Abstract:We compared selection of northern Yellowstone elk (Cervus elaphus) by hunters in the Gardiner Late Hunt and northern Yellowstone wolves (Canis lupus) with regard to sex, age, and impacts to recruitment. We compared harvest data from 1996–2001 with wolf‐killed elk data from 1995–2001. We assessed the effects of hunting and wolf predation on reproductive female elk by constructing a life table and calculating reproductive values for females in the northern Yellowstone herd. We devised an index of total reproduct… Show more
“…We found a weak negative relationship between age and survival, which was consistent with age-specific variation in survival found in other ungulate populations (Loison et al 1999;Gaillard et al 2000;Festa-Bianchet et al 2003). A negative relationship between survival and age in the Fort Riley population could be due to hunters avoiding harvesting a calf or yearling, and thereby increasing the mortality risk for adult female elk in older age-classes (Wright et al 2006). The average age at harvest for female elk at Fort Riley ( x x = 6.9 y) was within what has been defined as the prime-age life stage for elk (2-9 y; Raithel et al 2007), and is similar to the average age of elk harvested from a population in Idaho ( x x = 7.3 y; Husseman et al 2003).…”
Section: Discussionsupporting
confidence: 86%
“…As the primary source of mortality, hunting is expected to directly influence adult survival rates, which may subsequently influence the overall rate of population growth (l). Harvest may have a particularly strong influence on population dynamics if prime-age classes are selectively harvested (Wright et al 2006).…”
Understanding the influence of management actions and environmental conditions on demographic vital rates is important for effective conservation and management of wildlife populations. We used radio-telemetry to monitor annual and seasonal survival of 34 female elk Cervus elaphus at Fort Riley, Kansas in a 3.5-y field study (November 2003 to February 2007. We modeled the relationship between individual and environmental covariates and survival rates of female elk. We observed eight mortalities, and harvest was the primary cause of mortality in our study population. Annual survival rates of female elk in Kansas (0.76) were similar to other harvested populations of elk. Among the candidate model set, models that included age as a covariate were most supported. Parameter estimates from top models provided support for a slight negative relationship between age and survival. Monthly survival estimates during hunting season declined with age from 0.98 for 1.5-y-old females to 0.80 for 16.5-y-old females.
“…We found a weak negative relationship between age and survival, which was consistent with age-specific variation in survival found in other ungulate populations (Loison et al 1999;Gaillard et al 2000;Festa-Bianchet et al 2003). A negative relationship between survival and age in the Fort Riley population could be due to hunters avoiding harvesting a calf or yearling, and thereby increasing the mortality risk for adult female elk in older age-classes (Wright et al 2006). The average age at harvest for female elk at Fort Riley ( x x = 6.9 y) was within what has been defined as the prime-age life stage for elk (2-9 y; Raithel et al 2007), and is similar to the average age of elk harvested from a population in Idaho ( x x = 7.3 y; Husseman et al 2003).…”
Section: Discussionsupporting
confidence: 86%
“…As the primary source of mortality, hunting is expected to directly influence adult survival rates, which may subsequently influence the overall rate of population growth (l). Harvest may have a particularly strong influence on population dynamics if prime-age classes are selectively harvested (Wright et al 2006).…”
Understanding the influence of management actions and environmental conditions on demographic vital rates is important for effective conservation and management of wildlife populations. We used radio-telemetry to monitor annual and seasonal survival of 34 female elk Cervus elaphus at Fort Riley, Kansas in a 3.5-y field study (November 2003 to February 2007. We modeled the relationship between individual and environmental covariates and survival rates of female elk. We observed eight mortalities, and harvest was the primary cause of mortality in our study population. Annual survival rates of female elk in Kansas (0.76) were similar to other harvested populations of elk. Among the candidate model set, models that included age as a covariate were most supported. Parameter estimates from top models provided support for a slight negative relationship between age and survival. Monthly survival estimates during hunting season declined with age from 0.98 for 1.5-y-old females to 0.80 for 16.5-y-old females.
“…Associated trophic cascades have been documented, including recovery of riparian vegetation (Beyer et al 2007) and aspen (Ripple and Beschta 2007). The greater reproductive impact of cow elk hunting relative to wolf predation (Wright et al 2006) suggested adjusting hunting pressure was a more powerful management tool than predation for regulating elk population size. Whether coyotes on our study area are capable of filling a similar niche to wolves in Yellowstone is doubtful.…”
Coyote (Canis latrans) spatial and social ecology are variable, but have been little studied in high-elevation environments. In these temperate ecosystems, large ungulates are prevalent and coyote pack size may be large in order for them to scavenge and defend ungulate carcasses from conspecifics in neighboring packs. We initiated a study to understand the spatial and social ecology of coyotes on the Valles Caldera National Preserve, a high-elevation (2450-3400 m) protected area in northern New Mexico. Our objectives were to (1) describe the home range size and habitat use of coyotes in the preserve, (2) describe coyote movements within and outside of packs, and (3) to evaluate the relationship between coyote social cohesion and the amount of elk (Cervus elaphus) in the coyote diet. We acquired global positioning system and telemetry locations from 33 coyotes from August 2005 to July 2009. We classified 23 coyotes (70 % of individuals) as residents (i.e., territorial) during at least part of the study and ten coyotes (30 %) as transients. Overall mean home range size of resident packs was 10.6 ± 2.2 (SD) km 2 . Home range size varied between packs, but did not vary by season or year. Coyotes used dry and wet meadow habitats as expected based on availability; coyotes used riparian habitat more than expected, and forests less than expected. Social cohesion did not vary among biological seasons. Alpha coyotes were more socially cohesive with each other than with other pack members, and a transient exhibited temporal-spatial avoidance of pack members while inside the pack's territory followed by integration into the pack. Contrary to expectations, we found no relationship between coyote social cohesion and the proportion of elk in coyote diets. We concluded that coyote space use and sociality on the preserve were relatively stable year-round despite changes in biological needs, snow depth, and utilization of variously sized prey.
“…The elaborate stotting that prey such as Thomson's gazelles, Gazella thomsoni, perform at the beginning of a predator attack suggests that the predators are capable of detecting slight differences in the motor performance of prey (FitzGibbon & Fanshawe 1988). It is also well known that predators efficiently identify weak, injured or sick prey (Mills, 1990;Quinn and Cresswell, 2004;Martin et al, 2006;Wright et al, 2006). In summary, natural selection on predators has probably enhanced animals' ability to detect subtle differences in the motor performance of potential prey.…”
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