Journal of Mammalogy, 97(1):128–134, 2016 DOI:10.1093/jmammal/gyv162 Published online October 21, 2015 Abiotic and biotic factors affecting the denning behaviors in Asiatic black bears Ursus thibetanus Toshiaki Yamamoto,* Hiroo Tamatani, Junpei Tanaka, Gen Oshima, Serina Mura, and Masaru Koyama Department of Veterinary Nursing and Technology, Nippon Veterinary and Life Science University, Musashino, Tokyo 180-8602, Japan (TY, SM) Department of Bear Management, Picchio Wildlife Research Center, Hoshino Karuizawa, Kitasaku-gun, Nagano 389-0194, Japan (HT, JT, GO) Department of Tourism and Economy, Karuizawa town office, Karuizawa, Kitasaku-gun, Nagano 389-0111, Japan (MK) * Correspondent: [email protected] For bears, numerous associations between biotic and abiotic factors have been reported to correlate with the timing of den entry and emergence; however, an analysis showing which factors influence the timing of den entry and emergence has not been performed enough. In this study, a generalized linear mixed model was generated using 66 entry dates for 26 females and 40 entry dates for 26 males, and 56 emergence dates for 26 females and 25 emergence dates for 18 males between 1999 and 2012. Regarding factors for den entry, the average temperature in November and mast production of Mongolian oaks were significant for both males and females. For the date of den emergence, the average temperature in March affected strongly. For males, good mast production of Mongolian oaks in the previous year was found to be associated with early den emergence. For females, the presence of newborns had a significant influence on their den entry and emergence. This study indicated that denning behavior appears to be regulated by several abiotic and biotic factors and regulation factors are sex specific. Key words: Asiatic black bear, den emergence, den entry, denning period, mast, Mongolian oak © 2015 American Society of Mammalogists, www.mammalogy.org Denning behavior of the genus Ursus is a phenomenon evolved to minimize energy consumption by shutting down most of the bear’s activities, including ingestion and excretion (Nelson et al. 1973). This process markedly reduces metabolism and enables Ursus spp. to survive harsh environmental conditions, primarily a seasonal lack of food and unfavorable weather (Mystrud 1983). This behavior has been observed in American black bears (Ursus americanus), Asiatic black bears (Ursus thibetanus), brown bears (Ursus arctos), and polar bears (Ursus maritimus—Hellgren 1998; Seryodkin et al. 2003; Tøien et al. 2011). Bears generally spend several months in the den, but the duration of denning is a variable dependent upon location and can vary from a few weeks to 7 months or more (Linnell et al. 2000). Even within local populations, the duration of denning has been found to differ by as much as a month among individuals (e.g., Tietje and Ruff 1980; Haroldson et al. 2002). Understanding the factors that influence the timing of den entry and emergence thus may provide insights regarding the variation in ursid life histories. Previous studies have clarified associations between the timing of denning behavior and various other factors. For example, it has been long believed that snowfall is associated with den entry (e.g., Craighead and Craighead 1972; Reynolds et al. 1976), but others have not corroborated this relationship (e.g., Judd et al. 1986; van Daele et al. 1990). There is, however, general agreement that low temperatures stimulate ursids to enter their dens (Lindzey and Meslow 1976; Johnson and Pelton 1980). Other researchers have suggested that a reduction in available food sources in autumn influences denning chronology, and that den entry begins earlier when the production of acorn is low (Schooley et al. 1994; Kozakai 2009). Denning behavior has also been reported to be influenced by not only abiotic but also biotic factors. Delivery of newborn cubs influences the timing of den entry and emergence of females. In ursids, pregnant females go into the den earlier than other individuals and emerge from the den later (e.g., Lindzey and Meslow 1976; Tietje and Ruff 1980; Haroldson et al. 2002). Variations dependent on age and sex among brown bears have been observed. For example, the denning period was correlated positively with age in females (Friebe et al. 2001), but the opposite result was found in males (Manchi and Swenson 2005). As described above, various biotic and abiotic factors 128 YAMAMOTO ET AL.