Christopher C. Kyriazis’s research while affiliated with University of California, Los Angeles and other places

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Publications (29)


Figure 3: Inferred versus simulated DFEs from simulated human genomes. Simulations were performed using a human out-of-Africa demographic model with a gamma-distributed DFE acting on exons (see Methods). DFE is inferred separately for each of the three extant populations (CEU, CHB, and YRI) by three different methods: GRAPES, polyDFE, and dadi-cli. (A-B) Mean absolute value of selection coefficient (|E(s)|) and shape parameter are shown for each DFE inferred from all three simulated datasets, with median values marked by horizontal bars and simulated values represented by dashed horizontal lines. (C) Binned distribution of s implied by the average DFE inferred from the three simulated datasets (averaging the inferred gamma parameters); white bars represent the distribution used in the simulation.
Figure 4: Inferred versus simulated DFEs from simulated vaquita genomes. Simulations were performed using a two-epoch model of vaquita porpoise demography with a gamma-distributed DFE acting on nonsynonymous mutations with a relationship between the selection coefficient (s) and dominance coefficient (h) (see Methods). The DFE is inferred by analyzing all simulated genomes jointly by one of three different methods: GRAPES, polyDFE, and dadi-cli. (A-B) Mean absolute value of selection coefficient (|E(s)|) and shape parameter are shown for each DFE inferred from all three simulated datasets, with median values marked by horizontal bars and simulated values represented by dashed horizontal lines. (C) Binned distribution of 2hs implied by the simulated DFE compared with the distribution of s implied by the average DFE inferred for each method from the three simulated datasets (averaging the inferred gamma parameters). The distribution of 2hs is multimodal because of the simulated relationship between h and s (see text).
Figure 6: Power to detect selective sweeps as a function of local recombination rate. This figure shows the same power estimates shown in Figure 5, but with the genomic segments plotted against their average recombination rates instead of position along chromosome 1. Genomic segments were simulated with sweeps under a three population out-of-Africa model and with background selection from deleterious mutations in exons. Three methods for detecting sweeps were applied to simulated data: sweepfinder2 (top row-labeled CLR), diploshic (middle row), and reduced diversity (π) (bottom row). Power (true positive rate) is shown for these methods for the CEU and YRI samples (left and right respectively). The thresholds of the test statistics were set to obtain a 5% false positive rate under a neutral null model (blue) and a null model with background selection from deleterious mutations in exons (red). Fitted lines represent loess smoothed regressions.
Accessible, realistic genome simulation with selection using stdpopsim
  • Preprint
  • File available

March 2025

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12 Reads

Graham Gower

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Nathaniel S. Pope

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Murillo F. Rodrigues

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Andrew D. Kern

Selection is a fundamental evolutionary force that shapes patterns of genetic variation across species. However, simulations incorporating realistic selection along heterogeneous genomes in complex demographic histories are challenging, limiting our ability to benchmark statistical methods aimed at detecting selection and to explore theoretical predictions. stdpopsim is a community-maintained simulation library that already provides an extensive catalog of species-specific population genetic models. Here we present a major extension to the stdpopsim framework that enables simulation of various modes of selection, including background selection, selective sweeps, and arbitrary distributions of fitness effects (DFE) acting on annotated subsets of the genome (for instance, exons). This extension maintains stdpopsim 's core principles of reproducibility and accessibility while adding support for species-specific genomic annotations and published DFE estimates. We demonstrate the utility of this framework by benchmarking methods for demographic inference, DFE estimation, and selective sweep detection across several species and scenarios. Our results demonstrate the robustness of demographic inference methods to selection on linked sites, reveal the sensitivity of DFE-inference methods to model assumptions, and show how genomic features, like recombination rate and functional sequence density, influence power to detect selective sweeps. This extension to stdpopsim provides a powerful new resource for the population genetics community to explore the interplay between selection and other evolutionary forces in a reproducible, low-barrier framework.

