Tropical Medicine and Hygiene 1:768–783. [DOI] [PubMed] [Google Scholar]
- 64.Hopla CE. 1953. Experimental studies on tick transmission of tularemia organisms. Am J Hyg 58:101–118. [DOI] [PubMed] [Google Scholar]
- 65.Hopla C. 1955. The multiplication of tularemia organisms in the lone star tick. American Journal of Epidemiology 61:371–380. [DOI] [PubMed] [Google Scholar]
- 66.Hopla CE. 1960. The transmission of tularemia organisms by ticks in the southern states. Southern Medical Journal 53:92–7. [DOI] [PubMed] [Google Scholar]
- 67.Hopla CE. 1974. The ecology of tularemia. Adv Vet Sci Comp Med 18:25–53. [PubMed] [Google Scholar]
- 68.Hornfeldt B. 1978. Synchronous population fluctuations in voles,small game,owls,and tularemia in northern Sweden. Oecologia 32:141–152 [DOI] [PubMed] [Google Scholar]
- 69.Hubálek Z, Halouzka J. 1997. Mosquitoes (Diptera: Culicidae), in Contrast to Ticks (Acari: Ixodidae), Do Not Carry Francisella tularensis in a Natural Focus of Tularemia in the Czech Republic. J Med Entomol 34:660–3. [DOI] [PubMed] [Google Scholar]
- 70.Hubalek Z, Rudolf I. 2017. Francisella tularensis prevalence and load in Dermacentor reticulatus ticks in an endemic area in Central Europe. Medical and Veterinary Entomology 31:234–239. [DOI] [PubMed] [Google Scholar]
- 71.Ivanov IN, Mitkova N, Reye AL, Hübschen JM, Vatcheva-Dobrevska RS, Dobreva EG, et al. 2011. Detection of New Francisella-Like Tick Endosymbionts in Hyalomma spp. and Rhipicephalus spp. (Acari: Ixodidae) from Bulgaria. Appl Environ Microbiol 77:5562–5. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 72.Jellison WL. 1950. Tularemia geographical distribution of “deerfly fever” and the biting fly, Chrysops discalis. Public Health Rep 65:1315–50. [PubMed] [Google Scholar]
- 73.Jellison WL. 1974. Tularemia in North America, 1930–1974 University of Montana, University of Montana Foundation, 276 pp [Google Scholar]
- 74.Jellison WL, Kohls GM, Butler WJ, Weaver JA. 1942. Epizootic Tularemia in the Beaver, Castor canadensis, and the Contamination of Stream Water with Pasteurella tularensis. American Journal of Hygiene 36:168–82. [Google Scholar]
- 75.Jellison WL, Owen C, Bell J, Kohls GM. 1961. Tularemia and animal populations. Wildlife Diseases 17:1–22. [Google Scholar]
- 76.Karlsson E, Svensson K, Lindgren P, Byström M, Sjödin A, Forsman M, et al. 2013. The phylogeographic pattern of Francisella tularensis in Sweden indicates a Scandinavian origin of Eurosiberian tularaemia. Environmental Microbiology 15:634–45. [DOI] [PubMed] [Google Scholar]
- 77.Karpoff SP, Antonoff NI. 1936. The Spread of Tularemia through Water, as a New Factor in Its Epidemiology. J. Bacteriol 32:243–258. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 78.Keim P, Johansson A, Wagner DM. 2007. Molecular Epidemiology, Evolution, and Ecology of Francisella. Annals of the New York Academy of Sciences 1105:30–66. [DOI] [PubMed] [Google Scholar]
- 79.Kingry LC, Petersen JM. 2014. Comparative review of Francisella tularensis and Francisella novicida. Front Cell Infect Microbiol [DOI] [PMC free article] [PubMed] [Google Scholar]
- 80.Kharitonova N, Leonov Y. 1985. Omsk Hemorrhagic Fever: Ecology of the Agent and Epizootiology New Dehli: Amerind Publishing Company. [Google Scholar]
- 81.Kugeler KJ, Mead PS, Janusz AM, Staples JE, Kubota KA, Chalcraft LG, et al. 2009. Molecular Epidemiology of Francisella tularensis in the United States. Clin Infect Dis 48:863–70. [DOI] [PubMed] [Google Scholar]
- 82.KuoLee R, Zhao X, Austin J, Harris G, Conlan JW, Chen W. 2007. Mouse model of oral infection with virulent type A Francisella tularensis. Infect Immun 75:1651–60 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 83.Lake GC, Francis E. 1922. Tularæmia Francis 1921: VII. Six Cases of Tularæmia Occurring in Laboratory Workers Public Health Reports; 37:392–413. [Google Scholar]
