Introduction
- Top of page
- Summary
- Introduction
- Methods
- Results
- Discussion
- Acknowledgements
- References
Between 1925 and 1929, plains bison (Bison bison bison) were relocated from Wainwright Buffalo Park in central Alberta, Canada, to the newly created Wood Buffalo National Park (WBNP) to relieve overcrowding at Wainwright (the history of the park was reviewed by Carbyn, Oosenbrug & Anions 1993; Fuller 2002). Over 6000 bison were shipped although many were reported to have perished on route or were euthanized upon arrival (Carbyn et al. 1993; p. 27). The plains bison mixed with the 1500 indigenous wood bison (Bison bison athabascae), and by 1934 the population numbered approximately 12 000 bison. Bovine brucellosis (Brucella abortus) and tuberculosis (Mycobacterium bovis) were discovered in WBNP in the 1950s. The two pathogens were probably introduced with the bison from Wainwright National Park.
Bovine tuberculosis and brucellosis each have the potential to reduce survival and fecundity in bison (reviewed by Tessaro 1987, 1989), have significant economic consequences for the domestic cattle and bison ranching industries (e.g. Animal, Plant and Food Health Risk Assessment 1998), and are seen as the main impediment to further recovery of a once endangered species bison in northern Canada (Gates, Chowns & Reynolds 1994; RENEW 2001). Further, the presence of these pathogens may have played a significant role in the decline of the bison population of WBNP dropping from approximately 11 000 bison in 1970 to less than 2500 at the end of the 1990s (e.g. Joly 2001).
The prevalence of these pathogens in bison in WBNP has not been evaluated in a systematic manner. Previously, prevalence levels were determined during bison slaughter operations (Choquette et al. 1961, 1978; Fuller 1962) or on opportunistically sampled bison (Tessaro et al. 1990). These estimates of prevalence were questioned during public hearings on disease management in the late 1980s (e.g. Ferguson 1989); in particular whether these data were representative of the bison populations in WBNP (Ferguson & Burke 1994). Further, if transmission of either pathogen is density-dependent, prevalence may have declined in response to the sustained and substantial decline in numbers. This would be an important factor to consider in managing these pathogens, as if it could be shown that prevalence is density-dependent then partial culls of the population might be a viable management action for disease control. Alternatively, if prevalence is insensitive to bison density, more drastic management actions would be necessary for disease eradication. Dobson & Meagher (1996) proposed a nonlinear, density-dependent relationship between bison numbers and Brucella abortus prevalence. Rodwell, Whyte & Boyce (2001) found that tuberculosis prevalence in African buffalo (Syncerus caffer) did not covary with population size among regions in Kruger National Park, South Africa. It is not known if prevalence of either pathogen is a function of density or population size in bison.
Herein, we present the results of tuberculosis and brucellosis testing of bison in WBNP during February and March of 1997–1999. Our objective was to examine age- and sex-related trends in prevalence, as well as to determine if prevalence varied among three populations of various sizes within WBNP as an indication of a possible relationship between density and prevalence. Further, we discuss previous estimates of prevalence in an alternate examination of possible pathogen–density relationships.
Methods
- Top of page
- Summary
- Introduction
- Methods
- Results
- Discussion
- Acknowledgements
- References
Wood Buffalo National Park is approximately 44 000 km2 in size, and straddles the border between the Province of Alberta and the North-west Territories (60° N, 112° W). Aspects of the WBNP environment relevant to bison ecology are described in detail in Carbyn et al. (1993).
Bison in WBNP are spatially distributed as a metapopulation, with five main populations (sensuWells & Richmond 1995): Garden River, Delta, Hay Camp, Nyarling River and Little Buffalo (Joly 2001). Bison were captured for testing in the Nyarling River (females only), Hay Camp and Delta populations. Bison densities at the start of the study varied dramatically among our three study areas: Nyarling River, 0·011 bison km−1; Hay Camp, 0·124 bison km−1; and Delta, 0·162 bison km−1 (Joly 2001). Bison capture and handling protocols were described in detail in Joly (2001). Briefly, adult males too large to be slung under the helicopter were darted from the air using carfentanil and xylazine hydrochloride (Haigh & Gates 1995). Bulls were re-immobilized after 72 h to determine the results of the caudal fold test for tuberculosis. In February and March of 1997 and 1998, female and juvenile bison were captured with a net-gun fired from a Hughes 500D helicopter (Helicopter Wildlife Management, Salt Lake City, Utah). Bison were held in captivity for 72 h, after which the results of the caudal fold test were determined. Adult (> 3 years) and sub-adult (1–2 years) animals were kept in individual pens, while calves (< l year) were paired to reduce isolation stress. A long-acting neuroleptic, Clopixol-Acuphase, was administered to keep the bison calm during captivity (Ebedes 1992). Second-cut alfalfa hay or alfalfa cubes were provided for food, and fresh snow was provided for water. After 72 h in the corral, the bison were immobilized with carfentanil and xylazine hydrochloride in order to read the results of the caudal fold test for tuberculosis. In 1998, the xylazine was reversed using tolazoline. Naltrexone hydrochloride was used to reverse the carfentanil, and bison were released in a manner that encouraged individuals to leave as a group. In 1999, female bison were captured with a net gun fired from a Hughes 500D helicopter (Helicopter Wildlife Management and Helicopter Capture Services, Salt Lake City, Utah). Handling (in the same manner as described above) was done at the capture site and bison were released immediately after handling and radio-collaring. Bison were relocated in 3 days and recaptured by net gunning to determine the results of the caudal fold test.