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Constraining models of dominance for nonsynonymous mutations in the human genome

September 2024

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19 Reads

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1 Citation

Dominance is a fundamental parameter in genetics, determining the dynamics of natural selection on deleterious and beneficial mutations, the patterns of genetic variation in natural populations, and the severity of inbreeding depression in a population. Despite this importance, dominance parameters remain poorly known, particularly in humans or other non-model organisms. A key reason for this lack of information about dominance is that it is extremely challenging to disentangle the selection coefficient (s) of a mutation from its dominance coefficient (h). Here, we explore dominance and selection parameters in humans by fitting models to the site frequency spectrum (SFS) for nonsynonymous mutations. When assuming a single dominance coefficient for all nonsynonymous mutations, we find that numerous h values can fit the data, so long as h is greater than ~0.15. Moreover, we also observe that theoretically-predicted models with a negative relationship between h and s can also fit the data well, including models with h = 0.05 for strongly deleterious mutations. Finally, we use our estimated dominance and selection parameters to inform simulations revisiting the question of whether the out-of-Africa bottleneck has led to differences in genetic load between African and non-African human populations. These simulations suggest that the relative burden of genetic load in non-African populations depends on the dominance model assumed, with slight increases for more weakly recessive models and slight decreases shown for more strongly recessive models. Moreover, these results also demonstrate that models of partially recessive nonsynonymous mutations can explain the observed severity of inbreeding depression in humans, bridging the gap between molecular population genetics and direct measures of fitness in humans. Our work represents a comprehensive assessment of dominance and deleterious variation in humans, with implications for parameterizing models of deleterious variation in humans and other mammalian species.


The influence of gene flow on population viability in an isolated urban caracal population

April 2024

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67 Reads

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7 Citations

Molecular Ecology

Wildlife populations are becoming increasingly fragmented by anthropogenic development. Small and isolated populations often face an elevated risk of extinction, in part due to inbreeding depression. Here, we examine the genomic consequences of urbanization in a caracal ( Caracal caracal ) population that has become isolated in the Cape Peninsula region of the City of Cape Town, South Africa, and is thought to number ~50 individuals. We document low levels of migration into the population over the past ~75 years, with an estimated rate of 1.3 effective migrants per generation. As a consequence of this isolation and small population size, levels of inbreeding are elevated in the contemporary Cape Peninsula population (mean F ROH = 0.20). Inbreeding primarily manifests as long runs of homozygosity >10 Mb, consistent with the effects of isolation due to the rapid recent growth of Cape Town. To explore how reduced migration and elevated inbreeding may impact future population dynamics, we parameterized an eco‐evolutionary simulation model. We find that if migration rates do not change in the future, the population is expected to decline, though with a low projected risk of extinction. However, if migration rates decline or anthropogenic mortality rates increase, the potential risk of extinction is greatly elevated. To avert a population decline, we suggest that translocating migrants into the Cape Peninsula to initiate a genetic rescue may be warranted in the near future. Our analysis highlights the utility of genomic datasets coupled with computational simulation models for investigating the influence of gene flow on population viability.


Figure 3: Inference of the Distribution of Fitness Effects (DFE) of non-synonymous mutations under varying strengths of recombination. Comparison of the discretized DFE for non-synonymous mutations between the true DFE and the average inferred DFE for each
The impact of non-neutral synonymous mutations when inferring selection on non-synonymous mutations