—TIMING OF DENNING BEHAVIORS IN BEARS129 for denning behavior have been individually reported in Ursus, but a complex analysis to determine the most influential factors for denning behavior has not been performed. The duration of denning varies among Asiatic black bears, which are widely distributed from the Middle East to East Asia. In Japan, denning lasts for 5–6 months in Tohoku district (latitude of 36–42°N) but only for approximately 1 month in a section of Chugoku district (latitude of 33–35°N—Maita 1996; Koike and Hazumi 2008; Yamazaki 2011). Except for pregnant females, Asiatic black bears inhabiting Taiwan do not hibernate (Hwang and Garshelis 2007), and the timing of den entry markedly varies by year in Asiatic black bears inhabiting in central Japan (Kozakai et al. 2009), suggesting that various factors influence denning behavior. However, the factors associated with the timing of den entry and emergence are poorly documented in Asiatic black bears. In this study, we surveyed den entry and emergence in Asiatic black bears inhabiting the foothills of Mt. Asama in Nagano Prefecture, Japan, between 1999 and 2012, and performed analyses of biotic and abiotic factors to identify those associated with denning chronology in males and females. Materials and Methods Study site.—The survey was performed in the foothills of Mt. Asama, located in the east of Nagano Prefecture in central Japan (approximately 400 km2; Fig. 1). The elevation of the survey area was 600–2,500 m, and the forests consisted of mixed foliage, including conifers, Larix kaempferi (syn. Larix leptolepis), and broad-leaved trees: chestnut (Castanea crenata), Mongolian oak (Quercus crispula), and Konara oak (Quercus serrata). For Asiatic black bears, the hard mast production of these broad-leaved tree species is the most important food resource from early September to the end of October and strongly affects feeding behavior (Izumiyama et al. 2004; Nakajima 2012). Depending on the year and location, mast production of these species fluctuates widely and has a marked correlation with the number of nuisance bears killed in northern Japan (Oka et al. 2004). The annual rainfall is between 1000 and 1500 mm, and snowfall rarely exceeds 30 cm during winter months. The average annual temperatures are 20 and −5°C in summer and winter, respectively. Tracking of individuals.—Data from 29 female and 26 male Asiatic black bears tracked from 1999 to 2012 were used. These animals were captured in culvert traps using honey and honeycombs as attractants after obtaining permission from the Ministry of the Environment and Nagano Prefecture. Captured individuals were anesthetized (1:1 combination of tiletamine and zolazepam, 100 mg/kg), and their gender was identified by a genital examination. External physical measurements, including body length and body weight, were also taken, and a premolar was extracted to identify the animal’s age. Bears were fitted with a collar (ATS Inc., Isanti, Minnesota) and released. Research in live animals followed American Society of Mammalogists’ guidelines (Sikes et al. 2011). A Yagi antenna and portable receiver were used to track the bears’ movements via locating the VHF signals emitted by collars; the location of each bear was determined by triangulation (White and Garrott 1990). We located each bear approximately once every 10 days. Estimation of den entry and emergence.—The date of den entry was estimated as the midpoint between the first day, when the animal was judged to have stopped moving, and the last day, when the animal was assumed to be moving based on its location. Because telemetry error was previously estimated as 84.3 m (range: 20–161 m; Yamamoto et al. 2012), we concluded that a bear was still moving when the current location was estimated to be more than 100 m away from the denning site. The date of den emergence was defined as the midpoint between the first day that the animal moved more than 100 m and the last day that its presence in the den was confirmed. Because the locations of the animals were confirmed at intervals of no more than 10 days during the denning period, errors in the estimated entry and emergence dates were small. In addition, when the location was not confirmed for 10 days or longer, data for the animal were excluded. Biotic factors.—Parturition was confirmed by physically listening for vocalizations of cubs near the dens during February and March or directly observing the presence or absence of cubs from April to November. Even when we had access to the den and did not hear vocalizations of a cub, we did not confirm the absence of cubs. When the presence or absence of parturition could not be confirmed, the animal was excluded from analysis. In order to determine the age of individuals, the premolar extracted during the capture was decalcified and thin-sectioned, and the number of intensely stained layers in the cementum was counted (see Willey 1974). Abiotic factors.