Skip to main content
Proceedings of the Royal Society B: Biological Sciences logoLink to Proceedings of the Royal Society B: Biological Sciences
editorial
. 2022 Dec 21;289(1989):20221930. doi: 10.1098/rspb.2022.1930

Taking quantitative genomics into the wild

Susan E Johnston 1,, Nancy Chen 2, Emily B Josephs 3
PMCID: PMC9768650  PMID: 36541172

Abstract

We organized this special issue to highlight new work and review recent advances at the cutting edge of ‘wild quantitative genomics’. In this editorial, we will present some history of wild quantitative genetic and genomic studies, before discussing the main themes in the papers published in this special issue and highlighting the future outlook of this dynamic field.

Keywords: genetics, genomics, evolution, wild populations

1. Introduction

A key goal in studies of ecology and evolution is understanding the causes of phenotypic diversity in nature. Most traits of interest such as those relating to morphology life-history, immunity and behaviour are quantitative, and phenotypic variation is driven by the cumulative effects of genetic and environmental variation [1]. The field of quantitative genetics aims to quantify the additive genetic component of this trait variance (i.e. the heritability), often with the underlying assumption that trait variance is driven by many loci of very tiny (infinitesimal) effects throughout the genome [2,3]. This approach allows us to understand the evolutionary potential of natural populations and can be extended to examine the genetic covariation with fitness to predict responses to selection [4]. Therefore, quantitative genetic studies are fundamental to understanding evolution in the wild [1].

Over the last two decades, there has been a wealth of quantitative genetic studies investigating trait heritabilities and genetic correlations, but these studies were initially limited to long-term studies of pedigreed populations, or common garden experiments in organisms more easily suited to crossing and rearing in a controlled environment. However, the advent of tractable genomic technologies has since allowed quantitative genetic studies to be conducted in a more diverse range of wild systems and has increased the opportunities for addressing outstanding questions in ecology and evolution. In particular, genomic studies can uncover the genetic basis of fitness-related quantitative traits, allowing a better understanding of their evolutionary dynamics.

We organized this special issue to highlight new work and review recent advances at the cutting edge of ‘wild quantitative genomics'. In this editorial, we will present some history of wild quantitative genetic and genomic studies, before discussing the main themes in the papers published in this special issue and highlighting the future outlook of this dynamic field.

2. A short history of quantitative genetics in the wild

(a) . Traditional quantitative genetics

Quantitative genetic models have traditionally estimated the heritability of traits using information on the pairwise relationships between individuals within a population [3]. These models, such as the commonly used ‘animal model’ [5], were originally developed for animal and plant breeding experiments with experimentally determined relatedness and have become powerful tools in predicting responses to artificial selection [2]. From the 1980s onwards, DNA parentage analysis gradually became more tractable in non-model species, providing the opportunity to construct pedigrees and thus quantify pairwise relatedness in previously well-studied populations [68]. These new analyses allowed quantitative genetics to address a range of outstanding questions in wild systems living in natural conditions, including the heritability of life-history traits [9], the contribution of common environment effects to phenotypic variation [10] and the paradox of evolutionary stasis, where traits do not evolve despite apparent selection [11]. However, these traditional models cannot be refined beyond the assumption that traits are controlled by an infinite number of genes of infinitely small effect (known as the infinitesimal model) [12]. In addition, traditional models only consider the expected pedigree relatedness between individuals, whereas the true relatedness between individuals can deviate from this expectation due to the randomness of recombination and Mendelian segregation [13]. More critically, such studies were almost always restricted to established long-term studies of mammals and birds, where multiple generations of individuals were already available for pedigree construction. While these long-term, individual-based studies have been crucial in establishing a solid foundation for what is feasible in wild populations, they have tended to be biased towards smaller populations and organisms that do not move long distances, making them easier to study and sample. Gienapp et al. [4] referred to this as a ‘tool of privilege’, as it remained challenging to establish and fund long-term quantitative genetic studies in new and more diverse study systems.

Alongside studies of pedigreed populations in the wild, studies of plants and other organisms that could be reared in controlled conditions have investigated quantitative genetics using common garden studies [14]. These studies often use crossing designs to generate populations with known relatedness between individuals. Then, these individuals are phenotyped in a common field environment to quantify genetic variation for phenotypes of interest. These powerful approaches have allowed quantitative geneticists to estimate additive genetic variance for fitness and evaluate the potential for adaptation to changing environments [15], measure inbreeding depression [16] and determine the mechanisms of genetic correlations [17], among other questions. However, as with pedigree-based approaches discussed above, common garden studies have some limitations. First, they require a design where specific individuals can be marked so that they are distinguishable from each other. Second, these experiments generally study individuals from emergence to senescence, missing key parts of the life cycle [18,19]. Finally, these studies are often only able to look at one or a few years, limiting their ability to describe selection that may vary across many years [20].

(b) . The genomics era

The rise of high-throughput DNA sequencing and genotyping arrays created an unprecedented opportunity to bring quantitative genetics to a much wider range of taxa and research directions [4,13]. The characterization of individual genomic variation, most often through single-nucleotide polymorphisms (SNPs), has led to two key advances that genomics offers over traditional methods. First, it is now possible to quantify the actual proportion of genomic variation shared between individuals in wild populations (i.e. genomic-pairwise rather than pedigree–pairwise relationships) [2126]. This is a major development in the field and means that quantitative genetic studies could feasibly be carried out in any system with a suitable number of phenotyped individuals, even without pedigrees, provided there are enough genomic markers and related individuals sampled (i.e. that markers are in linkage disequilibrium with causal variants [4,23,24,27]). Second, it is increasingly possible to decompose heritable variation into its underlying genetic architecture—that is, use genetic mapping techniques to discover the number, effect sizes, distribution and interactions of the underlying genes throughout the genome [28,29] (but see [30]), as well as the contribution of epigenetic mechanisms [31] and indirect genetic effects, such as maternal genetic effects [24,32,33].

3. Wild quantitative genomics today

These advances have created opportunities to better understand selection and evolution in wild populations. In particular, they have provided a foundation for detailed dissection of the genomic architecture of additive genetic variation [26,31,34], local adaptation [35,36], inbreeding depression [37,38], indirect genetic effects and multi-genomic architectures [24,39], genotype-by-environment interactions [40] and multivariate genetic architectures and selection [4143], as well as more accurate predictions of evolutionary responses and constraints [4446] and the genetic pathways important to local adaptation and fitness [47]. In this special issue, we present 12 contributed publications that encompass broad themes in cutting-edge wild quantitative genomics.

(a) . Understanding the genetic architecture of quantitative traits

A common goal of quantitative genomic studies is determining the genetic architecture of traits. In this issue, Kelly [46] notes that this allows us to peer into the ‘black box’ of quantitative genetic models and to see the genetic mechanisms shaping trait variation. A first step is to quantify the trait heritability; this measure can indicate the adaptive potential of populations, and heritable variation is necessary to identify causal loci. Duntsch et al. [26] quantify the heritability of morphological traits in the hihi (Notiomytis cincta, also known as the stitchbird), a passerine bird endemic to Aotearoa | New Zealand with two approaches: a traditional pedigree relatedness matrix between individuals, and a genomic relatedness matrix (GRM) quantifying the realized relatedness between individuals based on dense SNP genotype information. The similarity of their findings between pedigree and GRM approaches provides useful evidence that quantitative genomic studies do not require pedigrees to estimate trait heritability, provided there are enough related individuals and SNPs to capture the genetic variation within the population [23].