February 2024

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37 Reads

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1 Citation

The distribution of fitness effects (DFE) describes the proportions of new mutations that have different effects on reproductive fitness. Accurate measurements of the DFE are important because the DFE is a fundamental parameter in evolutionary genetics and has implications for our understanding of other phenomena like complex disease or inbreeding depression. Current computational methods to infer the DFE for nonsynonymous mutations from natural variation first estimate demographic parameters from synonymous variants to control for the effects of demography and background selection. Then, conditional on these parameters, the DFE is then inferred for nonsynonymous mutations. This approach relies on the assumption that synonymous variants are neutrally evolving. However, some evidence points toward synonymous mutations having measurable effects on fitness. To test whether selection on synonymous mutations affects inference of the DFE of nonsynonymous mutations, we simulated several possible models of selection on synonymous mutations using SLiM and attempted to recover the DFE of nonsynonymous mutations using Fit∂a∂i, a common method for DFE inference. Our results show that the presence of selection on synonymous variants leads to incorrect inferences of recent population growth. Furthermore, under certain parameter combinations, inferences of the DFE can have an inflated proportion of highly deleterious nonsynonymous mutations. However, this bias can be eliminated if the correct demographic parameters are used for DFE inference instead of the biased ones inferred from synonymous variants. Our work demonstrates how unmodeled selection on synonymous mutations may affect downstream inferences of the DFE.