Blood samples were taken from each bison from the caudal or carotid vein during the first handling period. Blood was collected in serum separator tubes to facilitate clotting, and prevented from freezing. Serum was removed by centrifuge within 12 h, and serum samples were frozen until serological tests were conducted.
The standard procedure for Brucella abortus testing in cattle is to use the buffered plate antigen test (BPAT) as a screening test, and the complement fixation test (CFT) as the confirmatory test for sera that agglutinate in the BPAT (Nielsen et al. 1996). Testing was done at the Animal Disease Research Institute, Lethbridge, Alberta (Animal and Plant Health, Canadian Food Inspection Agency). Sera that met either of the following criteria are referred to as B. abortus-positive (Joly, Leighton & Messier 1998): (a) agglutinated in the BPAT and agglutinated in the CFT at dilutions of ≥ 1 : 5 or (b) agglutinated in the CFT at dilutions of > 1 : 5 . We refer to the proportion of a given subset of bison (i.e. sex, age and population) that is B. abortus-positive as B. abortus-prevalence. This is equivalent to ‘apparent prevalence’ as defined by Greiner & Gardner (2000, p. 17): the probability that a randomly selected unit of analysis has a positive test result.
We tested for Mycobacterium bovis using the caudal fold test with (PPD) tuberculin (Thoen et al. 1988; Monaghan et al. 1994). Bison were injected with 0·1 mL of (PPD) tuberculin intradermally in the caudal fold. A veterinarian (T. Shury) accredited by the Canadian Food Inspection Agency conducted the tuberculosis test. He inspected the injection site after 72 h to determine pathogen exposure status (Monaghan et al. 1994). Bison were classified as positive, negative or suspicious reactors, based on the degree of reaction at the injection site. As recently infected animals or those in the latter stages of infection may not react to the injection of tuberculin (e.g. Griffin & Buchan 1994), we supplemented the caudal fold test with the fluorescent polarization assay for Mycobacterium bovis (Lin et al. 1996). Lin et al. (1996) did not provide interpretation criteria for the fluorescent polarization assay. To determine the diagnostic threshold for the fluorescent polarization assay, we examined the millipolarization units (mp) values for 85 bison sera from Elk Island National Park, Canada (Om Surujballi, Canadian Food Inspection Agency, Nepean, ON, unpublished data), a known tuberculosis-free herd. We rearranged the formula for comparison of a single observation against a sample distribution (equation 9·5 in Sokal & Rohlf 1995) to determine the maximum mp value that would be consistent with a distribution of negative samples (one-tailed alpha = 0·05). The mean mp for these bison was 166·5 (SE 0·48, n = 85), and less than 5% of a distribution of negative bison would have a mp value greater than 174 mp. We assumed that sera from bison with mp values greater than this threshold had a positive status. Bison that tested positive on either the caudal fold or the fluorescent polarization tests were considered positive and are referred to as M. bovis-positive. We refer to the proportion of a given subset of bison (i.e. sex, age and population) that is M. bovis-positive as M. bovis-prevalence. As above, this definition is synonymous with apparent prevalence as defined by Greiner & Gardner (2000).
The variables age, sex and population (Nyarling River, Hay Camp or Delta) were examined as possible factors associated with a positive status for each disease using logistic regression analysis (Sokal & Rohlf 1995; pp. 767–776). Model selection was based on small sample size corrected Akaike Information Criteria (AICc), and parameter estimates were averaged among all possible models weighted by Akaike weights (Burnham & Anderson 1998, pp. 119–140). Analysis was first conducted using age as a continuous variable; however, when preliminary analysis indicated nonlinearity in the relationship we grouped bison into the following age classes and entered age as a categorical variable in the model: < l, 1, 2, 3–5, 6–10 and 11–19. We found in a preliminary analysis an interaction between age and sex for both pathogens, therefore we elected to conduct analyses on each sex separately. We did not include in the analysis test results from the second capture if a bison was caught in more than one year.
