Demographic data show many populations of Rocky Mountain (Cervus elaphus nelsoni) and Roosevelt (Cervus elaphus roosevelti) elk have been declining over the last few decades. Recent work suggests that forage quality and associated animal nutritional condition, particularly in late summer and early autumn, influence reproduction and survival in elk. Therefore, we estimated seasonal nutritional condition of 861 female elk in 2,114 capture events from 21 herds in Washington, Oregon, Wyoming, Colorado, and South Dakota from 1998 to 2007. We estimated ingesta-free body fat and body mass, and determined age, pregnancy status, and lactation status. We obtained estimates for most herds in both late winter-early spring (late Feb-early Apr) and in autumn (Nov-early Dec) to identify changes in nutritional condition of individuals across seasons.Body fat levels of lactating females in autumn were consistently lower than their non-lactating counterparts, and herd averages of lactating elk ranged from 5.5% to 12.4%. These levels were 30-75% of those documented for captive lactating elk fed high-quality diets during summer and autumn. Body fat levels were generally lowest in the coastal and inland northwest regions and highest along the west-slope of the northern Cascades. Adult females in most herds lost an average of 30.7 kg (range: 5-62 kg), or about 13% (range: 2.6-25%) of their autumn mass during winter, indicating nutritional deficiencies. However, we found no significant relationships between spring body fat or change in body fat over winter with winter weather, region, or herd, despite markedly different winter weather among herds and regions. Instead, body fat levels in spring were primarily a function of fat levels the previous autumn. Thinner females in autumn lost less body fat and body mass over winter than did fatter females, a compensatory response, but still ended the season with less body fat than the fatter elk.Body fat levels of lactating females in autumn varied among herds but were unrelated to their body fat levels the previous spring. Within herds, thinner females exhibited a compensatory response during summer and accrued more fat than their fatter counterparts over summer, resulting in similar body fat levels among lactating elk in autumn despite considerable differences in their fat levels the previous spring. Level of body fat achieved by lactating females in autumn varied 2-fold among herds, undoubtedly because of differences in summer nutrition. Thus, summer nutrition set limits to rates of body fat accrual of lactating females that in turn limited body condition across the annual cycle.Pregnancy rates of 2-to 14-year-old females ranged from 68% to 100% in coastal populations of Washington, 69% to 98% in Cascade populations of Washington and Oregon, 84% to 94% in inland northwestern populations of Washington and Oregon, and 78% to 93% in Rocky Mountain populations. We found evidence of late breeding, even in herds with comparatively high pregnancy rates. Mean body mass of calves (n ¼ 242) in 3 popul...

Summary 1. Understanding the interaction among predators and between predation and climate is critical to understanding the mechanisms for compensatory mortality. We used data from 1999 radio‐marked neonatal elk (Cervus elaphus) calves from 12 populations in the north‐western United States to test for effects of predation on neonatal survival, and whether predation interacted with climate to render mortality compensatory. 2. Weibull survival models with a random effect for each population were fit as a function of the number of predator species in a community (3–5), seven indices of climatic variability, sex, birth date, birth weight, and all interactions between climate and predators. Cumulative incidence functions (CIF) were used to test whether the effects of individual species of predators were additive or compensatory. 3. Neonatal elk survival to 3 months declined following hotter previous summers and increased with higher May precipitation, especially in areas with wolves and/or grizzly bears. Mortality hazards were significantly lower in systems with only coyotes (Canis latrans), cougars (Puma concolor) and black bears (Ursus americanus) compared to higher mortality hazards experienced with gray wolves (Canis lupus) and grizzly bears (Ursus horribilis). 4. In systems with wolves and grizzly bears, mortality by cougars decreased, and predation by bears was the dominant cause of neonatal mortality. Only bear predation appeared additive and occurred earlier than other predators, which may render later mortality by other predators compensatory as calves age. Wolf predation was low and most likely a compensatory source of mortality for neonatal elk calves. 5. Functional redundancy and interspecific competition among predators may combine with the effects of climate on vulnerability to predation to drive compensatory mortality of neonatal elk calves. The exception was the evidence for additive bear predation. These results suggest that effects of predation by recovering wolves on neonatal elk survival, a contentious issue for management of elk populations, may be less important than the composition of the predator community. Future studies would benefit by synthesizing overwinter calf and adult‐survival data sets, ideally from experimental studies, to test the roles of predation in annual compensatory and additive mortality of elk.