Population structure and sample origins for the fin whale genomes obtained in this study
A Thirty skin samples were collected along Eastern North Pacific (ENP) locations near Alaska (AK), British Columbia (BC), Washington (WA), Oregon (OR), and California (CA) from 1995 to 2017. Twenty samples were collected in seven sites within the Gulf of California (GOC) from Bahía de La Paz and Los Frailes in the southern Gulf to Bahía de los Ángeles, Puerto Refugio, and Bahía Kino around the Midriff islands (Table S1). B PCA for 50 samples are colored by their location origin. The admixed individuals are labeled. C Admixture analyses supported two ancestral populations (K = 2). The map in A was generated with the R package ggOceanMaps¹¹² which uses publicly available bathymetry data from the ETOPO1 1-arc minute global relief data set distributed by the National Center for Environmental Information¹¹³ (https://www.ncei.noaa.gov/products/etopo-global-relief-model). Source data are provided as a Source Data file.
ROH and distribution of heterozygosity across the genome
A Points of genome-wide heterozygosity for each sample are ranked by decreasing heterozygosity from top to bottom. Circles at the bottom axis denote heterozygosity in other mammals. Barplots present summed lengths of short (0.1 Mb ≤ ROH < 1 Mb) to long (>5 Mb) ROH per individual (top axis). B The left panel shows per-site heterozygosity in non-overlapping 1-Mb windows across called scaffolds. The genome-wide heterozygosity value is annotated as “Mean het”. The right panel summarizes the distribution of per-window heterozygosity. Individuals with divergent demographic histories were selected as examples. ENPAK19 represents the large outbred Eastern North Pacific population that recently experienced whaling. ENPCA09 is an admixed individual. GOC002 and GOC125 belong to the small, isolated Gulf of California population. Source data are provided as a Source Data file.
Demographic history inferred for fin whale populations
A The historical demography of the Eastern North Pacific (ENP; green) population is best represented by a single-population 3-epoch model. This model has an initial expansion, occurring around 115 thousand years ago (kya; 4424 generations) followed by an ~99% reduction only 26 to 52 years ago (one or two generations), during the whaling period for this species in the North Pacific (red horizontal bar). B Fit of the SFS from each demographic model (1- to 4-epoch) obtained with ∂a∂i for the ENP population to the SFS from the empirical data (Data). The SFS distribution for the 3-epoch model represented in A shows the best fit to the data. C Two-population model showing an ancestral effective population size expansion from approximately 16,000 to 25,000 individuals during the Eemian interglacial period >100 kya (between the Illinois [gray bar] and Wisconsin [light blue bar] glaciations). The two populations diverged around 16 kya, during the Last Glacial Maximum. After the divergence, the ENP population (green) remained at an effective population size of ~17,000, whereas the Gulf of California (GOC; orange) population has remained small at an effective size of Ne = 114. These populations have maintained low levels of asymmetrical gene flow, with higher migration rates from ENP into GOC (3.42E-03), than vice-versa (9.24E-05). However, when scaled by the receiving population’s effective size, the GOC is only receiving 0.39 effective migrants/generation, while the ENP receives 1.61 effective migrants/gen. The black line to the right shows the relative sea level¹¹⁴. Source data are provided as a Source Data file.
Increase in putatively deleterious variation in the GOC compared to the ENP fin whales
Sample sizes: Gulf of California (GOC) N = 17, Eastern North Pacific (ENP) N = 27. A The GOC fin whales contain significantly fewer heterozygous and more homozygous derived genotypes in all four functional categories of variants. B Only putatively deleterious nonsynonymous alleles (DEL) are significantly elevated (two-tailed MWU test p < 0.001; Table S15) in the GOC compared with the ENP population. The ENP and GOC fin whales contain similar numbers of derived neutral alleles (SYN: synonymous and TOL: tolerated nonsynonymous), and putatively deleterious loss-of-function (LOF) alleles. For A and B, we used two-tailed Mann-Whitney U tests without multiple testing adjustment (the exact p values for the Mann–Whitney U tests are given in Table S15 in the supplementary material). In the boxplots, the notch indicates the median, and the boxes represent the 25th and 75th percentiles. The whiskers extend to data points no >1.5 * IQR (inter-quantile range) from the hinges and the points show outliers beyond the whiskers. CRXY\documentclass[12pt]{minimal} \usepackage{amsmath} \usepackage{wasysym} \usepackage{amsfonts} \usepackage{amssymb} \usepackage{amsbsy} \usepackage{mathrsfs} \usepackage{upgreek} \setlength{\oddsidemargin}{-69pt} \begin{document}$${R}_{{XY}}$$\end{document} and RXY2\documentclass[12pt]{minimal} \usepackage{amsmath} \usepackage{wasysym} \usepackage{amsfonts} \usepackage{amssymb} \usepackage{amsbsy} \usepackage{mathrsfs} \usepackage{upgreek} \setlength{\oddsidemargin}{-69pt} \begin{document}$${R}_{{XY}}^{2}$$\end{document} statistics in GOC (X) and ENP (Y) populations. RXY>1\documentclass[12pt]{minimal} \usepackage{amsmath} \usepackage{wasysym} \usepackage{amsfonts} \usepackage{amssymb} \usepackage{amsbsy} \usepackage{mathrsfs} \usepackage{upgreek} \setlength{\oddsidemargin}{-69pt} \begin{document}$${R}_{{XY}} > 1$$\end{document} (dashed gray line) indicates a relative accumulation of the corresponding mutation category in the GOC population. Similarly, RXY2>1\documentclass[12pt]{minimal} \usepackage{amsmath} \usepackage{wasysym} \usepackage{amsfonts} \usepackage{amssymb} \usepackage{amsbsy} \usepackage{mathrsfs} \usepackage{upgreek} \setlength{\oddsidemargin}{-69pt} \begin{document}$${R}_{{XY}}^{2} > 1$$\end{document} indicates relative accumulation of homozygous mutations. The 2x standard error based on the jackknife distribution is denoted as error bar, the circles in the center of the error bars represent the RXY or R²XY values. For C we used a two-tailed Z score test without multiple testing adjustment (RXYZ-test significant values: pSYN = 0.61, pDEL = 0.02, pTOL = 0.98, pLOF = 0.88; R²XYZ-test significant values: pSYN = 0, pDEL = 2.60e-142, pTOL = 3.73e-234, pLOF = 9.91e-17). Significance levels: ns, not significant; *p < 0.05; **p < 0.01; ***p < 0.001; ****p < 0.0001. Source data are provided as a Source Data file.
Simulations of heterozygosity, inbreeding coefficient, and genetic load
Representations of the demographic scenarios under which the simulations were performed are shown at the top. A Results for simulations under single-population 3-epoch model for the ENP population (green), including mean heterozygosity, levels of inbreeding (FROH>1Mb), and mean genetic load. Each quantity was measured prior to the onset of the whaling bottleneck (pre-bott), after two generations at the bottleneck Ne = 305 (2 gens), after 20 generations at the bottleneck Ne = 305 (20 gens), and 20 generations following the onset bottleneck where recovery to Ne = 1000 occurred after just two generations at Ne = 305 (20 gens w/ recov). In the demographic representations, the dashed line indicates the timing of sampling. B Results for simulations under our chosen two-population model. Each quantity is shown for the ENP (green) and GOC (orange; GOC w/mig) populations at the end of the simulation. We also simulated under a no migration demographic scenario for the GOC population (orange; GOC w/o mig). Note the much lower heterozygosity, higher inbreeding, and higher genetic load in the GOC population in the absence of migration. In the demographic representations, the sampled population, ENP or GOC, are shown in green or orange, respectively, and the presence/absence of migration indicated with the black arrows. For all boxplots, the notch indicates the median, and the boxes represent the 25th and 75th percentiles. The whiskers extend to data points no >1.5 * IQR (inter-quantile range) from the hinges and the solid squares show outliers beyond the whiskers. Hollow squares denote each simulation’s value. Source data are provided as a Source Data file.
The genomic footprint of whaling and isolation in fin whale populations

