ABSTRACT
Global patterns of population genetic variation through time offer a window into evolutionary processes that maintain diversity. Over time, lineages may expand or contract their distribution, causing turnover in population genetic composition. At individual loci, migration, drift and selection (among other processes) may affect allele frequencies. Museum specimens of widely distributed species offer a unique window into the genetics of understudied populations and changes over time. Here, we sequenced genomes of 130 herbarium specimens and 91 new field collections of Arabidopsis thaliana and combined these with published genomes. We sought a broader view of genomic diversity across the species and to test if population genomic composition is changing through time. We documented extensive and previously uncharacterised diversity in a range of populations in Africa, populations that are under threat from anthropogenic climate change. Through time, we did not find dramatic changes in genomic composition of populations. Instead, we found a pattern of genetic change every 100 years of the same magnitude seen when comparing Eurasian populations that are 185 km apart, potentially due to a combination of drift and changing selection. We found only mixed signals of polygenic adaptation at phenology and physiology QTL. We did find that genes conserved across eudicots show altered levels of directional allele frequency change, potentially due to variable purifying and background selection. Our study highlights how museum specimens can reveal new dimensions of population diversity and show how wild populations are evolving in recent history.
Keywords: allele frequency change, genomic diversity, museum specimens, population structure, time series genomics
1. Introduction
The genomic composition and diversity of species across their geographic range can reveal the relative importance of processes such as demography, drift and spatially varying selection. The evolutionary history of a species is reflected in its present‐day patterns of relatedness across the genome, and these patterns will change in the future as demography and environments change (Fulgione and Hancock 2018; Lee et al. 2017; Olalde et al. 2018; Rhoné et al. 2020). For example, regions that differ in their history of colonisation may show distinct patterns of diversity and genetic turnover through space (Lasky et al. 2024; Petkova et al. 2016). Furthermore, knowledge of geographic patterns in diversity and population structure can be used to optimise sampling designs for studies of genetic variation in phenotype (Fulgione and Hancock 2018).
While biologists have often studied geographic patterns in genotype and phenotype, their study of the temporal genomic dynamics has developed only more recently, largely due to a previous lack of data. As global environments are changing, species range‐wide study of temporal dynamics in population genomics could reveal corresponding evolutionary changes. However, the breadth of sampling required through space and time is a logistical hurdle. Recent studies have used ancient human sequences to demonstrate dramatic turnovers in population ancestry in some regions, as new lineages replaced older ones (Allentoft et al. 2024; Kennett et al. 2022; LaPolice et al. 2024; Olalde et al. 2018), or consistent geographic population structure through time (Antonio et al. 2024). For non‐human species, long‐term field studies have offered powerful windows into temporal dynamics (Bergland et al. 2014; Lynch et al. 2024; Troth et al. 2018). Global natural history collections made over the last couple of centuries are an underutilised but incredibly valuable resource for biology, holding a wealth of information on genotype and phenotype (Burbano and Gutaker 2023; Lopez et al. 2020). For example, researchers have used museum specimens to show demographic turnover in a plant species where there was dramatic expansion of tetraploids across parts of Europe formerly inhabited only by diploids (Rosche et al. 2024). Recent population studies have also used sequences of museum specimens to identify changes in genetic diversity over time (Bi et al. 2019; Gauthier et al. 2020) and the history of spread of plant pathogens (Yoshida et al. 2013). Furthermore, museum collections often hold samples from a wide geographic area, allowing greater spatial coverage in evolutionary studies.
Arabidopsis thaliana, the model plant (hereafter referred to as ‘Arabidopsis’), is a useful system for studying drivers of geographic and temporal turnover in genotype. Arabidopsis is an annual, largely self‐fertilising plant species with a broad native distribution in Eurasia and Africa (Fulgione and Hancock 2018; Yim et al. 2023). Populations of Arabidopsis occur across a wide range of climatic regions and different environments (e.g., from the Mediterranean coast to alpine systems) (Ågren and Schemske 2012; Elfarargi et al. 2023; Gamba et al. 2024; Montesinos et al. 2009; Yim et al. 2023). Global studies on A. thaliana have revealed high levels of genetic and phenotypic diversity among populations (Koornneef et al. 2004; Mitchell‐Olds 2001); this species has become a model for eco‐evolutionary studies (Takou et al. 2019; Turner et al. 2020; Vasseur et al. 2018; Wuest and Niklaus 2018).
Along with life history variation across contrasting environments, A. thaliana displays substantial large‐scale population structure (Beck et al. 2008; Lasky et al. 2012; Schmid et al. 2006; Sharbel et al. 2000). The largest genetic divisions within this species can be found between most Eurasian genotypes and the so‐called relict lineages associated with distinct mountain ranges in Africa, Atlantic islands and some areas of Mediterranean Europe (Alonso‐Blanco et al. 2016; Durvasula et al. 2017; Fulgione and Hancock 2018; Gamba et al. 2024; Lee et al. 2017). However, many such regions, especially in Africa (Yim et al. 2023), have been little sampled and it is likely there are additional uncharacterised unique lineages. Isolation by distance has also been detected at regional and local scales (Hesen et al. 2024; Lasky et al. 2024; Picó et al. 2008; Tyagi et al. 2016) suggesting that Arabidopsis gene flow is rather limited in space.