Results
- Top of page
- Summary
- Introduction
- Methods
- Results
- Discussion
- Acknowledgements
- References
Overall, 30·9% (107/346) bison were B. abortus-positive. Sera that were anti-complementary (i.e. that reacted to the addition of complement in the absence of antigen) in the complement fixation test were excluded (n = 11). Inclusion of these sera drastically alters the sensitivity and specificity of this test, depending on whether they are treated as positive or negative (see Gall et al. 2000).
Initial analysis indicated that B. abortus-prevalence was a function of sex and age, where prevalence increased with age and females were more likely to test positive than males (male vs. female odds ratio, 0·70; 95% confidence interval (CI), 0·52–0·95). Sex-specific analyses indicated that age was a good predictor of B. abortus-prevalence in males (Table 1). Few males < 2 years of age were B. abortus-positive compared to females of the same age, yet after 2 years of age B. abortus-prevalence rose dramatically among males (Fig. 1). There appeared to be a bimodal relationship between age and B. abortus-prevalence in males; males 2–5 years of age had high B. abortus-prevalence, then B. abortus-prevalence declined in 6–10 year olds before increasing again in males > 11 years of age (Table 1; Fig. 1).
Table 1. Relationship between age and Brucella abortus prevalence in males (n = 94). Odds ratios refer the increase in probability of testing positive for brucellosis relative to the youngest age class (e.g. male bison in the 3–5 year age class are 40·26 times more likely to test positive for brucellosis than male bison in the < 1-year age class) | Age class | Odds ratio | 95% CI | Wald statistic* | P |
|---|
|
| < 2 years | − | Reference category | − | – |
| 2 years | 48·22 | 4·08–569·81 | 9·46 | 0·002 |
| 3–5 years | 40·26 | 3·89–416·72 | 9·60 | 0·002 |
| 6–10 years | 4·82 | 0·269–86·29 | 1·14 | 0·29 |
| 11–14 years | 45·00 | 3·73–543·1 | 8·97 | 0·003 |
B. abortus-prevalence in females increased with age in the Delta population, but this effect was not detectable in either the Hay Camp or the Nyarling River populations (Table 2). Female bison in the Hay Camp region were 1·5 times more likely to be B. abortus-positive than in the Delta after controlling for the effects of age (95% CI; 1·1–2·0; Fig. 2). As we did not test females < 2 years of age in the Nyarling River population, and only three 2-year olds were tested there, we repeated the analysis including only females > 2 years of age and in all three populations. After controlling for age, females in the Nyarling River were more likely to be B. abortus-positive than those in the Delta population (odds ratio, 1·7, 95% CI, 1·0–2·7) but not the Hay Camp population (odds ratio, 1·0; 95% CI, 0·6–1·6).
Table 2. Relationship of age to Brucella abortus seroprevalence for females in the Delta and Hay Camp populations (n = 215). There was no effect of age on brucellosis seroprevalence for females 2 years and older in the Nyarling River population (Wald Statistic = 5·18, d.f. = 3, P = 0·15) | Age class | Odds ratio (95% CI)* |
|---|
| Delta | Hay Camp |
|---|
|
| < 1 year | − | Reference category |
| 1 year† | Reference category | 2·25 (0·32–15·76) |
| 2 years | 1·92 (0·24–15·26) | 2·81 (0·50–15·77) |
| 3–5 years | 8·33 (1·23–56·67) | 1·61 (0·26–10·14) |
| 6–10 years | 7·29 (1·31–40·53) | 2·86 (0·47–17·35) |
| > 11 years | 4·50 (0·88–22·95) | 5·32 (0·94–30·0) |
Forty-nine percent of bison tested in late winters 1997–1999 tested positive on either the caudal fold test or the fluorescent polarization assay (n = 342). Mycobacterium bovis-prevalence was a function of age, and it increased faster for males than females (model-averaged odds ratios (95% CI): sex, 1·16 (0·95–1·43); age, 1·25 (1·14–1·36); sex × age, 0·89 (0·81–0·97)). Sex-specific analyses indicated that age was the predominant factor associated with M. bovis-prevalence in males, with the probability of testing positive for tuberculosis increasing 1·26 times for each additional year of age (95% CI, 1·03–1·54; Table 3). There was some indication that M. bovis-prevalence may increase with age faster in the Hay Camp area, and that males in general may have a higher M . bovis-prevalence in the Hay Camp population, although neither odds ratio differed from one (Table 3). The most parsimonious model predicted that male M. bovis-prevalence increased to almost 70% by the age of 9 years (Fig. 3).