September 2023

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301 Reads

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16 Citations

Twentieth century industrial whaling pushed several species to the brink of extinction, with fin whales being the most impacted. However, a small, resident population in the Gulf of California was not targeted by whaling. Here, we analyzed 50 whole-genomes from the Eastern North Pacific (ENP) and Gulf of California (GOC) fin whale populations to investigate their demographic history and the genomic effects of natural and human-induced bottlenecks. We show that the two populations diverged~16,000 years ago, after which the ENP population expanded and then suffered a 99% reduction in effective size during the whaling period. In contrast, the GOC population remained small and isolated, receiving less than one migrant per generation. However, this low level of migration has been crucial for maintaining its viability. Our study exposes the severity of whaling, emphasizes the importance of migration, and demonstrates the use of genome-based analyses and simulations to inform conservation strategies.


The influence of gene flow on population viability in an isolated urban caracal population

July 2023

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172 Reads

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1 Citation

Wildlife populations are becoming increasingly fragmented by anthropogenic development. Such small and isolated populations often face an elevated risk of extinction, in part due to inbreeding depression. Here, we examine the genomic consequences of urbanization in a caracal ( Caracal caracal ) population that has become isolated in the Cape Peninsula region of the city of Cape Town, South Africa and is thought to number ∼50 individuals. We document low levels of migration into the population over the past ∼75 years, with an estimated rate of 1.3 effective migrants per generation. As a consequence of this isolation and small population size, levels of inbreeding are elevated in the contemporary Cape Peninsula population (mean F ROH>1Mb =0.20). Inbreeding primarily manifests as long runs of homozygosity >10Mb, consistent with the effects of isolation due to the rapid recent growth of Cape Town. To explore how reduced migration and elevated inbreeding may impact future population dynamics, we parameterized an eco-evolutionary simulation model. We find that if migration rates do not change in the future, the population is expected to decline only slightly, with a low projected risk of extinction. However, if migration rates decline or anthropogenic mortality rates increase, the potential risk of extinction is greatly elevated. To avert a population decline, we suggest that translocating migrants into the Cape Peninsula to initiate a genetic rescue may be warranted in the near future. Our analysis highlights the utility of genomic datasets coupled with computational simulation models for investigating the influence of gene flow on population viability.


Using Computational Simulations to Model Deleterious Variation and Genetic Load in Natural Populations

July 2023

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45 Reads

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16 Citations

The American Naturalist

Deleterious genetic variation is abundant in wild populations, and understanding the ecological and conservation implications of such variation is an area of active research. Genomic methods are increasingly used to quantify the impacts of deleterious variation in natural populations; however, these approaches remain limited by an inability to accurately predict the selective and dominance effects of mutations. Computational simulations of deleterious variation offer a complementary tool that can help overcome these limitations, although such approaches have yet to be widely employed. In this perspective article, we aim to encourage ecological and conservation genomics researchers to adopt greater use of computational simulations to aid in deepening our understanding of deleterious variation in natural populations. We first provide an overview of the components of a simulation of deleterious variation, describing the key parameters involved in such models. Next, we discuss several approaches for validating simulation models. Finally, we compare and validate several recently proposed deleterious mutation models, demonstrating that models based on estimates of selection parameters from experimental systems are biased toward highly deleterious mutations. We describe a new model that is supported by multiple orthogonal lines of evidence and provide example scripts for implementing this model (https://github.com/ckyriazis/simulations_review).