- 84.Larson MA, Fey PD, Hinrichs SH, Iwen PC. 2014. Francisella tularensis Bacteria Associated with Feline Tularemia in the United States. Emerg Infect Dis 20:2068–71. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 85.Larson MA, Nalbantoglu U, Sayood K, Zentz EB, Cer RZ, Iwen PC, et al. 2016. Reclassification of Wolbachia persica as Francisella persica comb. nov. and emended description of the family Francisellaceae. International Journal of Systematic and Evolutionary Microbiology 66:1200–5. [DOI] [PubMed] [Google Scholar]
- 86.Londono-Renteria B, Cardenas JC, Cardenas LD, Christofferson RC, Chisenhall DM, Wesson DM, et al. 2013. Use of Anti-Aedes aegypti Salivary Extract Antibody Concentration to Correlate Risk of Vector Exposure and Dengue Transmission Risk in Colombia. PLOS ONE 8:e81211. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 87.Loss SR, Will T, Marra PP. 2013. The impact of free-ranging domestic cats on wildlife of the United States. Nat Commun 4:1396. [DOI] [PubMed] [Google Scholar]
- 88.Lundström JO, Andersson A-C, Bäckman S, Schäfer ML, Forsman M, Thelaus J. 2011. Transstadial Transmission of Francisella tularensis holarctica in Mosquitoes, Sweden. Emerg Infect Dis 17:794–9. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 89.Luque-Larena JJ, Mougeot F,Arroyo B, Vidal MD, RodrõÂguez Pastor R, Escudero R, et al. 2017. Irruptive mammal host populations shape tularemia epidemiology. PLoS Pathog 13:e1006622. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 90.Mahajan UV, Gravgaard J, Turnbull M, Jacobs DB, McNealy TL. 2011. Larval exposure to Francisella tularensis LVS affects fitness of the mosquito Culex quinquefasciatus. FEMS Microbiol Ecol 78:520–30 [DOI] [PubMed] [Google Scholar]
- 91.Magnarelli L, Levy S, Koski R. 2007. Detection of antibodies to Francisella tularensis in cats. Research in Veterinary Science 82:22–6. [DOI] [PubMed] [Google Scholar]
- 92.Mailles A, Vaillant V. 2014. 10 years of surveillance of human tularaemia in France. Eurosurveillance 19:20956. [DOI] [PubMed] [Google Scholar]
- 93.Maksimov AA. 1960. Natural Nidi of Tularemia in the U.SSR Medical Literature Publishing House, Moscow-Leningrad, 261 pp. [Google Scholar]
- 94.Matyas BT, Nieder HS, Telford SR. 2007. Pneumonic Tularemia on Martha’s Vineyard. Annals of the New York Academy of Sciences 1105:351–77. [DOI] [PubMed] [Google Scholar]
- 95.May RM. 1984. Ecology and population biology. Pp 152–166 in Tropical and Geographic Medicine, eds Warren KS, Mahmoud AA. McGraw-Hill, NY. 1175 pp. [Google Scholar]
- 96.McCoy G. A plague-like disease of rodents. Public Health Bulletin 1911:53–71. [Google Scholar]
- 97.McCoy GW, Chapin CW. Further Observations on a Plague-Like Disease of Rodents with a Preliminary Note on the Causative Agent, Bacterium tularense. The Journal of Infectious Diseases 1912;10:61–72. [Google Scholar]
- 98.Miller RP. 1946. Viability of dried Bacterium tularense. Publ Health Reports 61:1081–1085. [PubMed] [Google Scholar]
- 99.Mironchuk YV, Mazepa AV. 2002. Viability and virulence of Francisella tularensis subsp. Holarctica in water ecosystems (experimental study). Zh Mikrobiol Epidemiol Immunobiol 2:9–1 [PubMed] [Google Scholar]
- 100.Molins CR, Delorey MJ, Yockey BM, Young JW, Sheldon SW, Reese SM, et al. 2010. Virulence Differences Among Francisella tularensis Subsp. tularensis Clades in Mice. PLOS ONE 5:e10205. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 101.Moule MG, Monack DM, Schneider DS. 2010. Reciprocal analysis of Francisella novicidainfections of a Drosophila melanogaster model reveal host-pathogen conflicts mediated by reactive oxygen and imd-regulated innate immune response. PLoS Pathog 6:e1001065. