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Deer have been a major resource for human populations for thousands of years. Anthropogenic activities, such as hunting, have influenced the genetic structure and distribution of deer populations. In Japan, wild Japanese sika deer (Cervus nippon) have been hunted since ancient times but have also been historically protected as sacred animals in several sanctuaries. Sika deer have been protected for over a thousand years in the religious sanctuary around the Kasuga Taisha Shrine on the Kii Peninsula, located in the center of Japan. Here, we used short sequence repeats (SSR) and mitochondrial DNA (mtDNA) to investigate the genetic diversity, population structure, and demography of Japanese sika deer inhabiting the Kii Peninsula, Japan, and discuss possible anthropogenic influences. Using SSR, three distinct genetic groups were distinguished on the Kii Peninsula: an Eastern genetic group, a Western genetic group, and an isolated genetic group with individuals in the religious sanctuary of Kasuga Taisha Shrine in Nara city. The isolated genetic sanctuary group had only the mtDNA haplotype S4. The SSR genotype data suggested a newer divergence time of the genetic groups of the religious sanctuary than would have occurred as a result of Late Quaternary climate change. This time scale coincided with the establishment of the sanctuary with Kasuga Taisha Shrine. Thus, the religious protection conserved genetic variation over a thousand years. [ABSTRACT FROM AUTHOR]

Carrying capacity is 1 driver of wildlife population dynamics. Although in previous studies carrying capacity was considered to be a fixed entity, it may differ among locations due to environmental variation. The factors underlying variability in carrying capacity, however, have rarely been examined. Here, we investigated spatial heterogeneity in the carrying capacity of Japanese sika deer (Cervus nippon) from 2005 to 2014 in Yamanashi Prefecture, central Japan (mesh with grid cells of 5.5 × 4.6 km) by state-space modeling. Both carrying capacity and density dependence differed greatly among cells. Estimated carrying capacities ranged from 1.34 to 98.4 deer/km2. According to estimated population dynamics, grid cells with larger proportions of artificial grassland and deciduous forest were subject to lower density dependence and higher carrying capacity. We conclude that population dynamics of ungulates may vary spatially through spatial variation in carrying capacity and that the density level for controlling ungulate abundance should be based on the current density level relative to the carrying capacity for each area. [ABSTRACT FROM AUTHOR]