The distribution of Dermacentor ticks in Canada in relation to bioclimatic zones.

Canadian Journal of Zoology (Impact Factor: 1.35). 08/1967; 45(4):517-37. DOI: 10.1139/z67-066
Source: PubMed

ABSTRACT Dermacentor andersoni has been collected north of Jasper, Alberta, close to 54° N. and near 53° N. in British Columbia. Spread to the north and northwest is probably limited by low summer soil temperatures, which would act principally by slowing egg development, thus disrupting the seasonal cycle of the tick. To the southwest, mild winters may fail to release diapause at the correct time of year. Aspect and slope are important factors. Altitude spread of records is from 1000–7000 ft. The most generally applicable description of its distribution is the ecotone between western grassland and moister regions, including clearings and rocky outcrops m the montane and Columbia forests, and shrubby areas of the prairies. In British Columbia, a series of randomly selected transects indicated a strong association between the tick's presence and several species of shrubs growing without tree shade.Each bioclimatic zone tends to have a characteristic group of rodents as main hosts of the immature stages. The prairie and montane regions differ in the indigenous hosts available to the adult tick.East of 105° D. andersoni is replaced by D. variabilis, which is adapted to the more humid summers of the eastern deciduous forest zones, and differs considerably from D. andersoni in its phenology. There are no reliable records of indigenous D. variabilis north of 52° latitude.D. albipictus occurs from the east to the west coast. Because of the winter activity of its larvae, allowing the whole summer for egg development, it is able to penetrate much farther north than the other two species. There are two records close to 60° latitude.

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    • "Winter ticks are a common pest of horses, elk, mule deer, moose, and other wildlife species in the United States, in addition to occasionally infesting cattle (Wilkinson 1967, Samuel et al. 1991). These Dermacentor species extend much further north than other Dermacentor species and are able to use a much broader seasonal window for development than other species (Wilkinson 1967). Although no information has quantified the ability of D. albipictus populations to persist at higher elevations, this species is present at higher latitudes and commonly found on a variety of wildlife that are adapted to higher elevations. "
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    ABSTRACT: Livestock parasitism on high-elevation rangeland (>1,800 m (6,000’)) may not be as well documented as parasitism is at lower elevations because producers assume elevation limits parasite persistence and exposure of livestock to parasites. Certain parasites, such as horn flies, Haematobia irritans (L.) (Diptera: Muscidae), and biting midges, Culicoides spp. (Diptera: Ceratopogonidae), a vector of bluetongue virus, are restricted to lower elevations. However, some parasites are endemic to high elevations, such as the Rocky Mountain wood tick, Dermacentor andersoni (Stiles) (Acari: Ixodidae), a vector of many diseases. Multiple horse fly and mosquito species persist at various elevation gradients, with some having preference for lower or higher elevations. For example, the horse fly, Hybomitra laticornis (Hine) (Diptera: Tabanidae), occurred from 1,700-3,035 m (5,577’-9,957’), Hybomitra phaenops (Osten Sacken) (Diptera: Tabanidae) only occurred above 2,499 m (8,198’), and the western horse fly, Tabanus punctifer (Osten Sacken) (Diptera: Tabanidae), only occurred below 2,250 m (7,381’). This variable elevation range is also expressed by several mosquito species, with six of 12 known mosquito species that transmit West Nile virus at or above 1,750 m (5,740’). Furthermore, gastrointestinal roundworms can survive > 1 yr at high elevations, use larvae inhibition to survive winter, and lungworm infection may increase with elevation. Evidence suggests changing weather patterns, climate variability, and animal movements could shift some parasites and diseases into higher elevations, such as mosquitoes and biting midges. Moving livestock to high-elevation ranges may also increase the opportunity for livestock-wildlife interactions, parasite and disease transmission, and exposure. Producers should develop high-elevation integrated pest management strategies, such as delaying or avoiding parasite treatment to optimize efficacy and reduce input costs, monitoring closely during wet years and periods of livestock-wildlife interactions, using elevation to avoid certain parasites, and not assuming that elevation is capable of preventing livestock parasitism.
    03/2015; 6(1):8-8. DOI:10.1093/jipm/pmv008
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    • "The life cycle of D. andersoni is completed over a time-span of 2–3 years and regional variation in climate affects the distribution and host-seeking activity of ticks observed in the field (James et al., 2006; Eisen, 2007). For example, Wilkinson (1967) observed that RMWTs in Canada were typically absent in areas with fewer than 2000 cumulative degree-days (growing days), even when appropriate host species were present. Eisen et al. (2007) observed that RMWT "
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    ABSTRACT: Dermacentor andersoni (Ixodida: Ixodidae) Stiles, also known as the Rocky Mountain Wood Tick (RMWT), is found throughout the western United States and transmits pathogens of importance to human and animal health. The distributions and activity patterns of RMWTs are shaped by regional climatic variation. However, it is unknown if responses to climatic variation differ across the tick's geographical range. The objective of this narrow study was to test the hypothesis that the responses of RMWTs to abiotic conditions [e.g. temperature and RH (relative humidity)] vary among populations. We collected RMWTs from ecologically distinct field sites in the states of Montana and Oregon (USA). In the laboratory, we tracked weekly survival of tick larvae under four combinations of RH (75% and 98%) and temperature (26 and 32 °C) that reflected the range of conditions observed in the source habitats during spring-summer. For both populations, larval survival time decreased at the higher ambient temperature (50% mortality 1-2 weeks earlier). Differences in RH did not affect the survival time of larvae from Oregon. By contrast, the survival time of larvae from Montana decreased at the lower RH (50% mortality 1 week earlier). These data suggest that the tolerance limits for water stress may differ among populations of D. andersoni.
    Medical and Veterinary Entomology 03/2014; 28(3). DOI:10.1111/mve.12049 · 2.33 Impact Factor
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    • "In contrast, the discovery of three D. andersoni larvae near Clavet, each representing a dierent 16S haplotype and feeding on a dierent host individual, was surprising because this species has not been recorded previously this far east in Saskatchewan (see Wilkinson 1967). Although the distributional range of D. andersoni has expanded eastwards in Saskatchewan since the 1970s, which may have implications for transmission of tick-borne pathogens to livestock and humans, the closest known population of D. andersoni to the study site near Clavet is situated ~70 km to the southeast "
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    ABSTRACT: Morphological examination of ticks feeding on northern pocket gophers, Thomomys talpoides, near Clavet (Saskatchewan, Canada) revealed the presence of two genera, Ixodes and Dermacentor. All adult ticks collected were identified as I. kingi. Single strand conformation polymorphism (SSCP) analyses and DNA sequencing of the mitochondrial 16S rRNA gene confirmed the species identity of most Ixodes immatures as I. kingi (two nymphs and 82 larvae), and the Dermacentor immatures as D. variabilis (one nymph and one larva) and D. andersoni (three larvae). Six Ixodes larvae feeding on three T. talpoides individuals were identified as four different 16S haplotypes of I. scapularis, which was unexpected because there are no known established populations of this species in Saskatchewan. However, flagging for questing ticks and further examination of the ticks feeding on T. talpoides in two subsequent years failed to detect the presence of I. scapularis near Clavet, suggesting that there is no established population of I. scapularis in this area. Nonetheless, since I. scapularis is a vector of pathogenic agents, passive and active surveillance needs to be conducted in Saskatchewan on an ongoing basis to determine if this tick species and its associated pathogens become established within the province.
    Journal of Vector Ecology 12/2011; 36(2):355-60. DOI:10.1111/j.1948-7134.2011.00176.x · 1.44 Impact Factor
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