Figure 1. Parameters of the gamma distribution and the inferred DFE under different levels of recessive lethals A. Inference of the shape (a) and scale () parameters under a gamma DFE model from simulated data with different levels of recessive lethals using 1000 haploid genomes in each simulation.
Figure 3: Relationship between the percent of new mutations that are recessive lethal and the predicted number of segregating recessive lethals per diploid under mutation-selection-drift balance for humans and Drosophila melanogaster under varying effective population sizes. X-axis denotes the percent of new nonsynonymous mutations that are recessive lethal and Y-axis denotes the resulting number of segregating recessive lethals per diploid. Red shading indicates the range of empirical estimates of segregating recessive lethals for each species.
Quantifying the fraction of new mutations that are recessive lethal

April 2023

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35 Reads

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14 Citations

Evolution

The presence and impact of recessive lethal mutations has been widely documented in diploid outcrossing species. However, precise estimates of the proportion of new mutations that are recessive lethal remain limited. Here, we evaluate the performance of Fit∂a∂i, a commonly-used method for inferring the distribution of fitness effects (DFE), in the presence of lethal mutations. Using simulations, we demonstrate that in both additive and recessive cases, inference of the deleterious non-lethal portion of the DFE is minimally impacted by a small proportion (<10%) of lethal mutations. Additionally, we demonstrate that, while Fit∂a∂i cannot estimate the fraction of recessive lethal mutations, Fit∂a∂i can accurately infer the fraction of additive lethal mutations. Finally, as an alternative approach to estimate the proportion of mutations that are recessive lethal, we employ models of mutation-selection-drift balance using existing genomic parameters and estimates of segregating recessive lethals for humans and Drosophila melanogaster. In both species, the segregating recessive lethal load can be explained by a very small fraction (<1%) of new nonsynonymous mutations being recessive lethal. Our results refute recent assertions of a much higher proportion of mutations being recessive lethal (4-5%), while highlighting the need for additional information on the joint distribution of selection and dominance coefficients.



FIG. 1. Moose sampling and population structure. (A) Map of North America including localities for individuals sampled for genomic data in our study. Note that Sweden is excluded. (B) PCA of 50,361 LD-pruned SNPs for all sequenced samples. The inset are results when down-sampling to one individual per population and excluding the Swedish sample. (C ) Tree based on identity-by-state constructed using 50,361 LD-pruned SNPs. (D) fastSTRUCTURE results for K = 3. See supplementary figure S1, Supplementary Material online for results with varying K values and supplementary figure S2, Supplementary Material online for results when down-sampling to four unrelated individuals each from Isle Royale and Minnesota.
FIG. 2. Moose genetic diversity and inbreeding. (A) Comparison of mean genome-wide diversity in three moose populations to published values for other mammals. Note that two estimates are included for the same Swedish moose sample: one from this paper, and a second from Dussex et al. (2020) (denoted with an asterisk), and these estimates differ likely due to differences in bioinformatic pipelines. (B) Plots of mean genomewide diversity and summed ROH levels for North American moose genomes, with the corresponding F ROH values on the right-hand axis. Note that we were not able to obtain ROH calls for the Sweden sample due to its differing population origin. (C ) Per-site heterozygosity plotted in nonoverlapping 1 Mb windows for representative individuals from Sweden, Minnesota, and Isle Royale. To facilitate visualization, results are plotted only for the first 10 chromosomes. See supplementary figure S4, Supplementary Material online for plots of all individuals.
FIG. 3. Demographic inference results. (A) Schematic of the best-fit four-epoch model based on the site frequency spectrum (SFS) for the Minnesota sample. The right-hand axis assumes a generation time of 8 years. Numbers denote maximum likelihood estimates of the effective population sizes at various time points. Note the brief and severe bottleneck occurring near the onset of the Holocene. See supplementary table S2, Supplementary Material online for parameters of the second-best fitting run, which differs somewhat in bottleneck duration and magnitude and pre-/post-bottleneck population sizes. (B) Comparison of the empirical projected folded SFS from the Minnesota sample with the SFS predicted by the model shown in (A).
Genomic Underpinnings of Population Persistence in Isle Royale Moose

