| Literature DB >> 35430616 |
Sam Stroupe1, David Forgacs1,2,3, Andrew Harris2,4, James N Derr5,6, Brian W Davis7,8,9.
Abstract
During the late nineteenth century North American bison underwent a significant population bottleneck resulting in a reduction in population size of over 99% and a species-level near-extinction event. Factors responsible for this destruction included indiscriminate killing, loss of access to suitable habitat, and diseases. At the nadir of this population crash, very few wild plains bison survived and were restricted to Yellowstone National Park, USA and a small number of wild wood bison remained in Wood Buffalo National Park, Canada. However, most surviving bison in the late 1800's were maintained by cattle ranchers in private herds where hybridization between bison with various breeds of domestic cattle was often encouraged. Over the last 20 years, the legacy of this introgression has been identified using mitochondrial DNA and limited nuclear microsatellite analyses. However, no genome-wide assessment has been performed, and some herds were believed to be free of introgression based on current genetic testing strategies. Herein, we report detailed analyses using whole genome sequencing from nineteen modern and six historical bison, chosen to represent the major lineages of bison, to identify and quantitate signatures of nuclear introgression in their recent (within 200 years) history. Both low and high coverage genomes provided evidence for recent introgression, including animals from Yellowstone, Wind Cave, and Elk Island National Parks which were previously thought to be free from hybridization with domestic cattle. We employed multiple approaches, including one developed for this work, to identify putative cattle haplotypes in each bison genome. These regions vary greatly in size and frequency by sample and herd, though we detected domestic cattle introgression in all bison genomes tested. Since our sampling strategy spanned across the diversity of modern bison populations, these finding are best explained by multiple historical hybridization events between these two species with significant genetic recombination over the last 200 years. Our results demonstrate that whole genome sequencing approaches are required to accurately quantitate cattle introgression in bison.Entities:
Mesh:
Year: 2022 PMID: 35430616 PMCID: PMC9013353 DOI: 10.1038/s41598-022-09828-z
Source DB: PubMed Journal: Sci Rep ISSN: 2045-2322 Impact factor: 4.996
Figure 1This graph represents the survival and repopulation of bison by tracking the major founding lineages from wild captured bison to modern populations.The wild herds depicted represent the only populations of bison that survived the population bottleneck in the wild. The founder herds were privately owned bison that were established with bison captured from the wild. The wild and founder herds, seven in total, are the only herds that were in existence during the nadir of the population crash and represent the seven lineages of bison. The derived herds are those that were established with bison from one or more of the seven lineages. The solid arrow (direct transfer) represents direct movement of bison from one population to another, while the dashed line (indirect transfer) represents movement of bison with one or more intermediate populations between the populations depicted. This graph does not include all bison movement but is instead meant to show the contribution and influence that the founding herds have on modern populations based on documented evidence of transferring bison. This figure also identifies populations that are known to have domestic cattle introgression whether through historical documentation or modern genetic testing and the years when each population was established. The Banff National Park population is not the same as the reintroduced animals that currently reside in the park[16,17–19].
Figure 2Map of sampled bison populations. Color-coded by subspecies (Plains or Wood). Shapes are used to differentiate historic (before 1940) and modern (after 1990) samples. The dotted line estimates the historic range of bison in North America[12]. Image generated in R v4 using bisonmap.R script at github.com/agaricx/bisonmap/.
Locations and sources of material used for whole genome sequencing and comparison. Date of sampling and subspecies are shown. All samples were obtained opportunistically. Bone and hide samples were donated from their curated collection. Hair and blood were obtained from annual round-ups from the ranchers responsible for the management of the herd. No animals were accessed solely to sample for this study.