Density dependence plays a key role in life-history characteristics and population ecology of large, herbivorous mammals. We designed a manipulative experiment to test hypotheses relating effects of density-dependent mechanisms on physical condition and fecundity of North American elk (Cervus elaphus) by creating populations at low and high density. We hypothesized that if density-dependent effects were manifested principally through intraspecific competition, body condition and fecundity of females would be lower in an area of high population density than in a low-density area. Thus, we collected data on physical condition and rates of pregnancy in each experimental population. Our manipulative experiment indicated that density-dependent feedbacks affected physical condition and reproduction of adult female elk. Age-specific pregnancy rates were lower in the high-density area, although there were no differences in pregnancy of yearlings or in age at peak reproduction between areas. Age-specific rates of pregnancy began to diverge at 2 years of age between the two populations and peaked at 6 years old. Pregnancy rates were most affected by body condition and mass, although successful reproduction the previous year also reduced pregnancy rates during the current year. Our results indicated that while holding effects of winter constant, density-dependent mechanisms had a much greater effect on physical condition and fecundity than density-independent factors (e.g., precipitation and temperature). Moreover, our results demonstrated effects of differing nutrition resulting from population density during summer on body condition and reproduction. Thus, summer is a critical period for accumulation of body stores to buffer animals against winter; more emphasis should be placed on the role of spring and summer nutrition on population regulation in large, northern herbivores.

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In the 1980s resource managers were increasingly concerned about effects of timber harvest on ungulates in National Forests. Land and resource management plans incorporated restrictions on timber harvest to maintain cover for Rocky Mountain elk (Cefvus elaphus nelsoni V. Bailey) and mule deer (Odocoileus hemionus hemionus Rafinesque), and habitat models were used to predict effectiveness of various habitat components for these ungulates. Many of the assumptions on which these models were based were untested, however. The Starkey Project, in northeastern Oregon, was begun to address some of these issues through manipulative experiments in a landscape representative of inland National Forests in the West. A 25,000-acre (10 125-ha) area was surrounded with game-proof fencing to support studies on elk, mule deer, and cattle (SOS Taurus). A newly developed telemetry system, using loran-C (long range navigation-C) signals, tracks distribution of the three species in relation to common land management activities and habitat variables. Four primary research projects are underway: animal-unit equivalencies, intensive timber management, effects of roads and traffic, and breeding efficiency of bull elk. Activities at Starkey include trapping, feeding, and handling of deer and elk, radio-telemetry data collection, road and traffic monitoring, hunting, timber harvest, cattle grazing, and vegetation monitoring. An intensive technology transfer program is also an integral part of the Starkey Project. The physical site, including handling facilities and telemetry-related structures, and chronology of events related to the Starkey Project are described. A bibliography of project publications also is included.Keywords: Cattle, deer, elk, forest management, ungulates, Blue Mountains, Oregon, radio telemetry, habitat, Starkey Project, technology transfer, wildlife research. IntroductionLand-use planning for National Forests (NFs) in the 1980s illustrated the growing conflict over public lands management. In land and resource management plans (Forest plans) for the NFs of the Blue Mountains in Washington and Oregon, interactions of livestock with wildlife, especially deer' and elk, were identified as a major concern, as was the relation of wildlife to timber production. Constraints on timber harvest and road construction were incorporated in several Forest plans to meet objectives for deer and elk populations and habitats. These constraints may result in restricted timber harvest (Riggs and others 1993) and thus lower revenues for NFs, local governments, and timber companies, as well as road closures that potentially reduce opportunities for recreation and are costly to establish and maintain. During the 1980s models for predicting habitat effectiveness for deer and elk were being developed and implemented that promoted closing roads or maintaining certain cover:forage ratios for wildlife (Lyon 1983, Thomas and others 1979, Wisdom and others 1986.National Forests support, during some part of the year, more than 90 percent of the e...