A second step is determining the genomic regions contributing to heritable variation. Quantitative trait locus (QTL) mapping is an established approach that is still used to great effectiveness in well-phenotyped organisms where large numbers of molecular markers can be generated. Two studies in the issue used genotyping-by-sequencing data to identify QTLs; Lin et al. [35] used an F3 mapping population to map several fecundity QTLs in Boechera stricta (Drummond's rockcress), and Coughlan et al. [36] used an F2 mapping population from monkeyflowers Mimulus guttatus and M. decorus to identify 12 QTLs in six independent genomic regions associated with life-history traits important in local adaptation. The success of QTL mapping in controlled family crosses relies on generating co-inheritance of genetic markers and causal loci in subsequent generations. By contrast, genome-wide association study (GWAS) leverage natural genetic variation and linkage disequilibrium patterns already present in the population to map major-effect loci to a high resolution. In this issue, Tietgen et al. [34] show the ability to map a large-effect locus in a free-living population using GWAS using a dense SNP array, identifying MC1R as a major locus controlling coat colour in Arctic foxes (Vulpes lagopus).

One challenge for genotype–phenotype association studies is that traditional QTL and GWAS approaches can only detect moderate to large-effect loci, limiting our ability to study traits with polygenic architectures (i.e. controlled by many loci of small effects) and leading to a bias towards investigating traits with a simple genetic basis [30,48]. However, this special issue presents several approaches to characterize the nature of polygenic variation. For example, Duntsch et al. [26] did not identify significant loci in a GWAS but were able to quantify the contributions of individual chromosomes to the additive genetic variance using a technique called ‘chromosome partitioning’. They showed that the contribution of a chromosome to additive genetic variance was proportional to its length, indicating a polygenic architecture. Another approach to characterizing polygenic variation and adaptation—reviewed by McGaugh et al. [45]—is genomic prediction, where all SNP marker effects are estimated in the same model with a mixture of effect size distributions, in turn directly modelling how the whole genome affects a given trait [49]. This approach was used in a precursor study to that of Hunter et al. [44] to quantify the heritability and trait architectures of morphological traits in a wild population of Soay sheep (Ovis aries) [50]. We describe in more detail the utility of genomic prediction for studies of evolutionary change below.

A final point on the genetic architecture of traits is addressed in a review by Husby [31], who discusses the potential contribution of epigenetic variation to phenotypic variation in wild populations, including from small RNAs, DNA methylation and histone modifications. Epigenetic mechanisms have been shown to contribute to variation in developmental, morphological and reproductive traits in diverse species [51,52], although there is some suggestion that this contribution may be small and is likely to be in conjunction with genetic mechanisms [53]. Husby presents a number of tractable methods for studying epigenetic variation in wild populations, but also highlights several unanswered questions that could be addressed in future, such as the strength of selection, heritability and relative contribution to phenotypic variance of epigenetic markers, by combining approaches such as GWAS and epigenome-wide association studies (the association of epigenetic marks with phenotype) into quantitative genetic models.

(b) . Linking genotypic variation with local adaptation and fitness

Several papers in this issue tackle the most evolutionarily important of traits, fitness. Fitness is unique among quantitative traits because it is what is ‘seen’ by natural selection [54]. When the genetic architecture of fitness or fitness-related traits is known, we can understand the evolutionary forces maintaining observed variation and/or their potential role in local adaptation. The study by Lin et al. [35] in several populations of Boechera stricta identified multiple QTLs for traits directly related to fecundity, including a major-effect QTL associated with higher and sturdier flowering stalks. Variation at this QTL was associated with water availability across the landscape, and other fecundity QTLs showed high differentiation between genetic groups. These findings, along with significant differences in selection coefficients at different locations, are consistent with local adaptation maintaining variation in fitness.

Determining the genetic architecture of fitness-related traits can also help us understand why phenotypic variation persists. The study mapping coat colour variation in Arctic foxes [34] showed that heterozygous blue arctic foxes have higher fitness than homozygous white counterparts (comprising 90% of the population) and that this difference is likely mediated via an association with prey availability rather than other adaptations to winter, such as thermoregulation and camouflage. These results provide an explanation for the maintenance of variation of coat colour within this species.

(c) . Quantifying and predicting evolutionary change across the genome

Several papers in this issue present novel approaches to investigate selection and evolutionary change using information from all markers throughout the genome. One of the most promising new directions is the use of genomic prediction models [49]. This approach is well-established in animal and plant breeding and uses information from all SNPs in the genome to determine an individual's genomic estimated breeding values (GEBVs) for a trait of interest, without requiring pedigree information. A review by McGaugh et al. [45] describes how genomic prediction approaches open up new research avenues in wild populations, including (i) determining the genetic architecture of traits (see §2(a) above); (ii) estimating GEBVs in unphenotyped individuals and historical samples; (iii) incorporating information on the error around GEBV estimates, overcoming previous criticisms of pedigree-based approaches (see [55]); (iv) choosing which individuals to breed, either in studies of mate choice or for conservation purposes and (v) micro-evolutionary studies investigating changes in GEBVs over time. This last research question is addressed empirically by Hunter et al. [44], who investigate micro-evolutionary change in body weight in Soay sheep over a 35-year period. They show that despite a decrease in adult body weight over this period, there has been an increase in GEBVs at a rate greater than expected due to genetic drift, indicating that cryptic selection for increased body weight has occurred. This can arise when a trait has changed in response to selection, but a change in environment acts in the opposite direction on phenotype, masking changes in the underlying genotypes [56].

Another approach to investigate selection using genomic information is presented by Kelly [46]. His paper advocates the use of selection component analyses (SCA) to estimate selection at specific life cycle stages by relating individual genotypes to fitness components. For example, viability and sexual selection can be measured by comparing allele frequencies in surviving and non-surviving individuals, or reproducing and non-reproducing individuals, respectively. The paper uses simulation approaches to demonstrate the effectiveness of this method in field experiments of Mimulus guttatus and Drosophila melanogaster and provides practical advice on study design, particularly in the use of imprecise genotyping via low-coverage sequencing of large numbers of individuals to improve the power of this method.

Stahlke et al. [47] also use a population genetics approach to detect evolution in natural populations, investigating allele frequency changes in six populations of Tasmanian devils (Sarcophilus harrisii) before and after contracting a unique transmissible cancer known as devil facial tumour disease. Using a RAD-capture approach, they identify 186 candidate genes that are enriched for cell cycling and immune response, indicating the genetic pathways that are important for viability selection after infection. They also use DNA sequence information to compare these contemporary signatures with molecular signatures of selection (i.e. historical selection over millions of years) to investigate if these loci have been the target of recurrent selection in devils; notably, there was limited overlap in regions under selection over these different evolutionary timescales.

(d) . Multivariate quantitative genetics: moving beyond the genotype–phenotype map

Most research in wild quantitative genetics and genomics has focused on individual traits within one species. However, trade-offs and genetic conflict of polygenic variation within and between individuals, sexes, and even species, are important components of life-history theory [57,58]. Genetic correlations between traits can constrain or facilitate selection, and may explain the paradox that evolutionary stasis is common despite evidence of frequent directional selection on heritable traits [59]. The ability of populations to respond to multivariate selection is well demonstrated by the Lande equation Δz = Gβ, where Δz is the change in a vector of multivariate normal traits due to selection, G is the additive variance–covariance matrix (the structure of which can constrain evolution) and β is a vector of directional selection gradients [60,61]. The level of evolutionary constraint is also likely to be highly dependent on underlying genetic architectures [62]. Therefore, the integration of genomic data into multivariate models creates opportunities to investigate how genetic correlations can shape evolution from several different standpoints, as demonstrated by the studies described here.

Several papers in this issue use QTL mapping of multiple traits to investigate whether correlated traits share a genetic basis. Coughlan et al. [36] demonstrated that some mid-to-large effect QTLs associated with correlated life-history traits in Mimulus guttatus and M. decorus mapped to the same genomic regions. These QTLs explain life-history divergence between different parental populations, sometimes with the opposite effect than expected. In particular, delayed rhizome production over development in heterozygotes at a large-effect QTL may have implications for hybrid fitness in nature. Lin et al. [35] also identified overlapping QTL for correlated fitness and fitness-related traits in Boechera stricta from different parent populations and environments. The findings of both studies, particularly where opposing effects are observed, have implications for gene flow, local adaptation and population divergence.