—We established an average of 50 sites per year randomly within the survey area and examined the mast production of Mongolian oak, chestnut, and Konara oak from early September to early October from 1999 to 2012. At each site, we selected 10 reproductive trees of similar size (20– 60 cm diameter at breast height) for each species and observed the mast productions for a specific period of time (30 s to 1 min) using binoculars. The mast production was evaluated based on the number of nuts counted per 30 s at each site and was respectively judged as good, average, bad, or poor when more than 20, 5–20, 1–4, or 0 nuts were observed (Wildlife Management Research Center, Hyogo 2011). In total, 250–400 trees of each species per year were observed to estimate mast production and the mean of the combined sites was used as the amount of available food resources produced by each species of tree per year (Fig. 2). The mast productions of each species varied year by year, but no synchronization among the 3 species and sites was noted, unlike that reported in other regions (Kuramoto et al. 1995; Wildlife Management Research Center, Hyogo 2011). The location of each den was individually plotted using ArcGIS 10.2 (ESRI 2014), and the elevation was calculated using 50-m digital elevation model. The average temperatures in November and March and weather conditions on the first 130 JOURNAL OF MAMMALOGY Fig. 1.—Maps of the survey region. The lower map shows the elevation of the survey region; dark areas represent high elevations, and bright areas represent low elevations. Point data represent denning sites of Asiatic black bears. Fig. 2.—Changes in food availability (Mongolian oak, konara oak, and chestnut) for Asiatic black bears from 1999 to 2012. YAMAMOTO ET AL.—TIMING OF DENNING BEHAVIORS IN BEARS131 day of snow were obtained from the database of the Japan Meteorological Agency (Japan Meteorological Agency 2014). Statistical analysis.—To compare timing of den entry and emergence, and the denning duration among pregnant females, non-pregnant females, and males, a 1-way analysis of variance was performed, followed by Tukey’s multiple comparisons test. The correlation between age and denning duration for each sex was determined by Spearman rank correlation test. To analyze the association of each factor with denning behavior, a general linear mixed model (GLMM) was used, with the date of den entry (regarding 1 November as day 1) as a response variable and the following items as explanatory variables: the average temperature in November; date of 1st snowfall; food sources, namely Mongolian oak, chestnut, and Konara oak mast; elevation; presence or absence of pregnancy; and age (in males, the same items excluding the presence or absence of pregnancy). For the date of den emergence (regarding March 1 as day 1), the GLMM included the following 6 items as explanatory variables: average temperature in March, food sources, Mongolian oak mast production in the previous year, elevation, age, and presence or absence of young (in males, the same items excluding the presence or absence of young). To eliminate multicollinearity, Spearman’s rank correlation was analyzed beforehand, but no strong correlation was noted between any variables (ρ < 0.5 in all cases). A Poisson distribution was employed for the error distribution, and individuals were regarded as a random factor. For model selection, using the Akaike information criterion (AIC), the model with the lowest AIC was regarded as optimal. Analyses were performed using R.ver. 3.0 (R Development Core Team 2013). Results Over the 14-year period, the date of den entry could be confirmed 21 times for 15 pregnant females, 45 times for 20 nonpregnant females, and 40 times for 26 males. The date of den emergence could be identified 18 times for 12 females with cubs, 38 times for 23 females without cubs, and 25 times for 18 males. The mean age was 7.3 ± 2.9 years for females with cubs, 8.9 ± 4.7 years for females without cubs, and 7.2 ± 3.5 years for males. The mean elevation of the dens was 1,121 ± 204 m for pregnant females, 1,078 ± 230 m for non-pregnant females, and 1,174 ± 336 m for males (Fig. 1). Asiatic black bears in our study area entered and emerged from their dens primarily during November to December and April to May, respectively. The average date of den entry was 3 December (SD = 11.4) for females without cubs, 28 November (SD = 12.9) for females with cubs and 2 December (SD = 10.8) for males (Table 1). The date of den entry was not significantly different among the 3 groups (F2,103 = 1.17, P = 0.32). On the other hand, the average date of den emergence was 25 April (SD = 13.0) for females without cubs, 11 May (SD = 17.3) for females with cubs, and 17 April (SD = 9.3) for males (Table 1). Significant difference in the date of den emergence was detected among the 3 groups (F2,78 = 17.59, P < 0.001): males and females without cub emerged earlier, and females with cub later. The duration Table 1.