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 102.Niebylski ML, Peacock MG, Fischer ER, Porcella SF, Schwan TG. 1997. Characterization of an endosymbiont infecting wood ticks, Dermacentor andersoni, as a member of the genus Francisella. Appl Environ Microbiol 63:3933–40. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 103.Noda H, Munderloh UG, Kurtti TJ. 1997. Endosymbionts of ticks and their relationship to Wolbachia spp. and tick-borne pathogens of humans and animals. Appl Environ Microbiol 63:3926–32. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 104.Ohara Y, Sato T, Homma M. 1996. Epidemiological analysis of tularemia in Japan (yato-byo). FEMS Immunology & Medical Microbiology 13:185–9. [DOI] [PubMed] [Google Scholar]
- 105.Olin G. 1942. Occurrence and mode of transmission of tularemia in Sweden. Acta Pathologica, Microbiologica et Immunologica Scandinavica 19: 220–247. [Google Scholar]
- 106.Olsufiev NG. 1977. Results and perspectives of the study of natural foci of tularemia in USSR. Med Parazitol (Mosk) 46:273–82. [PubMed] [Google Scholar]
- 107.Olsufiev NG, Emelyanova OS, Dunayeva TN. 1959. Comparative Study of Strains of B. tularense in the Old and New World and their Taxonomy. J Hyg, Epidemiol, Microbiol & Immunol 3:138–49. [PubMed] [Google Scholar]
- 108.Olsufjev NG, Shlygina KN, Ananova EV. 1984. Persistence of Francisella tularensis McCoy et Chapin tularemia agent in the organism of highly sensitive rodents after oral infection. J Hyg Epidemiol Microbiol Immunol 28:441–54. [PubMed] [Google Scholar]
- 109.Overholt EL, Tigertt WD, Kadull PJ, Ward MK, David CN, Rene RM, et al. 1961. An analysis of forty-two cases of laboratory-acquired tularemia: Treatment with broad spectrum antibiotics. The American Journal of Medicine 30:785–806. [DOI] [PubMed] [Google Scholar]
- 110.Owen CR, Buker ER. 1956. Factors involved in the transmission of Pasteurella tularensis from inoculated animals to healthy cagemates. J Infect Dis 99:227–233 [DOI] [PubMed] [Google Scholar]
- 111.Parker RR, Spencer RR, Francis E. 1924. Tularæmia: XI. Tularæmia Infection in Ticks of the Species Dermacentor Andersoni Stiles in the Bitterroot Valley, Mont. Public Health Reports 39:1057–73.19314929 [Google Scholar]
- 112.Parker RR, Spencer RR. 1926. Hereditary transmission of tularemia infection by the wood tick, Dermacentor andersoni Stiles. Public Health Reports 41:1403–140719315042 [Google Scholar]
- 113.Parker RR, Jellison WL. 1945. Rodents, Rabbits and Tularemia in North America: Some Zoological and Epidemiological Considerations The American Journal of Tropical Medicine and Hygiene s1–25:349–62. [Google Scholar]
- 114.Parker R, Steinhaus E, Kohls G, Jellison W. 1951. Contamination of natural waters and mud with Pasteurella tularensis and tularemia in beavers and muskrats in the northwestern United States. Bull Natl Inst Health 193:1–161. [PubMed] [Google Scholar]
- 115.Parker DD. 1958. Attempted Transmission of Pasteurella tularensis by three Species of Fleas. Journal of Economic Entomology 50: 724–726. [Google Scholar]
- 116.Pavlovsky E. 1966. Natural nidality of transmissible diseases Urbana: Univeristy of Ilinois Press; 261 pp [Google Scholar]
- 117.Pedati C, House J, Hancock-Allen J, Colton L, Bryan K, Ortbahn D, et al. 2015. Notes from the Field: Increase in Human Cases of Tularemia--Colorado, Nebraska, South Dakota, and Wyoming, January-September 2015. MMWR Morb Mortal Wkly Rep 64:1317–8. [DOI] [PubMed] [Google Scholar]
- 118.Petersen JM, Carlson JK, Dietrich G, et al. 2008. Multiple Francisella tularensis subspecies and clades, tularemia outbreak, Utah. Emerg Infect Dis 14:1928. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 119.Petrov VG, Dunaeva TN. 1955. Relationship between infection of ixodid ticks and the course of tularemia in animal donors. Vopr Kraev Obshch Eksp Parazitol 9:153–161. [Google Scholar]