One phenomenon that can maintain genetic variation for fitness-related traits in natural populations is sexual antagonism, where selection favours different alleles within males and females [63]. Yet, the amount and prevalence of sexually antagonistic variation depends on the genetic architecture of dimorphism, which is not well understood [58,64]. Kollar et al. [43] used a multivariate approach to examine the genetic basis of sexual dimorphism in a scent-based fertilization syndrome in the moss Ceratodon purpureus. They disentangled constraints shaping variation in volatile organic compounds emissions, by analysing cross-sex genetic correlations within traits, sex-specific (co)variance between traits (i.e. the G matrix above) and cross-sex, cross-trait (co)variances. Their findings are highly trait dependent but are somewhat consistent with sex-specific architectures that may have evolved to resolve sexual conflict.

Reddiex & Chenoweth [42] also used the G matrix to investigate the maintenance of variation for phenotypic traits. They combined GWAS with multivariate models to investigate constraints on sexual selection on male cuticular hydrocarbons (CHCs) in wild-derived, genome-resequenced lines of Drosophila serrata. They estimated the genetic (co)variance matrix G in conjunction with multivariate SNP effects to detect genomic regions with the strongest multivariate associations. By investigating the (mis)alignment of G and the directional selection gradients β, they present evidence of multivariate genetic constraints on CHC evolution that are likely to be polygenic in nature.

Finally, it is long known that a trait of an individual can be influenced not only by its own genome, but also the genome of interacting individuals. This can arise through indirect genetic effects within the same species (e.g. maternal effects and/or behaviour of other related or unrelated individuals [65]), a phenomenon well-described in evolutionary genetics [66,67]. However, this can also arise through the genetic effects of other species; for example, some phenotypes measured in plants and animals are likely to be influenced by their microbiota and therefore may map to and co-evolve with the genome of an entirely different species [68]. Yet, this phenomenon remains poorly understood. O'Brien et al. [39] used a simulation approach to investigate the genetic architecture and coevolution of a host–microbe mutualism under several evolutionary scenarios. In mutualisms, both species have fitness benefits, but this outcome can be influenced by conflict, i.e. when optimal trait values and/or strengths of selection are different for each species [69]. O'Brien et al. demonstrate that GWAS can map a joint trait to loci in multiple genomes, and they also show how fitness conflict and feedback loops can lead to variation in multi-genomic architectures. They show that fitnesses can also be positively correlated in spite of conflict, and that even when reaching a trait optimum (and often generating a strong mutualistic dependency), genetic variation and the evolutionary potential of a joint trait can be maintained.

4. Future outlook for the field

The wild quantitative genomic studies presented in this special issue demonstrate the promise of genomic technologies to better characterize quantitative genomic variation and to understand a number of outstanding evolutionary questions. Such studies are more accessible than ever before, and outcomes will have a wider impact in the fields of conservation genetics, molecular biology, and animal and plant breeding, among others. Yet, a number of immediate challenges remain, from the perennial issue of study power, to persistent structural barriers faced by researchers from the Global South and other historically excluded groups. Here, we will discuss these promises and challenges in more detail, and consider the direction and legacy of wild quantitative genomics in the years to come.

(a) . Wild quantitative genomic studies are more feasible than ever before

Genomic technologies have made quantitative genetic studies more achievable in a wider range of systems. Pedigrees are no longer an explicit requirement for estimating heritabilities and breeding values in populations where enough genomic variation is captured [4,23,26,42,44,45]. Furthermore, the use of GEBVs overcomes numerous biases that arise when deriving pedigree-based estimates [55], particularly for individuals with fewer pedigree connections where environmental and genetic effects on phenotype are more likely to be confounded [70]. Genomic prediction also has the advantage of allowing the estimation of breeding values for individuals that have not been phenotyped [45,49]. The use of GEBVs is gaining traction in wild evolutionary studies [44,71,72] and will have important applications for investigating responses to selection over time, although there are limitations (see §4(c) below).

Although pedigrees are no longer required to estimate heritabilities and breeding values, long-term longitudinal datasets are still vital for the field as they allow us to investigate temporal trends and microevolution [73]. Pedigrees remain an integral tool for many analyses, including estimation of individual reproductive success [7]; validation of genomic heritability estimates [27]; determining if allele frequency changes are greater than those expected under genetic drift (i.e. simulation of Mendelian sampling, or ‘gene-dropping’, of alleles through the pedigree) [74]; and for managing genetic diversity in threatened populations [75]. Indeed, methods have been developed that use genomic data to reconstruct pedigree relatedness between individuals, even in cases where connecting individuals are missing [76]; this can be conducted using relatively small numbers of molecular markers, which may be more cost-effective than larger scale genomic studies. In addition, long-term datasets allow more fine-scale modelling of important covariates to quantify the effects and account for intrinsic and extrinsic variation within and between individuals, including common environment effects, indirect genetic effects, environment quality, population densities and age [10]. Finally, long-term studies are important for building long-term partnerships with conservation practitioners and indigenous guardians of vulnerable populations [75].

Quantitative genomics is also creating new opportunities to examine genetic architectures and evolution within multivariate frameworks. It is unlikely that quantitative traits evolve independently, but are rather constrained and/or coevolve with correlated traits. Identifying the genetic architecture of correlated, polygenic traits may help to elucidate the role of pleiotropy (i.e. genetic architecture shared between traits) and/or patterns of linkage disequilibrium between causal loci in driving trait correlations [7779]. In addition, understanding the genetic architecture of cross-sex correlations and sex-by-locus interactions may explain the evolution of sexual dimorphism and the prevalence of sexual conflict in maintaining genetic variation and/or preventing phenotypes from reaching their sex-specific optima [42,43,63]. There is also more scope for investigating the genetics of interacting individuals and species [39], as well as potential interactions at the genotypic level with environmental heterogeneity [35,36].

(b) . The importance of polygenic variation is becoming clearer

Traditional quantitative genetics relies on the assumption of the infinitesimal model. However, with the advent of QTL mapping and GWAS, the focus shifted away from quantifying this polygenic component and instead investigating effects at loci of large effect [30,80]. These ‘low-hanging fruit’ were easier to detect as they often explain a large proportion of trait variance, with empirical examples often shown to be maintained through stabilizing selection [8184], fluctuating selection [85] and/or local adaptation [86]. However, these observations may be the exception, rather than the rule [87]. Responses to selection on traits are often consistent with a polygenic architecture (i.e. the infinitesimal model), as responses to artificial directional selection are repeatedly shown to be steady over many generations [87,88]. The prevalence of polygenic architectures is also supported by GWAS results in model systems with very large sample sizes, where even if some of the genetic variance can be explained by candidate genes in core pathways, the majority of the genetic variance is explained by loci of small effect spread across the genome [89].

Fortunately, advances in quantitative genomics have led to better frameworks for determining the genetic architecture of traits, particularly in the absence of large effect loci. In previous QTL and GWAS studies, it was often not possible to distinguish if a lack of detectable loci was due to a trait being polygenic or due to a lack of power [29]. Now, models using genome partitioning [26] or genomic prediction [44] provide direct support for underlying polygenic architectures of many traits of interest, suggesting that the infinitesimal model may continue to be useful in many situations. Nevertheless, QTL and GWAS studies remain an essential tool in quantitative genomic studies. Major-effect loci have been repeatedly uncovered for a range of quantitative traits, as demonstrated in this issue [3436] and elsewhere [29], giving insight into underlying genetic mechanisms and their evolutionary dynamics [90]. In addition, GWAS summary statistics can be used to determine the proportion of loci that have non-zero effects on phenotypes, giving insight into the distribution of underlying effect sizes (and potentially the polygenicity) of traits [79,91]. However, studies investigating polygenic architectures are still subject to some limitations and issues with power, as outlined in §4(c) below.