—Average data of den entry, den emergence, and den duration in male and female Asiatic black bear by reproductive categories during 1999–2012. Category Sex N Average (range) Den entry Females with cubs Females with no cubs Males Females with cubs Females with no cubs Males Females with cubs Females with no cubs Males 21 45 40 18 38 25 15 32 23 28 Nov (8 Nov–28 Dec) 3 Dec (12 Nov–2 Jan) 2 Dec (15 Nov–24 Dec) 11 May (4 Apr–12 Jun) 25 Apr (28 Mar–18 May) 17 Apr (2 Apr–27 Apr) 168.8 days (141–212) 141.1days (108–177) 135.1days (115–153) Den emergence Den duration of denning was 135.1 ± 10.4 days for males, 141.1 ± 19.3 days for females without cubs, and 168.8 ± 17.0 days for females with cubs, with significant differences among the 3 groups (F2,67 = 21.18, P < 0.001); duration was about on 1 month longer in females that gave birth compared to that of the others (Table 1). Moreover, the duration of denning was negatively correlated with age in males (ρ = −0.43, P = 0.04) and positively correlated with age in females (ρ = 0.31, P = 0.01). The GLMM was used to analyze factors affecting den entry and emergence. During model selection for the timing of den entry in females, positive correlations were noted in parturition during denning and temperature in November and an inverse correlation in the elevation (Tables 2 and 3). In years with above average temperatures in November, den entry was delayed at lower elevations, excluding females experiencing parturition during the denning. The timing of den entry was also strongly influenced by the mast production of Mongolian oak. Similarly, the timing of den entry in males was positively correlated with the temperature in November and inversely correlated with the mast production of Mongolian oak (Tables 2 and 3). On the other hand, timing of snowfall and age were not in the best model for den entry. In the GLMM analysis of den emergence, the average temperature in March was relevant in both genders (Tables 2 and 3). In addition, den emergence was markedly influenced by the elevation, parturition during denning in females, and the mast production of Mongolian oak in the previous year in males (Tables 2 and 3). However, age was not included in the parameters of the best model for the timing of den emergence. Discussion In this study, temperature was associated with den entry and emergence in both genders. Asiatic black bears are widely distributed in Japan. The duration of denning is about 5 months in bears distributed in northern regions, whereas it is about 1 month in southern regions (Maita 1996; Oi 2009). Similar variations in the denning period dependent on the latitude have been reported in other ursid species, suggesting that food resources remain available later in autumn as the latitude decreases (Wooding and Hardisky 1992; Linnell et al. 2000). For a similar reason, bears inhabiting Karuizawa enter the den 132 JOURNAL OF MAMMALOGY later and emerge earlier in warm years. Furthermore, snow accumulates earlier at higher elevations in this area, which makes it difficult for bears to forage. Thus, elevation was also selected as a negative factor for females; however, elevation was not selected for males. One reason may have been that, in almost all cases, the locations of male dens were at higher elevations, and the individual variation was too low to detect this factor. In both genders, mast production of Mongolian oak was also strongly associated with the timing of den entry. We predicted Table 2.—The top-ranked candidate (∆AICc<2) for den entry and emergence of male and female. ID listed in the table indicates the identification code of each section. Numbers listed in the Variables column represent the following entry (1–8) and emergence (5–9) factors: 1— November temperature, 2—snowfall, 3—Konara oak, 4—Japanese chestnut, 5—Mongolian oak, 6—elevation, 7—age, 8—parturition during denning, 9—March temperature. Model Sex Variables AIC ∆AICc Den entry Male 1 + 5 1 + 3 + 5 1 + 5 + 7 1 + 4 + 5 1 + 2 + 5 1 + 2 + 4 + 5 + 6 + 8 1 + 2 + 4 + 5 + 6 + 7 + 8 1 + 4 + 5 + 6 + 8 1 + 2 + 3 + 4 + 5 + 6 + 8 2 + 5 + 9 2 + 9 2 + 5 + 7 + 9 6 + 8 + 9 6 + 8 6 + 7 + 8 + 9 2 + 6 + 8 + 9 82.3 83.0 83.1 83.6 84.3 0.00 0.77 0.77 1.30 1.99 0.00 1.53 1.68 1.99 0.00 0.81 1.68 0.00 0.81 1.29 1.97 Female