- 120.Petrov VG. 1960. Experimental study of Dermacentor marginatus Sulz. and Rhipicephalus rossicus Jak. et K. Jak. ticks as vectors of tularemia. J Parasitol 46:877–84 [PubMed] [Google Scholar]
- 121.Petrov VG. 1962. Concerning transovarial transmission of the tularemia agent in Dermacentor marginatus Schulz. Ticks. Med Parazitol Bolezn 31:62–66. [PubMed] [Google Scholar]
- 122.Philip CB, Parker RR. 1932. Experimental transmission of tularemia by mosquitoes. Public Health Reports 47:2077–2088.19315370 [Google Scholar]
- 123.Philip CB, Jellison WL. 1934. The American Dog Tick, Dermacentor variabilis, as a Host of Bacterium tularense. Public Health Reports 49:386–92. [Google Scholar]
- 124.Pilo P. 2018. Phylogenetic Lineages of Francisella tularensis in Animals. Front Cell Infect Microbiol 8:258. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 125.Pollitzer R. 1967. History and incidence of tularemia in the Soviet Union: a review Institute of Contemporary Russian Studies, Fordham University. [Google Scholar]
- 126.Price RD. 1956. The Multiplication of Pasteurella tularensis in Human Body Lice. American Journal of Hygiene 63:186–197. [DOI] [PubMed] [Google Scholar]
- 127.Price RD. 1957. A microscopic study of Pasteurella tularensis in the human body louse. Parasitology 47:435–46 [DOI] [PubMed] [Google Scholar]
- 128.Prince FM, McMahon MC. 1946. Tularemia: Attempted Transmission by Each of Two Species of Fleas: Xenopsylla cheopis (Roths.) and Diamanus montanus (Baker). Public Health Reports 61:79–85. [PubMed] [Google Scholar]
- 129.Pullen RL, Stuart BM. 1945. Tularemia: analysis of 225 cases. J Am Med Assoc 129:495–500. [Google Scholar]
- 130.Reese SM, Dietrich G, Dolan MC, Sheldon SW, Piesman J, Petersen JM, et al. 2010. Transmission Dynamics of Francisella tularensis Subspecies and Clades by Nymphal Dermacentor variabilis (Acari: Ixodidae). The American Journal of Tropical Medicine and Hygiene 83:645–52. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 131.Reese SM, Petersen JM, Sheldon SW, Dolan MC, Dietrich G, Piesman J, et al. 2011. Transmission Efficiency of Francisella tularensis by Adult American Dog Ticks (Acari: Ixodidae). J Med Entomol 48:884–90. [DOI] [PubMed] [Google Scholar]
- 132.Reif KE, Palmer GH, Crowder DW, Ueti MW, Noh SM. 2014. Restriction of Francisella novicida Genetic Diversity during Infection of the Vector Midgut. PLoS Pathogens 10:e1004499. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 133.Reinhardt C, Aeschlimann A, Hecker H. 1972. Distribution of Rickettsia-like microorganisms in various organs of an Ornithodorus moubata laboratory strain (Ixodoidea, Argasidae) as revealed by electron microscopy. Zeitschrift Fur Parasitenkd 39:201–209 [DOI] [PubMed] [Google Scholar]
- 134.Reintjes R, Dedushaj I, Gjini A, Jorgensen TR, Cotter B, Lieftucht A, D’Ancona F, Dennis DT, Kosoy MA, Mulliqi-Osmani G, Grunow R, Kalaveshi A, Gashi L, Humolli I. 2002. Tularemia outbreak investigation in Kosovo: case control and environmental studies. Emerg. Infect. Dis 8:69–73 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 135.Romanova VP, Bojenko VP, Yakolev MG. 1955. Studies of the natural nidus of the water meadow type of tularemia. In Natural Nidi of Human Diseases and Regional Epidemiology State Publishing House of Medical Literature (Medgiz), Leningrad [Google Scholar]
- 136.Rydén P, Björk R, Schäfer ML, Lundström JO, Petersén B, Lindblom A, et al. 2012. Outbreaks of Tularemia in a Boreal Forest Region Depends on Mosquito Prevalence. J Infect Dis 205:297–304. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 137.Scoles GA. 2004. Phylogenetic Analysis of the Francisella-like Endosymbionts of Dermacentor Ticks. J Med Entomol 41:277–86. [DOI] [PubMed] [Google Scholar]
- 138.Simpson WM. 1929. Tularemia: History, Pathology, Diagnosis and Treatment Hoeber, Univ Minnesota Press [Google Scholar]