This special issue has also highlighted the utility of common population genetic approaches to characterize both simple and polygenic genomic signatures of selection in natural populations. Quantitative genetic studies are often focused on specific (fitness-related) phenotypes, yet population genetic approaches can overcome the constraint of phenotype by focusing on variation in allele frequencies between different groups of individuals. This is demonstrated in this special issue by the use of SCA by Kelly [46]. Such approaches can test for selection at different life stages where this information is available [92], providing a powerful framework for predicting allele frequency changes over time [93] and assessing the role of sexual conflict [94] or life-history trade-offs in maintaining genetic variation [95]. Overall, both quantitative and population genomic approaches applied to individual-level genomic data can characterize simple and polygenic architectures of fitness and adaptation, to better understand and validate the underlying genetic mechanisms and pathways at play.

(c) . Wild quantitative genomic studies still face challenges

A recurrent and familiar issue is that wild quantitative genomic studies are often underpowered, particularly when they aim to determine the genetic architecture of traits [29]. The number of individuals that can be sampled, phenotyped and genotyped are often limited (from 10 s to 1000 s), which can lead to overestimation of effect sizes and/or false-positive associations in QTL and GWA studies, a phenomenon known as the ‘Beavis effect’ [96,97]. Another issue is that closely related individuals may be more likely to share environments, which may upwardly bias heritability estimates if common environment effects are not or cannot be accounted for [10]. Furthermore, obtaining reliable genotypes with suitable marker density can itself be a challenge, especially in species without reference genomes or those with large genomes, or in cases where tissue samples cannot be easily prepared and preserved in situ. Estimation of trait heritabilities and breeding values using genomic approaches rely on markers being in linkage disequilibrium with causal variants, and so low marker densities could lead to underestimation of the genetic contribution to phenotype [24]. Reduced representation sequencing approaches have been popular for generating markers in less-tractable systems [98,99], and newer approaches involving imputation along with low-coverage short-read sequencing have potential to generate higher numbers of genotypes in non-model systems [100,101].

One route to understanding the effects of sample sizes and marker density on quantitative genomic analyses are simulation approaches that estimate and/or incorporate population demographic histories and markers densities [102], as well as replication and/or subsampling of data [103]. McGaugh et al. [45] in this issue also use simulation approaches to highlight the issue of power to accurately estimate GEBVs in outbred populations, demonstrating the requirement for appropriately sized training datasets, high marker densities, moderate to high heritabilities and high concordance between the modelled distribution of effect sizes and the true genetic architecture of focal traits. As a result, researchers should recognize the limitations of examining the microevolution of polygenic traits in a genomic prediction framework [45].

(d) . Quantitative genomics will be an important tool in conservation

Advancements in the field of quantitative genomics can have important implications for conservation [104,105]. To date, most conservation genetics studies and management recommendations are based on the idea that maximizing levels of genetic diversity is important for maintaining population viability in the face of changing environments [106]. While the importance of neutral genetic diversity in conservation has been debated [107,108], linking genomic variation to trait variation and adaptive potential will be useful for conservation goals. In turn, understanding the genetic basis of fitness-related traits and estimating adaptive potential in such populations can improve the population genetic theories underlying conservation genetic management and to inform conservation efforts in the future.

Studies in this special issue provide important lessons in this context. Duntsch et al. [26] discuss how understanding the genetic architecture of ecologically relevant traits in the hihi enables better predictions of adaptive potential and response to selection. They caution that the adaptive potential of low heritability traits can be further constrained if those traits are polygenic, and how adaptive variation may be lost to drift faster than mutation can replenish it in populations with small effective population sizes. Stahlke et al. [47] use a complementary approach to assess the genomic response to selection across different timescales, identifying potential loci that could be useful in future monitoring efforts for adaptation to DFT disease in Tasmanian devils. McGaugh et al. [45] also note that genomic prediction methods could inform captive breeding strategies to select individuals e.g. for resistance to disease and (theoretically) for accelerating responses to climate change. While the potential of quantitative genomics to increase our ability to predict population trajectories and better inform conservation strategies is improving, we acknowledge that on-the-ground habitat protection and management is still of paramount importance in the protection of declining species.

(e) . Barriers to increasing diversity of researchers and research systems persist

Earlier, we mentioned that quantitative genetics can sometimes be a ‘tool of privilege’. There is a large potential for this field to reach more diverse species and research questions, but there are still clear structural barriers to accessing genomics technologies and for inclusion of researchers from historically excluded groups and the Global South [109]. The latter is a pervasive problem in ecology and evolution [110114]. If both barriers are unaddressed, we will miss critical insights from species in the most biodiverse and vulnerable habitats and, more importantly, novel research directions, approaches and perspectives from researchers from diverse backgrounds [115]. As a field, it is imperative that we collectively dismantle these structural barriers through actions such as fixing disparities in access to funding [116], publishing [117,118] and networking opportunities [119]; critically examining our tendency to associate with similar people and instead fostering more inclusive recruitment, authorship and collaboration practices [111]; and reducing helicopter science by building meaningful relationships with indigenous guardians and local communities to ensure equitable cogeneration of knowledge and sharing of benefits [110].

We also wish to note that this special issue was compiled during the first years of the COVID-19 pandemic. While this was a difficult period for the life and work of many, it is now well acknowledged that the pandemic has exacerbated systemic inequalities related to race and gender in science [120], and is therefore likely to have had a similar impact within the wild quantitative genomics field.

5. Conclusion

The field of wild quantitative genomics has a rich history of adapting classic approaches for investigating genetic variation of fitness-related traits, while dealing with individual and environmental heterogeneity and challenges of statistical power. Genomic technologies have widened the questions and opportunities to better understand the variation we see in the world around us. The lessons we learn in wild populations inform our basic understanding of the drivers and evolutionary dynamics of quantitative variation in any population. We hope that this special issue shows the continued promise of these approaches for better understanding the natural world, as well as providing a solid foundation of knowledge that can inform applied research in conservation, animal and plant breeding, and medical and human genetics.

Acknowledgements

We thank Shalene Singh-Shepherd for her patience and understanding on compiling this issue during the COVID-19 pandemic and periods of family leave by the authors. We thank Gary Carvalho, who acted as Senior Editor for all of our papers. We thank Anna Santure, Loeske Kruuk and two anonymous reviewers who made insightful suggestions on this editorial piece. Finally, we thank all of the authors and reviewers who contributed to this special issue, particularly given the personal and professional challenges of the pandemic.

Data accessibility

This article has no additional data.

Authors' contributions

All authors wrote and edited the manuscript, and approved the final version.

All authors gave final approval for publication and agreed to be held accountable for the work performed therein.

Conflict of interest declaration

We declare we have no competing interests.

Funding

This study was funded by Royal Society University Research Fellowship (grant no. UF150448) to S.E.J. US National Institutes of Health (grant no. 1R35GM133412) to N.C. US National Institutes of Health (grant no. 1R35GM142829) to E.B.J.

Glossary

adaptive potential

the ability of a population to respond to selection via adaptation, typically measured as the additive genetic variance for fitness

epigenetics

changes in the genome, such as DNA methylation, that can have phenotypic effects but do not involve changes in nucleotide sequences

fitness

the contribution of an individual to the next generation or reproductive pool. Fitness is often estimated using fitness-related traits or components, such as survival, fecundity or growth rate

genetic architecture

the number, effect sizes, frequencies and/or interactions of genes that underlie a trait. Genetic architecture can be described as monogenic or Mendelian if variation at one gene shapes trait variation, and polygenic if variation at many genes shapes trait variation

genetic correlation

the proportion of genetic variance that is shared between traits. These are estimated in multivariate models, which simultaneously analyses two or more phenotypes. Genetic correlations can be caused by linkage disequilibrium between QTLs for two traits, or pleiotropy where the same QTLs affect multiple traits

genomic prediction

a method using genome-wide molecular SNP markers to predict genomic estimated breeding values (GEBVs) for quantitative traits within individuals. It can also be used to estimate the effect sizes of individual SNP markers on phenotypes

genomic relatedness matrix (GRM)

a covariance matrix calculated based on the similarity of SNP genotypes between individuals. This can be used to calculate the narrow-sense heritability or to account for phenotypic variation shaped by background genetics and shared environment in a GWAS

genome-wide association study (GWAS)

modelling the association between genome-wide SNP loci and a phenotype, used to identify regions of the genome associated with trait variation

heritability

the proportion of trait variance that is contributed by genetic variation. The ‘narrow-sense’ heritability is trait variance that is attributable to additive effects of genetic variants (additive genetic variance)

inbreeding depression

the decrease in fitness associated with increasing homozygosity in the genome, most often due to matings between closely related individuals

indirect genetic effects

the variance of a trait that is contributed by additive genetic effects in other (conspecific) individuals, e.g. maternal genetic effects

life-history trait

a trait that is related to the pattern of survival and reproduction events over an organism's lifespan

linkage disequilibrium

the non-random association of alleles at a pair of loci

quantitative genetics

the study of the genetic basis of continuous/complex/quantitative traits

quantitative trait locus (QTL)

a locus associated with variation in a quantitative trait. Can be identified through QTL mapping or GWAS. QTLs may be: the causal variant that directly contributes to trait variation; a region containing that variant; or neutral variation that is in linkage disequilibrium with a causal variant