Den emergence Male Female 209.5 209.6 209.9 85.9 86.8 87.6 245.9 246.7 247.2 247.8 that denning behavior would start later when food sources were scarce, because the energy stores needed to survive the winter had not yet been secured. However, the situation was actually the opposite; during years in which food sources were scarce, denning behavior started early, perhaps to reduce the basal metabolic rate to below the energy levels required for feeding. A similar tendency was observed in the American black bear (Schooley et al. 1994) and the Asiatic black bear (Kozakai et al. 2009). In Asiatic black bears inhabiting areas around the Ashio Copper Mine in Tochigi Prefecture, where the food source availability and denning behavior were compared over 2 years, the results showed that denning started about 1 month earlier in the year when the production of acorns was low (Kozakai et al. 2009). Such studies support the conclusion early den entry in bears is at least in part the result of insufficient food resources in autumn. One interesting observation was that the mast productions of Mongolian oaks in the previous year influenced the den emergence of males. It has been reported that, based on fecal analysis, bears feed on the acorns from the previous year after emerging from their dens, suggesting that oak acorns are an important source of food for males after den emergence (Koike 2010). Such evidence suggests that males emerge earlier from the den to feed when they can feed on acorns from the previous year, whereas when acorns are scarce, they continue denning behavior in order to save energy in preparation for the breeding season. In future work, more attention should be given to understanding the relationship between the timing of den emergence and available food resources. A comparison of the duration of denning between males and females confirms that pregnant females entered the den earlier. Females tended to enter earlier, although the difference was not always significant. Regarding den emergence, males emerged earlier, and females with cubs emerged later. This sex-based Table 3.—The parameters of the best model for den entry and emergence of males and females and the 95% confidence intervals (CI) of the models. Variables indicated using asterisks mean that the value ranges of the 95% CI did not include zero. Model Sex Den entry Male Female Den emergence Male Female Variables Intercept November temperature Mongolian oak Intercept November temperature Mongolian oak Japanese chestnut Elevation Parturition during denning Snowfall Intercept March temperature Mongolian oak Elevation Intercept March temperature Elevation Parturition during denning Coefficient SE 1.732 0.186 0.674 4.083 0.180 0.390 −0.099 −0.730 0.218 0.003 0.479 −0.188 −0.729 0.450 −0.547 −0.061 1.498 −0.307 0.363 0.037 0.181 1.000 0.025 0.128 0.040 0.320 0.061 0.002 1.688 0.076 0.257 0.241 1.249 0.030 0.399 0.067 Upper lower 0.259 1.029 0.113 0.319 0.229 0.641 −0.021 −0.103 0.338 0.007 0.131 0.139 −0.177 −1.357 0.098 −0.001 −0.039 −0.225 0.922 −0.337 −1.233 −0.022 −0.002 2.280 −0.176 −0.120 0.716 −0.438 YAMAMOTO ET AL.—TIMING OF DENNING BEHAVIORS IN BEARS133 den emergence behavior has been previously noted in brown bears, American black bears, and Asian black bears (e.g., Tietje and Ruff 1980; Haroldson et al. 2002; Manchi and Swenson 2005; Oi and Yamazaki 2006). The shorter duration of denning in males than in females may generally be explained by differences in body size and energy consumption. Reportedly, the duration of denning is associated with the amount of fat accumulation and the rate of fat catabolism in bears (Schwartz et al. 1987), and the rate of metabolizing fat stores is proportional to the surface area to body weight ratio. Therefore, males with a large body size than females use a smaller amount of energy and accumulated fat to move and consequently spend a shorter time in the den. Moreover, Manchi and Swenson (2005) detected that the duration of denning decreased with increasing age and body mass in males. When age and body mass are positively correlated in males, the duration of denning might be correlated with both. Large adult males and small subadult males were included in this study, and thus we could detect a negative relationship between age and the duration of denning. However, since age was not selected in the best model, age does not appear to have a strong influence on the timing of den entry and emergence. On the other hand, there might be different reasons that explain why pregnant females spent a longer time in their dens. Similar trends in the timing of entry into and emergence out of dens among female ursids