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. 2020 Feb 21;11:1001. doi: 10.1038/s41467-020-14803-1

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© The Author(s) 2020

Open Access This article is licensed under a Creative Commons Attribution 4.0 International License, which permits use, sharing, adaptation, distribution and reproduction in any medium or format, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license, and indicate if changes were made. The images or other third party material in this article are included in the article’s Creative Commons license, unless indicated otherwise in a credit line to the material. If material is not included in the article’s Creative Commons license and your intended use is not permitted by statutory regulation or exceeds the permitted use, you will need to obtain permission directly from the copyright holder. To view a copy of this license, visit http://creativecommons.org/licenses/by/4.0/.

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Fig. 1 — a Geographical distribution and IUCN conservation status of ibex and wild goat species (LC: Least concern, V: Vulnerable, NT: Near threatened³⁹). Sample sizes: Alpine ibex (C. ibex): N = 29, Iberian ibex (C. pyrenaica): N = 4, Bezoar (C. aegagrus): N = 6, Siberian ibex (C. sibirica): N = 2, Markhor (C. falconeri): N = 1, Nubian ibex (C. nubiana): N = 2. b Maximum likelihood phylogenetic analyses, (c) nucleotide diversity, (d) proportion of the genome with runs of homozygosity (ROH) longer than 2.5 Mb and (e) percentage of polymorphic sites within species that segregate highly deleterious mutations. Confidence intervals are based on downsampling to four individuals matching the sample size of Iberian ibex (100 replicates). Boxplots show the median, the 25th and 75th percentiles, Tukey whiskers (median ± 1.5 times interquartile range), and outliers (^•). Source data are provided as a Source Data file.