References

  • 1.Kruuk LEB. 2004. Estimating genetic parameters in natural populations using the ‘animal model’. Phil. Trans. R. Soc. Lond. B 359, 873-890. ( 10.1098/rstb.2003.1437) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 2.Falconer DS, Mackay TFC. 1996. Introduction to quantitative genetics. Essex, UK: Longman. [Google Scholar]
  • 3.Lynch M, Walsh B. 1998. Genetics and analysis of quantitative traits. Sunderland, MA: Sinauer Associates. [Google Scholar]
  • 4.Gienapp P, Fior S, Guillaume F, Lasky JR, Sork VL, Csilléry K. 2017. Genomic quantitative genetics to study evolution in the wild. Trends Ecol. Evol. 32, 897-908. ( 10.1016/j.tree.2017.09.004) [DOI] [PubMed] [Google Scholar]
  • 5.Henderson CR. 1975. Best linear unbiased estimation and prediction under a selection model. Biometrics 31, 423-447. ( 10.2307/2529430) [DOI] [PubMed] [Google Scholar]
  • 6.Jeffreys AJ, Wilson V, Thein SL. 1985. Hypervariable ‘minisatellite’ regions in human DNA. Nature 314, 67-73. ( 10.1038/314067a0) [DOI] [PubMed] [Google Scholar]
  • 7.Pemberton JM. 2008. Wild pedigrees: the way forward. Proc. R. Soc. B 275, 613-621. ( 10.1098/rspb.2007.1531) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 8.Jones AG, Small CM, Paczolt KA, Ratterman NL. 2010. A practical guide to methods of parentage analysis. Mol. Ecol. Resour. 10, 6-30. ( 10.1111/j.1755-0998.2009.02778.x) [DOI] [PubMed] [Google Scholar]
  • 9.Teplitsky C, Mills JA, Yarrall JW, Merilä J. 2009. Heritability of fitness components in a wild bird population. Evolution 63, 716-726. ( 10.1111/j.1558-5646.2008.00581.x) [DOI] [PubMed] [Google Scholar]
  • 10.Kruuk LE, Merilä J, Sheldon BC. 2001. Phenotypic selection on a heritable size trait revisited. Am. Nat. 158, 557-571. ( 10.1086/323585) [DOI] [PubMed] [Google Scholar]
  • 11.Kruuk EB, Slate J, Pemberton JM, Brotherstone S, Guinness F, Clutton-Brock T. 2002. Antler size in red deer: heritability and selection but no evolution. Evolution 56, 1683-1695. ( 10.1111/j.0014-3820.2002.tb01480.x) [DOI] [PubMed] [Google Scholar]
  • 12.Fisher RA. 1919. XV.—The correlation between relatives on the supposition of Mendelian inheritance. Earth Environ. Sci. Trans. R. Soc. Edinb. 52, 399-433. ( 10.1017/S0080456800012163) [DOI] [Google Scholar]
  • 13.Jensen H, Szulkin M, Slate J. 2014. Molecular quantitative genetics. In Quantitative genetics in the wild (eds Charmantier A, Garant D, Kruuk LEB), pp. 209-227. Oxford, UK: Oxford University Press. [Google Scholar]
  • 14.Wadgymar SM, DeMarche ML, Josephs EB, Sheth SN, Anderson JT. 2022. Local adaptation: causal agents of selection and adaptive trait divergence. Annu. Rev. Ecol. Evol. Syst. 53, 87-111. ( 10.1146/annurev-ecolsys-012722-035231) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 15.Kulbaba MW, Sheth SN, Pain RE, Eckhart VM, Shaw RG. 2019. Additive genetic variance for lifetime fitness and the capacity for adaptation in an annual plant. Evolution 73, 1746-1758. ( 10.1111/evo.13830) [DOI] [PubMed] [Google Scholar]
  • 16.Fenster CB, Galloway LF. 2000. Inbreeding and outbreeding depression in natural populations of Chamaecrista fasciculata (Fabaceae). Conserv. Biol. 14, 1406-1412. ( 10.1046/j.1523-1739.2000.99234.x) [DOI] [Google Scholar]
  • 17.Conner JK. 2002. Genetic mechanisms of floral trait correlations in a natural population. Nature 420, 407-410. ( 10.1038/nature01105) [DOI] [PubMed] [Google Scholar]
  • 18.Bennington CC, McGraw JB. 1995. Phenotypic selection in an artificial population of Impatiens pallida: the importance of the invisible fraction. Evolution 49, 317-324. ( 10.1111/j.1558-5646.1995.tb02244.x) [DOI] [PubMed] [Google Scholar]
  • 19.Weis AE. 2018. Detecting the ‘invisible fraction’ bias in resurrection experiments. Evol. Appl. 11, 88-95. ( 10.1111/eva.12533) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 20.Wadgymar SM, Daws SC, Anderson JT. 2017. Integrating viability and fecundity selection to illuminate the adaptive nature of genetic clines. Evol. Lett. 1, 26-39. ( 10.1002/evl3.3) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 21.Yang J, et al. 2010. Common SNPs explain a large proportion of the heritability for human height. Nat. Genet. 42, 565-569. ( 10.1038/ng.608) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 22.Hill WG, Weir BS. 2011. Variation in actual relationship as a consequence of Mendelian sampling and linkage. Genet. Res. 93, 47-64. ( 10.1017/S0016672310000480) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 23.Vinkhuyzen AAE, Wray NR, Yang J, Goddard ME, Visscher PM. 2013. Estimation and partition of heritability in human populations using whole-genome analysis methods. Annu. Rev. Genet. 47, 75-95. ( 10.1146/annurev-genet-111212-133258) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 24.Bérénos C, Ellis PA, Pilkington JG, Pemberton JM. 2014. Estimating quantitative genetic parameters in wild populations: a comparison of pedigree and genomic approaches. Mol. Ecol. 23, 3434-3451. ( 10.1111/mec.12827) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 25.Santure AW, et al. 2015. Replicated analysis of the genetic architecture of quantitative traits in two wild great tit populations. Mol. Ecol. 24, 6148-6162. ( 10.1111/mec.13452) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 26.Duntsch L, Tomotani BM, de Villemereuil P, Brekke P, Lee KD, Ewen JG, Santure AW. 2020. Polygenic basis for adaptive morphological variation in a threatened Aotearoa | New Zealand bird, the hihi (Notiomystis cincta). Proc. R. Soc. B 287, 20200948. ( 10.1098/rspb.2020.0948) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 27.Perrier C, Delahaie B, Charmantier A. 2018. Heritability estimates from genomewide relatedness matrices in wild populations: application to a passerine, using a small sample size. Mol. Ecol. Resour. 18, 838-853. ( 10.1111/1755-0998.12886) [DOI] [PubMed] [Google Scholar]
  • 28.Savolainen O, Lascoux M, Merilä J. 2013. Ecological genomics of local adaptation. Nat. Rev. Genet. 14, 807-820. ( 10.1038/nrg3522) [DOI] [PubMed] [Google Scholar]
  • 29.Santure AW, Garant D. 2018. Wild GWAS—association mapping in natural populations. Mol. Ecol. Resour. 18, 729-738. ( 10.1111/1755-0998.12901) [DOI] [PubMed] [Google Scholar]
  • 30.Rockman MV. 2012. The QTN program and the alleles that matter for evolution: all that's gold does not glitter. Evolution 66, 1-17. ( 10.1111/j.1558-5646.2011.01486.x) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 31.Husby A. 2022. Wild epigenetics: insights from epigenetic studies on natural populations. Proc. R. Soc. B 289, 20211633. ( 10.1098/rspb.2021.1633) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 32.Kong A, et al. 2018. The nature of nurture: effects of parental genotypes. Science 359, 424-428. ( 10.1126/science.aan6877) [DOI] [PubMed] [Google Scholar]