Table 3. Comparison of models of Mycobacterium bovis prevalence in male bison in Wood Buffalo National Park (n = 97). The χ2 and P-value refer to the likelihood ratio goodness of fit test. Relative AlCc is presented as Δi, and the Akaike weight (ωi) refers to the probability that the model is the Kullback–Liebler best model, given the data (see Burnharn & Anderson 1998) | Model* | d.f. | χ2 | P | Δi | ωi |
|---|
|
| Age | 1 | 33·06 | < 0·001 | 0·00 | 0·52 |
| Age, age × population | 2 | 33·24 | < 0·001 | 1·95 | 0·20 |
| Age, population | 2 | 33·21 | < 0·001 | 1·98 | 0·19 |
| Age, population, age × population | 3 | 33·87 | < 0·001 | 3·49 | 0·09 |
| Age × population | 1 | 2·15 | 0·14 | 30·91 | < 0·001 |
| Population Population, age × population | 1 2 | 0·91 2·15 | 0·34 0·34 | 32·15 33·04 | < 0·001< 0·001 |
The most parsimonious model of M. bovis-prevalence in females indicated that prevalence varied as a function of age, population, and an interaction between age and population (Table 4). Mycobacterium bovis-prevalence in Hay Camp females was higher than in Nyarling River, which in turn was higher than in Delta (Table 4). Prevalence increased with age for females, with the probability of testing positive increasing 1·1 times with each year of age (95% CI, 1·00–1·2); however, this effect of age was not similar among the populations (Table 4). We repeated the analysis on separate populations to facilitate interpretation of these data, including age as a categorical variable (Fig. 4). M. bovis-prevalence in females rose with age in both Delta and Hay Camp populations (Hay Camp: Wald statistic = 14·3, d.f. = 5, P = 0·01; Delta: Wald statistic = 19·51, d.f. = 5, P = 0·002). Hay Camp population females in the 11–19 year age class had lower M. bovis-prevalence than those in the 6–10 year age class (Wald statistic = 7·26, d.f. = 1, P = 0·007); whereas the opposite was true for the Delta population (Fig. 4). We were unable to detect an effect of age on M. bovis-prevalence in the Nyarling River population for females 2 years of age or older (Fig. 4; Wald statistic = 3·79, d.f. = 3, P = 0·28).
Table 4. Comparison of models of Mycobacterium bovis prevalence in female bison in Wood Buffalo National Park (n = 260). The χ2 and P-value refer to the likelihood ratio goodness of fit test. Relative AICc is presented as Δi and the Akaike weight (ωi) refers to the probability that the model is the Kullback–Liebler best model, given the data (see Burnham & Anderson 1998) | Model* | d.f. | χ2 | P | Δi | ωi |
|---|
|
| Age, population, age × population | 3 | 31·46 | < 0·001 | 0·00 | 0·72 |
| Population, age × population | 2 | 26·19 | < 0·001 | 3·20 | 0·14 |
| Age, population | 2 | 23·92 | < 0·001 | 3·47 | 0·13 |
| Age | 1 | 13·79 | < 0·001 | 9·55 | 0·01 |
| Age, age × population | 2 | 16·14 | 0·001 | 11·25 | 0·002 |
| Age × population | 1 | 9·76 | 0·01 | 15·59 | < 0·001 |
| Population | 1 | 7·45 | 0·02 | 17·90 | < 0·001 |
Acknowledgements
- Top of page
- Summary
- Introduction
- Methods
- Results
- Discussion
- Acknowledgements
- References
This research was funded primarily through the Bison Research and Containment Program of Heritage Canada, under the advice of the Research Advisory Committee of the Bison Research and Containment Program. The Northern Scientific Training Program, the Government of the Northwest Territories and the University of Saskatchewan provided additional funding. D.O.J. was supported through a University of Saskatchewan Graduate Scholarship and a Natural Sciences and Engineering Research Council postgraduate scholarship. We gratefully thank the Canadian Food Inspection Agency (Lethbridge, AB, and Nepean, ON) for conducting disease testing. Thanks to Tim Evans, Trevor Evans, Michelle MacDonald and, particularly, Amanda Plante for technical assistance. Residents of Fort Chipewyan and Fort Smith provided support throughout the study, and the crews of Helicopter Wildlife Management, Helicopter Capture Services, and Big River Air risked their lives so that we may conduct this study.