February 2023

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250 Reads

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20 Citations

Molecular Biology and Evolution

Island ecosystems provide natural laboratories to assess the impacts of isolation on population persistence. However, most studies of persistence have focused on a single species, without comparisons to other organisms they interact with in the ecosystem. The case study of moose and gray wolves on Isle Royale allows for a direct contrast of genetic variation in isolated populations that have experienced dramatically differing population trajectories over the past decade. Whereas the Isle Royale wolf population recently declined nearly to extinction due to severe inbreeding depression, the moose population has thrived and continues to persist, despite having low genetic diversity and being isolated for ∼120 years. Here, we examine the patterns of genomic variation underlying the continued persistence of the Isle Royale moose population. We document high levels of inbreeding in the population, roughly as high as the wolf population at the time of its decline. However, inbreeding in the moose population manifests in the form of intermediate-length runs of homozygosity suggestive of historical inbreeding and purging, contrasting with the long runs of homozygosity observed in the smaller wolf population. Using simulations, we confirm that substantial purging has likely occurred in the moose population. However, we also document notable increases in genetic load, which could eventually threaten population viability over the long term. Overall, our results demonstrate a complex relationship between inbreeding, genetic diversity, and population viability that highlights the use of genomic datasets and computational simulation tools for understanding the factors enabling persistence in isolated populations.


Citations (26)


... Indeed, the distribution of hs is much more accurately estimated ( Figure 4C). Overall, these results are consistent with prior work showing that it is challenging to separately infer the DFE of s along with h (Veeramah et al., 2014;Kyriazis and Lohmueller, 2024;Balick et al., 2022) and that a large proportion (> 5%) of recessive deleterious mutations can confound inferences of s (Wade et al., 2023). Given the plethora of evidence for recessive deleterious mutations (Mukai et al., 1972;Agrawal and Whitlock, 2011;Huber, Durvasula, et al., 2018;Di and Lohmueller, 2024), these results suggest the need for care in DFE inference. ...

Reference:

Accessible, realistic genome simulation with selection using stdpopsim
Constraining models of dominance for nonsynonymous mutations in the human genome

... Episodic gene flow occurring amongst demes could theoretically retain N e within each individual deme at the level of a panmictic global population (Charlesworth 2009). Even under realistic scenarios of unequal gene flow amongst natural populations, admixture has the potential to increase N e of individual demes (e.g., Saremi et al. 2019;Kyriazis et al. 2024). ...

The influence of gene flow on population viability in an isolated urban caracal population
  • Citing Article
  • April 2024

Molecular Ecology

... For DEL/SYN variants, the ratios of both homozygous and heterozygous-derived genotypes were higher in the northern lineage than in the southern lineage (Fig. 4I, Additional file 2: Table S15). Furthermore, we used the counts of all four mutation types to assess the genetic load for the two lineages [29]. In general, we found that the number of homozygous-derived genotypes was higher in the northern lineage for all mutation types, especially for the DEL mutation type being the most significant (Fig. 4J, Additional file 2: Table S15). ...

The genomic footprint of whaling and isolation in fin whale populations

... pairwise nucleotide identity with a caracal mitochondrial genome (KP202272) [57] (Figure 3). This high level of similarity is not surprising given the recent study which showed that the Caracal population in Cape Town have elevated levels of inbreeding [58]. A comparison with mitochondrial genomes of two other members of the caracal lineage, an African golden cat (Caracal aurata) (KP202255) and a serval (Leptailurus serval) (KP202286) [57], showed they share 91.1-93% pairwise nucleotide identity. ...