occur elsewhere (van Daele et al. 1990; Friebe and Swenson 2001; Haroldson et al. 2002; Oi and Yamazaki 2006, see Schooley et al. 1994). One of the major objectives of pregnant females is to deliver and rear cubs safely in the den. Hence, they enter the den earlier and emerge later than males and females without cubs. Since reproductive status was affected by age, the duration of denning was correlated with age in this study, which is similar to the findings of Friebe (2001). Although many previous studies have shown that snowfall triggered denning behavior (e.g., Reynolds et al. 1976; Hamilton and Marchinton 1980), no association has been noted between snowy days and den entry in either gender. This may be attributable to the low amount of snowfall in the survey area. The burial of food sources by snow was believed to trigger denning in other regions (Reynolds et al. 1976; Hamilton and Marchinton 1980). However, in our survey region, the amount of snowfall was relatively low in November and December, which is the time that Asiatic black bears enter the dens (e.g., less than 10 cm in November 2012). In addition, the average temperature was higher in some years, even when the first snowfall came early. Thus, snowfall did not have any apparent association with the denning behavior of Asiatic black bears in this study. In conclusion, annual variations in the timing of den entry were attributed more to availability of autumn food sources, autumn temperatures, and the elevation of denning, rather than snowfall. Generally, the timing of den emergence varied depending on spring temperatures, mast productions in the previous year, and the elevation of denning. Furthermore, sex and female reproductive status also affected the timing of den entry and emergence. This study indicated that denning behavior in Asiatic black bears is a complex process and is regulated by several abiotic and biotic factors. Acknowledgments This study was performed as part of the Karuizawa town project for bear management and damage control. We thank the staff in the Karuizawa town office for their assistance and advice in the field and the Nagano Environmental Conservation Research Institute for estimating the age of individuals. We also thank T. Suzuki, Y. Kuroda, N. Izawa, and A. Mitsuke for supporting the fieldwork and D. Zmijewski for providing constructive comments on the manuscript. This study was supported in part by grants from the PRO NATURA FUND and the Mitsui & Co., Ltd. Environment Fund. Literature Cited Craighead, F. C., Jr., and J. J. Craighead. 1972. Grizzly bear prehibernation and denning activities as determined by radio tracking. Wildlife Monographs 3:3–35. ESRI. 2014. ArcGIS Ver. 10.2.1. Environmental System Research Institute, Redlands, California. Friebe, A., J. E. Swenson, and F. Sandegren. 2001. Denning chronology of female brown bears in central Sweden. Ursus 12:37–46. Hamilton, R. J., and R. L. Marchinton. 1980. Denning and related activities of black bears in the coastal plain of North Carolina. Proceedings of the International Conference on Bear Research and Management 4:121–126. Haroldson, M. A., M. A. Ternent, K. A. Gunther, and C. C. Schwartz. 2002. Grizzly bear denning chronology and movements in the Greater Yellowstone Ecosystem. Ursus 13:29–37. Hellgren, E. C. 1998. Physiology of hibernation in bears. Ursus 10:467–477. Hwang, M. H., and D. L. Garshelis. 2007. Activity patterns of Asiatic black bear (Ursus thibetanus) in the Central Mountains of Taiwan. Journal of Zoology 271:203–209. Izumiyama, S., and T. Shiraishi. 2004. Seasonal changes in elevation and habitat use of the Asiatic black bear (Ursus thibetanus) in the Northern Japan Alps. Mammal Study 29:1–8. Japan Meteorological Agency. 2014. Past weather data research. Japan Meteorological Agency, Tokyo. www.jma.go.jp. Accessed 5 October 2014. Johnson, K. G., and M. R. Pelton. 1980. Environmental relationships and the denning period of black bears in Tennessee. Journal of Mammalogy 61:653–660. Judd, S. L., R. R. Knight, and B. M. Blanchard. 1986. Denning of grizzly bears in the Yellowstone National Park Area. Proceedings of the International Conference on Bear Research and Management 6:111–117. Koike, S. 2010. Long-term trends in food habits of Asiatic black bears in the Misaka Mountains on the Pacific coast of central Japan. Mammalian Biology 75:17–28. Koike, S., and T. Hazumi. 2008. Notes on Asiatic black bears denning habits in the Misaka Mountains, central Japan. Ursus 19:80–84. Kozakai, C., K. Yamazaki, Y. Nemoto, A. Nakajima, S. Koike, and K. Kaji. 2009. Behavioral study of free-ranging Japanese black bears II: How do bears manage in a food shortage year? FFPRI Scientific Meeting Report 4:64–66. 