| Sample | Population | Source | Collection Date | Subspecies |
|---|---|---|---|---|
| Caprock_01 | Caprock Canyons State Park (TX, USA) | Texas Parks & Wildlife | 2018 | Plains |
| Caprock_02 | Caprock Canyons State Park (TX, USA) | Texas Parks & Wildlife | 2018 | Plains |
| ElkIslandP_01 | Elk Island National Park—Plains (AB, Canada) | Parks Canada | 2018 | Plains |
| ElkIslandP_02 | Elk Island National Park—Plains (AB, Canada) | Parks Canada | 2018 | Plains |
| ElkIslandW_01 | Elk Island National Park—Wood (AB, Canada) | Parks Canada | 2018 | Wood |
| ElkIslandW_02 | Elk Island National Park—Wood (AB, Canada) | Parks Canada | 2018 | Wood |
| HistP_1886 | Historical Plains Bison (MT, USA) | Smithsonian Institution | 1886 | Plains |
| HistP_1909 | Historical Plains Bison (SK, Canada) | Canadian Museum of Nature | 1909 | Plains |
| HistW_1892 | Historical Wood Bison (AB/NT, Canada) | Canadian Museum of Nature | 1892 | Wood |
| HistW_1921 | Historical Wood Bison (AB/NT, Canada) | Parks Canada | 1921 | Wood |
| HistW_1937 | Historical Wood Bison (AB/NT, Canada) | Smithsonian Institution | 1937 | Wood |
| Mackenzie_01 | Mackenzie Bison Sanctuary (NT, Canada) | Parks Canada | 1999 | Wood |
| Mackenzie_02 | Mackenzie Bison Sanctuary (NT, Canada) | Parks Canada | 1999 | Wood |
| SantaCataIsl_01 | Santa Catalina Island (CA, USA) | Santa Catalina Island Conservancy | 2009 | Plains |
| SantaCataIsl_02 | Santa Catalina Island (CA, USA) | Santa Catalina Island Conservancy | 2009 | Plains |
| Vermejo_01 | Vermejo Park Ranch (NM, USA) | Turner Enterprises, Inc | 2000 | Plains |
| Vermejo_02 | Vermejo Park Ranch (NM, USA) | Turner Enterprises, Inc | 2001 | Plains |
| WindCave_01 | Wind Cave National Park (SD, USA) | US National Parks Service | 2018 | Plains |
| WindCave_02 | Wind Cave National Park (SD, USA) | US National Parks Service | 2018 | Plains |
| Yellowstone_01 | Yellowstone National Park (WY/MT, USA) | US National Parks Service | 2011 | Plains |
| Yellowstone_02 | Yellowstone National Park (WY/MT, USA) | Turner Enterprises, Inc | 2011 | Plains |
| Yellowstone_03 | Yellowstone National Park (WY/MT, USA) | US National Parks Service | 2000 | Plains |
| Yellowstone_04 | Yellowstone National Park (WY/MT, USA) | US National Parks Service | 2000 | Plains |
| Yellowstone_05 | Yellowstone National Park (WY/MT, USA) | US National Parks Service | 2009 | Plains |
| Yellowstone_1925 | Yellowstone National Park (WY/MT, USA) | Yellowstone Heritage and Research Center | 1925 | Plains |
| Angus_01 | NCBI | SRR1425124 | – | Cattle |
| Charolais_01 | NCBI | SRR1355258 | – | Cattle |
| Hereford_01 | NCBI | SRR2226524 | – | Cattle |
| Holstein_01 | NCBI | SRR1365147 | – | Cattle |
| NCBI | SRR7284794 | – | Water Buffalo |
Figure 3TreeMix estimation of phylogenetic network and relationships among bison populations and domestic cattle with eight migration events. All modern bison were assigned to their respective populations while historic samples were included as individuals. A representative of each of the four cattle breeds (Angus, Charolais, Hereford, and Holstein) were assigned to the cattle population. Of the migration edges five of the eight are between the cattle lineage and bison populations. The migration with the highest weight is shown between cattle and Caprock while migrations of smaller weights can be seen between Cattle and historical wood bison, Elk Island-Plains, Yellowstone and a group consisting of Wind Cave and Santa Catalina. Three additional migration events can be seen between historical wood bison and modern wood bison populations as well as between historical plains and wood bison. These migration events shown agree with the historic documentation of introgression events and movements of bison.
Figure 4(a) D-statistics from individual level all-to-all comparisons of ancestral and derived allele frequencies. Negative D-statistic indicates that H1 (bison) is closer to H3 (Angus cattle) then H2 (bison). (b) Phylogenetic tree to show potential gene flow between B. taurus (H3) and B. bison (H1) or B. bison (H2).
Figure 5Whole genome heatmap of detected introgressed blocks by HybridCheck (a) and IntrogressionID (b) for individual WindCave_02. Chromosomes are listed numerically along the y-axis and their lengths are represented by the length of the respective heatmap box along the x-axis. Across each chromosome, the grey coloration indicates regions of no signal for introgression, the red coloration indicates signal of introgression and the blue coloration in (a) indicates signals of introgression that overlap across all sample comparisons for HybridCheck. The zoomed in box shows the HybridCheck output data plotted in a line graph with percent sequence similarity across the y-axis and base pair position across the x-axis.