- 139.Steinhaus E 1946. Insect Microbiology Ithaca, NY: Comstock Publishing Company [Google Scholar]
- 140.Suitor EC, Weiss E. 1961. Isolation of a Rickettsialike Microorganism (Wolbachia persica, n. sp.) from Argas persicus (Oken). The Journal of Infectious Diseases 108:95–106. [DOI] [PubMed] [Google Scholar]
- 141.Sun LV, Scoles GA, Fish D, O’Neill SL. 2000. Francisella-like endosymbionts of ticks. Journal of Invertebrate Pathology 76:301–3. [DOI] [PubMed] [Google Scholar]
- 142.Sutakova G, Rehacek J. 1991. Symbiotic microorganisms (endocytobionts) in Dermacentor reticulatus ticks, p. 41–43. In Dushabek F, Bukva V eds., Modern Acarology, vol. 2. Academia, Prague, Czech Republic [Google Scholar]
- 143.Suzuki J, Uda A, Watanabe K, Shimizu T, Watarai M. 2016. Symbiosis with Francisella tularensis provides resistance to pathogens in the silkworm. Sci. Reports 6:31476. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 144.Svensson K, Granberg M, Karlsson L, Neubauerova V, Forsman M, Johansson A. 2009. A Real-Time PCR Array for Hierarchical Identification of Francisella Isolates. PLOS ONE 4:e8360. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 145.Syrjala H, Kujala P, Myllyla V, Salminen A. 1985. Airborne transmission of tularemia in farmers. Scand. J. Infect. Dis 17:371–375 [DOI] [PubMed] [Google Scholar]
- 146.Thelaus J, Andersson A, Mathisen P, Forslund AL, Noppa L, Forsman M. 2008. Influence of nutrient status and grazing pressure on the fate of Francisella tularensis in lake water. FEMS Microbiol Ecol 67: 69–80 [DOI] [PubMed] [Google Scholar]
- 147.Thelaus J, Andersson A, Broman T, Bäckman S, Granberg M, Karlsson L, Kuoppa K, Larsson E, Lundmark E, Lundström JO, Mathisen P, Näslund J, Schäfer M, Wahab T, Forsman M. 2014. Francisella tularensis subspecies holarctica occurs in Swedish mosquitoes, persists through the developmental stages of laboratory-infected mosquitoes and is transmissible during blood feeding. Microb Ecol 67:96–107 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 148.Thelaus J, Lundmark E, Lindgren P, Sjödin A, Forsman M. 2018. Galleria mellonella Reveals Niche Differences Between Highly Pathogenic and Closely Related Strains of Francisella spp. Front. Cell. Infect. Microbiol 8:188. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 149.Timofeev V, Bakhteeva I, Titareva G, Kopylov P, Christiany D, Mokrievich A, et al. 2017. Russian isolates enlarge the known geographic diversity of Francisella tularensis subsp. mediasiatica. PLOS ONE 12:e0183714. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 150.Trager W. 1939. Acquired immunity to ticks. J. Parasitol 25:57–78 [Google Scholar]
- 151.Vogler AJ, Birdsell D, Price LB, Bowers JR, Beckstrom-Sternberg SM, Auerbach RK, et al. 2009. Phylogeography of Francisella tularensis: Global Expansion of a Highly Fit Clone. Journal of Bacteriology 191:2474–84. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 152.Volfrez AA, Kolpakov SA, Flegontoff AA. 1934. The role of ectoparasites in the tularaemic epizootic of the ground squirrels. Rev Microbiol Epidemiol Parasitol 13:103–116. [Google Scholar]
- 153.Vonkavaara M, Telepnev MV, Ryden P, Sjostedt A, Stoven S. 2008. Drosophila melanogaster as a model for elucidating the pathogenicity of Francisella tularensis. Cell. Microbiol 10: 1327–1338 [DOI] [PubMed] [Google Scholar]
- 154.Weber IB, Turabelidze G, Patrick S, Griffith KS, Kugeler KJ, Mead PS. 2012. Clinical Recognition and Management of Tularemia in Missouri: A Retrospective Records Review of 121 Cases. Clin Infect Dis 55:1283–90. [DOI] [PubMed] [Google Scholar]
- 155.Yeatter RE, Thompson DH. 1952. Tularemia, Weather, and Rabbit Populations. Tularemia, weather, and rabbit populations. Illinois Natural History Survey Bulletin 25: 351–382. [Google Scholar]