134 JOURNAL OF MAMMALOGY Kuramoto, S., T. Igarashi, M. Kadomatsu, and S. Funakoshi. 1995. Annual acornfall variation over 13 years for Quercus mongolica var. grosseserrata in the Uryu Experimental forest. Transaction of the Meeting of the Hokkaido branch of the Japanese Forestry Society 43:146–148 (in Japanese). Lindzey, F. G., and E. C. Meslow. 1976. Winter dormancy in black bears in southwestern Washington. The Journal of Wildlife Management 40:408–415. Linnell, J. D. C., J. E. Swenson, R. Anderson, and B. Barnes. 2000. How vulnerable are denning bears to disturbance? Wildlife Society Bulletin 28:400–413. Maita, K. 1996. Way to encounter bears in the mountains. Yama to Keikokusya, Tokyo, Japan (in Japanese). Manchi, S., and J. E. Swenson. 2005. Denning behavior of Scandinavian brown bear Ursus arctos. Wildlife Biology 11:123–132. Mystrud, I. 1983. Characteristics of summer beds of European brown bears in Norway. Proceedings of the International Conference on Bear Research and Management 5:208–222. Nakajima, A., et al. 2012. Spatial and elevational variation in fruiting phenology of a deciduous oak (Quercus crispula) and its effect on foraging behavior of the Asiatic black bear (Ursus thibetanus). Ecological Research 27:529–538. Nelson, R., H. Wahner, J. Jones, R. Ellefson, and P. Zollman. 1973. Metabolism of bears before, during, and after winter sleep. American Journal of Physiology 224:491–496. Oi, T. 2009. The Japanese black bear: Biology of bears in forest ecosystems. Tokai University Press, Kanagawa, Japan (in Japanese). Oi, T., and K. Yamazaki. 2006. The status of Asiatic black bears in Japan. Pp. 123–133 in Understanding Asian Bears to Secure Their Future (Japan Bear Network, ed.). Japan Bear Network, Ibaraki, Japan. Oka, T., S. Miura, T. Masaki, W. Suzuki, K. Osumi, and S. Saitoh. 2004. Relationship between changes in beechnut production and Asiatic black bears in northern Japan. Journal of Wildlife Management 68:979–986. R Development Core Team. 2013. R: A language and environment for statistical computing. R Foundation for Statistical Computing. http://www.R-project.org/. Accessed 12 December 2014. Reynolds, H., J. A. Curatolo, and R. Quimby. 1976. Denning ecology of grizzly bears in northeastern Alaska. Proceedings of the International Conference on Bear Research and Management 3:403–409. Schooley, R. L., C. R. McLaughlin, G. J. Matula, Jr., and W. B. Krohn. 1994. Denning chronology of female black bears: effects of food, weather, and reproduction. Journal of Mammalogy 75:466–477. Schwartz, C. C., S. D. Miller, and A. W. Franzmann. 1987. Denning ecology of three black bear populations in Alaska. Proceedings of the International Conference on Bear Research and Management 7:281–291. Seryodkin, I., et al. 2003. Denning ecology of brown bears and Asiatic black bears in the Russian Far East. Ursus 14:153–161. Sikes, R. S., W. L. Gannon, and The Animal Care and Use Community of the American Society of Mammalogists. 2011. Guidelines of the American Society of Mammalogists for the use of wild mammals in research. Journal of Mammalogy 92:235–253. Tietje, W. D., and L. R. Ruff. 1980. Denning behavior of black bears in boreal forest of Alberta. Journal of Wildlife Management 44:858–870. Tøien Ø., J. Blake, D. M. Edgar, D. A. Grahn, H. C. Heller, and B. M. Barnes. 2011. Hibernation in black bears: independence of metabolic suppression from body temperature. Science 331:906–909. van Daele, L. J., V. G. Barnes, Jr., and R. B. Smith. 1990. Denning characteristics of brown bears on Kodiak Island, Alaska. Proceedings of the International Conference on Bear Research and Management 8:257–267. White, G. C., and R. A. Garrott. 1990. Analysis of wildlife radio tracking data. Academic Press Inc., New York. Wildlife Management Research Center, Hyogo. 2011. Current status and issues of conservation and management of black bear in Hyogo. IC press, Hyogo, Japan (in Japanese). Willey, C. H. 1974. Aging black bears from first premolar tooth sections. Journal of Wildlife Management 38:97–100. Wooding, J. B., and T. S. Hardisky. 1992. Black bears denning in north-central Florida. Journal of Mammalogy 73:895–898. Yamamoto, T., et al. 2012. Annual and seasonal home range characteristics of female Asian black bears in Karuizawa, Nagano Prefecture, Japan. Ursus 23:218–225. Yamazaki, K. 2011. Behaviors. Pp. 119–144 in Bears in Japan: Biology of Hokkaido Brown Bears and Japanese Black Bears (T. Tsubota and K. Yamazaki, eds.). University of Tokyo Press, Tokyo, Japan (in Japanese). Submitted 7 January 2015. Accepted 1 October 2015. Associate Editor was I. Suzanne Prange.
© Copyright 2026 Paperzz