  • 33.Wu Y, Zhong X, Lin Y, Zhao Z, Chen J, Zheng B, Li JJ, Fletcher JM, Lu Q. 2021. Estimating genetic nurture with summary statistics of multigenerational genome-wide association studies. Proc. Natl Acad. Sci. USA 118, e2023184118. ( 10.1073/pnas.2023184118) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 34.Tietgen L, et al. 2021. Fur colour in the Arctic fox: genetic architecture and consequences for fitness. Proc. R. Soc. B 288, 20211452. ( 10.1098/rspb.2021.1452) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 35.Lin YP, Mitchell-Olds T, Lee CR. 2021. The ecological, genetic and genomic architecture of local adaptation and population differentiation in Boechera stricta. Proc. R. Soc. B 288, 20202472. ( 10.1098/rspb.2020.2472) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 36.Coughlan JM, Brown MW, Willis JH. 2021. The genetic architecture and evolution of life-history divergence among perennials in the Mimulus guttatus species complex. Proc. R. Soc. B 288, 20210077. ( 10.1098/rspb.2021.0077) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 37.Kardos M, et al. 2018. Genomic consequences of intensive inbreeding in an isolated wolf population. Nat. Ecol. Evol. 2, 124-131. ( 10.1038/s41559-017-0375-4) [DOI] [PubMed] [Google Scholar]
  • 38.Stoffel MA, Johnston SE, Pilkington JG, Pemberton JM. 2021. Genetic architecture and lifetime dynamics of inbreeding depression in a wild mammal. Nat. Commun. 12, 2972. ( 10.1038/s41467-021-23222-9) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 39.O'Brien AM, Jack CN, Friesen ML, Frederickson ME. 2021. Whose trait is it anyways? Coevolution of joint phenotypes and genetic architecture in mutualisms. Proc. R. Soc. B 288, 20202483. ( 10.1098/rspb.2020.2483) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 40.Fournier-Level A, Taylor MA, Paril JF, Martínez-Berdeja A, Stitzer MC, Cooper MD, Roe JL, Wilczek AM, Schmitt J. 2022. Adaptive significance of flowering time variation across natural seasonal environments in Arabidopsis thaliana. New Phytol. 234, 719-734. ( 10.1111/nph.17999) [DOI] [PubMed] [Google Scholar]
  • 41.Pitchers W, Nye J, Márquez EJ, Kowalski A, Dworkin I, Houle D. 2019. A multivariate genome-wide association study of wing shape in Drosophila melanogaster. Genetics 211, 1429-1447. ( 10.1534/genetics.118.301342) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 42.Reddiex AJ, Chenoweth SF. 2021. Integrating genomics and multivariate evolutionary quantitative genetics: a case study of constraints on sexual selection in Drosophila serrata. Proc. R. Soc. B 288, 20211785. ( 10.1098/rspb.2021.1785) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 43.Kollar LM, et al. 2021. The genetic architecture of sexual dimorphism in the moss Ceratodon purpureus. Proc. R. Soc. B 288, 20202908. ( 10.1098/rspb.2020.2908) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 44.Hunter DC, Ashraf B, Bérénos C, Ellis PA, Johnston SE, Wilson AJ, Pilkington JG, Pemberton JM, Slate J. 2022. Using genomic prediction to detect microevolutionary change of a quantitative trait. Proc. R. Soc. B 289, 20220330. ( 10.1098/rspb.2022.0330) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 45.McGaugh SE, Lorenz AJ, Flagel LE. 2021. The utility of genomic prediction models in evolutionary genetics. Proc. R. Soc. B 288, 20210693. ( 10.1098/rspb.2021.0693) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 46.Kelly JK. 2021. The promise and deceit of genomic selection component analyses. Proc. R. Soc. B 288, 20211812. ( 10.1098/rspb.2021.1812) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 47.Stahlke AR, et al. 2021. Contemporary and historical selection in Tasmanian devils (Sarcophilus harrisii) support novel, polygenic response to transmissible cancer. Proc. R. Soc. B 288, 20210577. ( 10.1098/rspb.2021.0577) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 48.Le Corre V, Kremer A. 2012. The genetic differentiation at quantitative trait loci under local adaptation. Mol. Ecol. 21, 1548-1566. ( 10.1111/j.1365-294X.2012.05479.x) [DOI] [PubMed] [Google Scholar]
  • 49.Meuwissen TH, Hayes BJ, Goddard ME. 2001. Prediction of total genetic value using genome-wide dense marker maps. Genetics 157, 1819-1829. ( 10.1093/genetics/157.4.1819) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 50.Ashraf B, Hunter DC, Bérénos C, Ellis PA, Johnston SE, Pilkington JG, Pemberton JM, Slate J. 2021. Genomic prediction in the wild: a case study in Soay sheep. Mol. Ecol. ( 10.1111/mec.16262) [DOI] [PubMed] [Google Scholar]
  • 51.Viitaniemi HM, Verhagen I, Visser ME, Honkela A, van Oers K, Husby A. 2019. Seasonal variation in genome-wide DNA methylation patterns and the onset of seasonal timing of reproduction in great tits. Genome Biol. Evol. 11, 970-983. ( 10.1093/gbe/evz044) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 52.Gore AV, Tomins KA, Iben J, Ma L, Castranova D, Davis AE, Parkhurst A, Jeffery WR, Weinstein BM. 2018. An epigenetic mechanism for cavefish eye degeneration. Nat. Ecol. Evol. 2, 1155-1160. ( 10.1038/s41559-018-0569-4) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 53.Charlesworth D, Barton NH, Charlesworth B. 2017. The sources of adaptive variation. Proc. R. Soc. B 284, 20162864. ( 10.1098/rspb.2016.2864) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 54.Orr HA. 2009. Fitness and its role in evolutionary genetics. Nat. Rev. Genet. 10, 531-539. ( 10.1038/nrg2603) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 55.Hadfield JD, Wilson AJ, Garant D, Sheldon BC, Kruuk LEB. 2010. The misuse of BLUP in ecology and evolution. Am. Nat. 175, 116-125. ( 10.1086/648604) [DOI] [PubMed] [Google Scholar]
  • 56.Merilä J, Kruuk LE, Sheldon BC. 2001. Cryptic evolution in a wild bird population. Nature 412, 76-79. ( 10.1038/35083580) [DOI] [PubMed] [Google Scholar]
  • 57.Lande R. 1980. Sexual dimorphism, sexual selection, and adaptation in polygenic characters. Evolution 34, 292-305. ( 10.1111/j.1558-5646.1980.tb04817.x) [DOI] [PubMed] [Google Scholar]
  • 58.Walsh B, Blows MW. 2009. Abundant genetic variation + strong selection = multivariate genetic constraints: a geometric view of adaptation. Ann. Rev. Ecol. Evol. Syst. 40, 41-59. ( 10.1146/annurev.ecolsys.110308.120232) [DOI] [Google Scholar]
  • 59.Merilä J, Sheldon BC, Kruuk LE. 2001. Explaining stasis: microevolutionary studies in natural populations. Genetica 112–113, 199-222. ( 10.1023/A:1013391806317) [DOI] [PubMed] [Google Scholar]
  • 60.Lande R. 1979. Quantitative genetic analysis of multivariate evolution, applied to brain:body size allometry. Evolution 33, 402-416. ( 10.1111/j.1558-5646.1979.tb04678.x) [DOI] [PubMed] [Google Scholar]
  • 61.Lande R, Arnold SJ. 1983. The measurement of selection on correlated characters. Evolution 37, 1210-1226. ( 10.1111/j.1558-5646.1983.tb00236.x) [DOI] [PubMed] [Google Scholar]