The influence of gene flow on population viability in an isolated urban caracal population

... Thus, the stdpopsim catalog provides Annotation objects based on species' publicly available functional genomic elements and DFE objects based on published DFE estimates ( Figure 1A). By using (Hunt et al. 2018) ensembl Havana CDS (Hunt et al. 2018) Distribution of Fitness effects DFEs Deleterious Gamma DFE Deleterious Log Normal DFE Deleterious Gamma DFE plus lethals (Kyriazis et al. 2023) example_with_selection.py 1 import stdpopsim 2 3 species = stdpopsim.get_species("HomSap") 4 contig = species.get_contig( ...

Using Computational Simulations to Model Deleterious Variation and Genetic Load in Natural Populations
  • Citing Article
  • July 2023

The American Naturalist

... Indeed, the distribution of hs is much more accurately estimated ( Figure 4C). Overall, these results are consistent with prior work showing that it is challenging to separately infer the DFE of s along with h (Veeramah et al., 2014;Kyriazis and Lohmueller, 2024;Balick et al., 2022) and that a large proportion (> 5%) of recessive deleterious mutations can confound inferences of s (Wade et al., 2023). Given the plethora of evidence for recessive deleterious mutations (Mukai et al., 1972;Agrawal and Whitlock, 2011;Huber, Durvasula, et al., 2018;Di and Lohmueller, 2024), these results suggest the need for care in DFE inference. ...

Quantifying the fraction of new mutations that are recessive lethal

Evolution

... Some researchers advocate that the most serious threat to population survival is inbreeding depression caused by an accumulation of realized genetic load. Inbreeding is exacerbated in small and isolated population fragments and the suggested management strategy is to avoid introducing masked load when translocating from large to small populations (Dussex et al., 2023;Grossen et al., 2020;Kyriazis et al., 2023;Robinson et al., 2018Robinson et al., , 2019Teixeira & Huber, 2021). Such a strategy would recommend that managers should be careful when moving individuals among population fragments. ...

Models based on best-available information support a low inbreeding load and potential for recovery in the vaquita

Heredity

... Regardless, the high prevalence of ROH is a concern for this species' genetic health, demonstrating the need for continued conservation attention [63]. It is worth noting that the proportion of the genome contained within ROH is low compared with other mammalian [64][65][66] and avian [67] systems with small population sizes. Indeed, a recent study that explored the island size-diversity relationship in smaller islands found a much higher ROH content in islands smaller than Ghizo (the smallest island in this dataset; [23]). ...

Genomic Underpinnings of Population Persistence in Isle Royale Moose

Molecular Biology and Evolution

... Here, we show that altering the mating system by modifying the strength of sexual selection has complex genomic consequences. Purging deleterious alleles from a population should help to reduce extinction risk [49] but, in contrast, high sexual conflict or sexual-natural selection trade-offs or increased drift could lead to a significant genetic load reducing population fitness. Sexual selection can alter the distribution of fitness effects from segregating deleterious loci in a way that could have complex consequences for a population in a rapidly changing environment. ...

Deleterious Variation in Natural Populations and Implications for Conservation Genetics
  • Citing Article
  • November 2022

Annual Review of Animal Biosciences

... Likewise, Exposito-Alonso et al. (2022) suggested a very low recovery of genetic variation in most species that are affected by habitat loss. Therefore, assessments and continuous monitoring of genetic diversity patterns in wildlife populations should be conducted to generate well-informed conservation proposals aimed at preventing the ongoing loss of biodiversity (Hoban et al. 2021, Frankham 2022, especially in landscapes currently experiencing high levels of anthropogenic disturbance. ...

Genetic diversity loss in the Anthropocene
  • Citing Article
  • September 2022

Science