Abstract

The snub-nosed monkey genus (Rhinopithecus) comprises five closely related species (R. avunculus, R. bieti, R. brelichi, R. roxellana, and R. strykeri). All are among the world's rarest and most endangered primates. However, the genomic impact associated with their population decline remains unknown. We analyzed population genomic data of all five snub-nosed monkey species to assess their genetic diversity, inbreeding level, and genetic load. For R. roxellana, R. bieti, and R. strykeri, population size is positively correlated with genetic diversity and negatively correlated with levels of inbreeding. Other species, however, which possess small population sizes, such as R. brelichi and R. avunculus, show high levels of genetic diversity and low levels of genomic inbreeding. Similarly, in the three populations of R. roxellana, the Shennongjia population, which possesses the lowest population size, displays a higher level of genetic diversity and lower level of genomic inbreeding. These findings suggest that although R. brelichi and R. avunculus and the Shennongjia population might be at risk, it possess significant genetic diversity and could thus help strengthen their long-term survival potential. Intriguingly, R. roxellana with large population size possess high genetic diversity and low level of genetic load, but they show the highest recent inbreeding level compared with the other snub-nosed monkeys. This suggests that, despite its large population size, R. roxellana has likely been experiencing recent inbreeding, which has not yet affected its mutational load and fitness. Analyses of homozygous-derived deleterious mutations identified in all snub-nosed monkey species indicate that these mutations are affecting immune, especially in smaller population sizes, indicating that the long-term consequences of inbreeding may be resulting in an overall reduction of immune capability in the snub-nosed monkeys, which could provide a dramatic effect on their long-term survival prospects. Altogether, our study provides valuable information concerning the genomic impact of population decline of the snub-nosed monkeys. We revealed multiple counterintuitive and unexpected patterns of genetic diversity in small and large population, which will be essential for conservation management of these endangered species.

Highlights

  • The snub-nosed monkey genus (Rhinopithecus) comprises five closely related species

  • As for R. brelichi and R. avunculus, we found that the smallest population of R. roxellana, i.e., Shennongjia National Nature Reserve (SNJ) population (∼1,200 individuals) possessed relatively higher levels of genetic diversity (He = 0.044%) compared with the Qinling mountain (QL) population (He = 0.038%, ∼5,500 individuals, p = 0.0193, Wilcox test) and even do for the largest population of R. roxellana, i.e., SG population (He = 0.046%, approximately 16,500 individuals, p = 0.5695, Wilcox test)

  • We found that R. brelichi (FROH = 49.37%) possessed the lowest level of genomic inbreeding and that R. bieti (FROH = 78.86%) and R. strykeri (FROH = 73.43%) have the highest level among the five snub-nosed monkey species (FROH = 68.11–78.86%) (p < 0.05, Wilcox test)

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Summary

Introduction

The snub-nosed monkey genus (Rhinopithecus) comprises five closely related species. The golden snub-nosed monkey (R. roxellana), Yunnan snub-nosed monkey (R. bieti), and Guizhou snub-nosed monkey (R. brelichi) are endemic to China, while the Tonkin snub-nosed monkey (R. avunculus) is distributed in northern Vietnam, and the Myanmar/Nujiang snub-nosed monkey (R. strykeri) inhabits northern Myanmar and the Nujiang prefecture in China (Geissmann et al, 2011; Liedigk et al, 2012; Ma et al, 2014; Meyer et al, 2017) (Figure 1). There are only 22,500 individuals of R. roxellana, the most numerous species, which are isolated in three fragmented populations in the Minshan and Qionglai mountains (SG; Sichuan/Gansu provinces), the Qinling mountain (QL; Shanxi province), and the Shennongjia National Nature Reserve (SNJ; Hubei province) (Quan and Xie, 2002; Liu et al, 2015; Li et al, 2018) Other species, such as R. bieti and R. strykeri are only ∼3,000 (Li et al, 2018; Zhao et al, 2019) and ∼950 individuals (Meyer et al, 2017; Ren et al, 2017; Yang et al, 2019), respectively, and there are fewer than 400 and 200 individuals of most endangered species R. brelichi (Guo et al, 2020) and R. avunculus (Nadler, 2018) left in the wild, respectively

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