  • 62.Friedman J, Twyford AD, Willis JH, Blackman BK. 2015. The extent and genetic basis of phenotypic divergence in life history traits in Mimulus guttatus. Mol. Ecol. 24, 111-122. ( 10.1111/mec.13004) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 63.Rowe L, Chenoweth SF, Agrawal AF. 2018. The genomics of sexual conflict. Am. Nat. 192, 274-286. ( 10.1086/698198) [DOI] [PubMed] [Google Scholar]
  • 64.Cheng C, Houle D. 2020. Predicting multivariate responses of sexual dimorphism to direct and indirect selection. Am. Nat. 196, 391-405. ( 10.1086/710353) [DOI] [PubMed] [Google Scholar]
  • 65.Wolf JB, Brodie ED III, Cheverud JM, Moore AJ, Wade MJ. 1998. Evolutionary consequences of indirect genetic effects. Trends Ecol. Evol. 13, 64-69. ( 10.1016/S0169-5347(97)01233-0) [DOI] [PubMed] [Google Scholar]
  • 66.Mousseau TA, Fox CW. 1998. The adaptive significance of maternal effects. Trends Ecol. Evol. 13, 403-407. ( 10.1016/S0169-5347(98)01472-4) [DOI] [PubMed] [Google Scholar]
  • 67.Wolf JB, Wade MJ. 2016. Evolutionary genetics of maternal effects. Evolution 70, 827-839. ( 10.1111/evo.12905) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 68.Papkou A, et al. 2019. The genomic basis of Red Queen dynamics during rapid reciprocal host–pathogen coevolution. Proc. Natl Acad. Sci. USA 116, 923-928. ( 10.1073/pnas.1810402116) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 69.Bronstein JL. 1994. Conditional outcomes in mutualistic interactions. Trends Ecol. Evol. 9, 214-217. ( 10.1016/0169-5347(94)90246-1) [DOI] [PubMed] [Google Scholar]
  • 70.Postma E. 2006. Implications of the difference between true and predicted breeding values for the study of natural selection and micro-evolution. J. Evol. Biol. 19, 309-320. ( 10.1111/j.1420-9101.2005.01007.x) [DOI] [PubMed] [Google Scholar]
  • 71.Gienapp P, Calus MPL, Laine VN, Visser ME. 2019. Genomic selection on breeding time in a wild bird population. Evol. Lett. 3, 142-151. ( 10.1002/evl3.103) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 72.Bosse M, et al. 2017. Recent natural selection causes adaptive evolution of an avian polygenic trait. Science 358, 365-368. ( 10.1126/science.aal3298) [DOI] [PubMed] [Google Scholar]
  • 73.Sheldon BC, Kruuk LEB, Alberts SC. 2022. The expanding value of long-term studies of individuals in the wild. Nat. Ecol. Evol 6, 1799-1801. ( 10.1038/s41559-022-01940-7) [DOI] [PubMed] [Google Scholar]
  • 74.Chen N, Juric I, Cosgrove EJ, Bowman R, Fitzpatrick JW, Schoech SJ, Clark AG, Coop G. 2019. Allele frequency dynamics in a pedigreed natural population. Proc. Natl Acad. Sci. USA 116, 2158-2164. ( 10.1073/pnas.1813852116) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 75.Galla SJ, et al. 2022. The relevance of pedigrees in the conservation genomics era. Mol. Ecol. 31, 41-54. ( 10.1111/mec.16192) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 76.Huisman J. 2017. Pedigree reconstruction from SNP data: parentage assignment, sibship clustering and beyond. Mol. Ecol. Resour. 17, 1009-1024. ( 10.1111/1755-0998.12665) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 77.Lande R. 1980. The genetic covariance between characters maintained by pleiotropic mutations. Genetics 94, 203-215. ( 10.1093/genetics/94.1.203) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 78.Ruzicka F, Hill MS, Pennell TM, Flis I, Ingleby FC, Mott R, Fowler K, Morrow EH, Reuter M. 2019. Genome-wide sexually antagonistic variants reveal long-standing constraints on sexual dimorphism in fruit flies. PLoS Biol. 17, e3000244. ( 10.1371/journal.pbio.3000244) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 79.Peters L, Huisman J, Kruuk LEB, Pemberton JM, Johnston SE. 2022. Genomic analysis reveals a polygenic architecture of antler morphology in wild red deer (Cervus elaphus). Mol. Ecol. 31, 1281-1298. ( 10.1111/mec.16314) [DOI] [PubMed] [Google Scholar]
  • 80.Slate J, Santure AW, Feulner PGD, Brown EA, Ball AD, Johnston SE, Gratten J. 2010. Genome mapping in intensively studied wild vertebrate populations. Trends Genet. 26, 275-284. ( 10.1016/j.tig.2010.03.005) [DOI] [PubMed] [Google Scholar]
  • 81.Johnston SE, Gratten J, Berenos C, Pilkington JG, Clutton-Brock TH, Pemberton JM, Slate J. 2013. Life history trade-offs at a single locus maintain sexually selected genetic variation. Nature 502, 93-95. ( 10.1038/nature12489) [DOI] [PubMed] [Google Scholar]
  • 82.Barson NJ, et al. 2015. Sex-dependent dominance at a single locus maintains variation in age at maturity in salmon. Nature 528, 405-408. ( 10.1038/nature16062) [DOI] [PubMed] [Google Scholar]
  • 83.Küpper C, et al. 2016. A supergene determines highly divergent male reproductive morphs in the ruff. Nat. Genet. 48, 79-83. ( 10.1038/ng.3443) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 84.Kratochwil CF, Kautt AF, Nater A, Härer A, Liang Y, Henning F, Meyer A. 2022. An intronic transposon insertion associates with a trans-species color polymorphism in Midas cichlid fishes. Nat. Commun. 13, 296. ( 10.1038/s41467-021-27685-8) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 85.Fournier-Level A, Korte A, Cooper MD, Nordborg M, Schmitt J, Wilczek AM. 2011. A map of local adaptation in Arabidopsis thaliana. Science 334, 86-89. ( 10.1126/science.1209271) [DOI] [PubMed] [Google Scholar]
  • 86.Troth A, Puzey JR, Kim RS, Willis JH, Kelly JK. 2018. Selective trade-offs maintain alleles underpinning complex trait variation in plants. Science 361, 475-478. ( 10.1126/science.aat5760) [DOI] [PubMed] [Google Scholar]
  • 87.Barton NH. 2022. The ‘New Synthesis’. Proc. Natl Acad. Sci. USA 119, e2122147119. ( 10.1073/pnas.2122147119) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 88.Sella G, Barton NH. 2019. Thinking about the evolution of complex traits in the era of genome-wide association studies. Annu. Rev. Genomics Hum. Genet. 20, 461-493. ( 10.1146/annurev-genom-083115-022316) [DOI] [PubMed] [Google Scholar]
  • 89.Boyle EA, Li YI, Pritchard JK. 2017. An expanded view of complex traits: from polygenic to omnigenic. Cell 169, 1177-1186. ( 10.1016/j.cell.2017.05.038) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 90.Josephs EB, Stinchcombe JR, Wright SI. 2017. What can genome-wide association studies tell us about the evolutionary forces maintaining genetic variation for quantitative traits? New Phytol. 214, 21-33. ( 10.1111/nph.14410) [DOI] [PubMed] [Google Scholar]
  • 91.Sinnott-Armstrong N, Naqvi S, Rivas M, Pritchard JK. 2021. GWAS of three molecular traits highlights core genes and pathways alongside a highly polygenic background. Elife 10, e58615. ( 10.7554/eLife.58615) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 92.Christiansen FB, Frydenberg O. 1973. Selection component analysis of natural polymorphisms using population samples including mother–offspring combinations. Theor. Popul. Biol. 4, 425-445. ( 10.1016/0040-5809(73)90019-1) [DOI] [PubMed] [Google Scholar]
  • 93.Monnahan PJ, Colicchio J, Fishman L, Macdonald SJ, Kelly JK. 2021. Predicting evolutionary change at the DNA level in a natural Mimulus population. PLoS Genet. 17, e1008945. ( 10.1371/journal.pgen.1008945) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 94.Delph LF, Brown KE, Ríos LD, Kelly JK. 2022. Sex-specific natural selection on SNPs in Silene latifolia. Evol. Lett. 6, 308-318. ( 10.1002/evl3.283) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 95.Anderson JT, Lee CR, Mitchell-Olds T. 2014. Strong selection genome-wide enhances fitness trade-offs across environments and episodes of selection. Evolution 68, 16-31. ( 10.1111/evo.12259) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 96.Beavis WD. 1994. The power and deceit of QTL experiments: lessons from comparative QTL studies. In Proceedings of the Forty-ninth Annual Corn and Sorghum Industry Research Conference, pp. 250-266. Washington, DC: American Seed Trade Association. [Google Scholar]
  • 97.Slate J. 2013. From Beavis to beak color: a simulation study to examine how much QTL mapping can reveal about the genetic architecture of quantitative traits. Evolution 67, 1251-1262. [DOI] [PubMed] [Google Scholar]
  • 98.Cariou M, Duret L, Charlat S. 2016. How and how much does RAD-seq bias genetic diversity estimates? BMC Evol. Biol. 16, 240. ( 10.1186/s12862-016-0791-0) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 99.Lowry DB, Hoban S, Kelley JL, Lotterhos KE, Reed LK, Antolin MF, Storfer A. 2017. Breaking RAD: an evaluation of the utility of restriction site-associated DNA sequencing for genome scans of adaptation. Mol. Ecol. Resour. 17, 142-152. ( 10.1111/1755-0998.12635) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 100.Lou RN, Jacobs A, Wilder AP, Therkildsen NO. 2021. A beginner's guide to low-coverage whole genome sequencing for population genomics. Mol. Ecol. 30, 5966-5993. ( 10.1111/mec.16077) [DOI] [PubMed] [Google Scholar]
  • 101.Li JH, Mazur CA, Berisa T, Pickrell JK. 2021. Low-pass sequencing increases the power of GWAS and decreases measurement error of polygenic risk scores compared to genotyping arrays. Genome Res. 31, 529-537. ( 10.1101/gr.266486.120) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 102.François O, Caye K. 2018. Naturalgwas: an R package for evaluating genomewide association methods with empirical data. Mol. Ecol. Resour. 18, 789-797. ( 10.1111/1755-0998.12892) [DOI] [PubMed] [Google Scholar]
  • 103.Schielzeth H, Rios Villamil A, Burri R. 2018. Success and failure in replication of genotype–phenotype associations: how does replication help in understanding the genetic basis of phenotypic variation in outbred populations? Mol. Ecol. Resour. 18, 739-754. ( 10.1111/1755-0998.12780) [DOI] [PubMed] [Google Scholar]
  • 104.Supple MA, Shapiro B. 2018. Conservation of biodiversity in the genomics era. Genome Biol. 19, 131. ( 10.1186/s13059-018-1520-3) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 105.Segelbacher G, et al. 2022. New developments in the field of genomic technologies and their relevance to conservation management. Conserv. Genet. 23, 217-242. ( 10.1007/s10592-021-01415-5) [DOI] [Google Scholar]
  • 106.Willi Y, van Buskirk J, Hoffmann AA. 2006. Limits to the adaptive potential of small populations. Annu. Rev. Ecol. Evol. Syst. 37, 433-458. ( 10.1146/annurev.ecolsys.37.091305.110145) [DOI] [Google Scholar]
  • 107.Teixeira JC, Huber CD. 2021. The inflated significance of neutral genetic diversity in conservation genetics. Proc. Natl Acad. Sci. USA 118, e2015096118. ( 10.1073/pnas.2015096118) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 108.Kardos M, Armstrong EE, Fitzpatrick SW, Hauser S, Hedrick PW, Miller JM, Tallmon DA, Funk WC. 2021. The crucial role of genome-wide genetic variation in conservation. Proc. Natl Acad. Sci. USA 118, e2104642118. ( 10.1073/pnas.2104642118) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 109.Marks RA, Hotaling S, Frandsen PB, VanBuren R. 2021. Representation and participation across 20 years of plant genome sequencing. Nat. Plants 7, 1571-1578. ( 10.1038/s41477-021-01031-8) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 110.Pettorelli N, Barlow J, Nuñez MA, Rader R, Stephens PA, Pinfield T, Newton E. 2021. How international journals can support ecology from the Global South. J. Appl. Ecol. 58, 4-8. ( 10.1111/1365-2664.13815) [DOI] [Google Scholar]
  • 111.Maas B, Pakeman RJ, Godet L, Smith L, Devictor V, Primack R. 2021. Women and Global South strikingly underrepresented among top-publishing ecologists. Conserv. Lett. 14, e12797. ( 10.1111/conl.12797) [DOI] [Google Scholar]
  • 112.Rushworth CA, Baucom RS, Blackman BK, Neiman M, Orive ME, Sethuraman A, Ware J, Matute DR. 2021. Who are we now? A demographic assessment of three evolution societies. Evolution 75, 208-218. ( 10.1111/evo.14168) [DOI] [PubMed] [Google Scholar]
  • 113.Graves JL. 2019. African Americans in evolutionary science: where we have been, and what's next. Evol. Educ. Outreach 12, 18. ( 10.1186/s12052-019-0110-5) [DOI] [Google Scholar]
  • 114.Cronin MR, et al. 2021. Anti-racist interventions to transform ecology, evolution and conservation biology departments. Nat. Ecol. Evol. 5, 1213-1223. ( 10.1038/s41559-021-01522-z) [DOI] [PubMed] [Google Scholar]
  • 115.Kamath A, Velocci B, Wesner A, Chen N, Formica V, Subramaniam B, Rebolleda-Gómez M. 2022. Nature, data, and power: how hegemonies shaped this special section. Am. Nat. 200, 81-88. ( 10.1086/720001) [DOI] [PubMed] [Google Scholar]
  • 116.Ginther DK, Schaffer WT, Schnell J, Masimore B, Liu F, Haak LL, Kington R. 2011. Race, ethnicity, and NIH research awards. Science 333, 1015-1019. ( 10.1126/science.1196783) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 117.Fox CW, Paine CET. 2019. Gender differences in peer review outcomes and manuscript impact at six journals of ecology and evolution. Ecol. Evol. 9, 3599-3619. ( 10.1002/ece3.4993) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 118.Shen YA, Webster JM, Shoda Y, Fine I. 2018. Persistent underrepresentation of women's science in high profile journals. BioRxiv, 275362. ( 10.1101/275362) [DOI]
  • 119.Schell CJ, Guy C, Shelton DS, Campbell-Staton SC, Sealey BA, Lee DN, Harris NC. 2020. Recreating Wakanda by promoting Black excellence in ecology and evolution. Nat. Ecol. Evol. 4, 1285-1287. ( 10.1038/s41559-020-1266-7) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 120.Staniscuaski F, et al. 2021. Gender, race and parenthood impact academic productivity during the COVID-19 pandemic: from survey to action. Front. Psychol. 12, 663252. ( 10.3389/fpsyg.2021.663252) [DOI] [PMC free article] [PubMed] [Google Scholar]

Associated Data

This section collects any data citations, data availability statements, or supplementary materials included in this article.

Data Availability Statement

This article has no additional data.


Articles from Proceedings of the Royal Society B: Biological Sciences are provided here courtesy of The Royal Society

RESOURCES