Plant populations are often adapted to their local environment (Ågren and Schemske 2012; Fournier‐Level et al. 2011; Hereford 2009; Lasky et al. 2018; Leimu and Fischer 2008). Individual genes underlying environmental adaptation in plants have been characterised for a number of these traits. For example, local adaptation has been mapped to natural variation in flowering time and phenology genes (Fulgione et al. 2022; Martínez‐Berdeja et al. 2020), genes affecting freezing tolerance (Lee et al. 2024; Monroe et al. 2016), trichomes (Arteaga et al. 2022), floral pigmentation (Todesco et al. 2022) and resistance to parasites and pathogens (Bellis et al. 2020; Karasov et al. 2014). However, these loci have been primarily identified and studied in the context of existing contemporary diversity, while loci underlying adaptation to environmental change through time are less well known (but see Exposito‐Alonso, Becker, et al. 2018; Franks et al. 2016; Lang et al. 2024; Troth et al. 2018). Furthermore, across the vast Arabidopsis range major elevational clines in some traits and loci reverse in direction between different mountains, indicating alternative local adaptation strategies (Gamba et al. 2024). This strongly suggests consideration of regional patterns is important to understand spatiotemporal patterns of genomic variation in Arabidopsis.
Environments are always changing, but current anthropogenic changes are especially rapid, and wild organisms are responding in some dramatic ways. Resurrection and long‐term experimental studies have shown evolutionary changes in quantitative traits and allele frequencies (Anstett et al. 2024; Hamann et al. 2018; Sekor and Franks 2018) and studies of museum specimens have shown changes in traits in response to environmental change (DeLeo et al. 2020; MacLean et al. 2018; Ng et al. 2023). In Arabidopsis we documented temporal phenotypic changes in herbarium specimens from the last two centuries, namely in collection date, leaf C:N and leaf d15N (DeLeo et al. 2020). The degree to which these changes are genetic versus plastic, and potential genetic changes are oligogenic versus polygenic, remains unknown. Recently, we used herbarium sequences to show that alleles associated with decreased stomatal density were rising in frequency at multiple loci (Lang et al. 2024; Latorre et al. 2022; Lopez et al. 2022). However, the degree of ancestry turnover in Arabidopsis populations and the potential change in quantitative trait loci (QTL) for ecologically important traits remains unexplored.
Multiple types of selection can influence temporal allele frequency dynamics. Abiotic and biotic environments can undergo a sustained directional shift, such as greenhouse gas‐induced warming, causing selection for new traits (Lynch and Lande 1993). As a result, the underlying allele frequencies may show directional shifts, including sweeps (Hayward and Sella 2022; Höllinger et al. 2019). Next, new beneficial mutations may rise in frequency, with some sweeping to fixation (Patwa and Wahl 2008). Other types of selection (e.g., frequency dependence) might cause more complicated temporal dynamics, which we set aside for our current study (Fijarczyk and Babik 2015; Siewert and Voight 2017). Here, we focus on directional allele frequency shifts. By identifying genes showing dramatic allele frequency shifts, researchers may gain insight into mechanisms of adaptation to directional shifts in environment. Of course, drift will also cause allele frequency shifts over time; thus, it may be necessary to identify loci with strong shifts relative to the genomic background (Akbari et al. 2024).
Despite changing environments, it is likely that many traits and loci do not experience changes in selection and instead are subject to consistent stabilising or purifying selection. For example, many genes are highly conserved in structure over speciation events and many millions of years (Kachroo et al. 2015; Margoliash 1963). However, it is important to recognise that purifying selection will still lead to non‐random change in frequencies of segregating alleles over time, that is, decreases in deleterious allele frequency. In simulations, (Buffalo and Coop 2020) demonstrated how background selection caused genome‐wide positive temporal autocorrelation in allele frequencies (i.e., directional allele frequency change) as deleterious variants are selected against. Thus, conserved genes might show some evidence of directional allele frequency change. However, it is unknown how purifying and background selection impact locus‐specific temporal change.
Here, we sequenced 130 herbarium specimens of Arabidopsis thaliana and combined these with new sequencing of recent field‐collected accessions and seedbank accessions, and published sequences of natural inbred lines and herbarium specimens (Alonso‐Blanco et al. 2016; Durvasula et al. 2017). These genotypes greatly expand the geographic range of sequenced Arabidopsis genomes into regions of Africa and Asia, and were collected from nature across a period of nearly 200 years. These data were used for several goals. First, we sought to generate a more complete view of Arabidopsis genetic diversity and population structure. Second, we sought to determine how population genetic composition has changed over time across the species range. Toward these goals, we focused on the following questions:
What is the geography of population structure and relatedness across Africa and Eurasia? Are African populations diverse and genetically distinct from each other and from those in Eurasia (i.e., ‘relicts’)?
Has geographic population structure remained static? Or have new lineages spread across the Arabidopsis range over the last 150 years?
Is there genetic turnover through time, indicating isolation‐by‐time?
Are QTL for ecologically important traits enriched for temporal turnover in allele frequency, suggesting changing selection?
Do conserved genes show lower temporal turnover than non‐conserved loci, suggesting continued conservation? Or do conserved genes show higher turnover due to purifying and background selection?
2. Methods
2.1. Sampling of Herbarium Specimens, Wild Individuals and Published Data
We obtained genomes of 527 Arabidopsis thaliana samples for this study (Table S1–S14). This includes data newly generated (n = 225) from multiple sources: herbarium specimens with ancient DNA (aDNA) protocols in a clean lab (n = 130), new collections from extant wild populations (n = 91), and stock centre accessions of (n = 4) naturally inbred lines. We also used 302 published genomes from stock centre lines (n = 199), herbarium (n = 38) and natural populations (n = 65) (Alonso‐Blanco et al. 2016; Durvasula et al. 2017; Lang et al. 2024). The published genomes from stock centre lines were mostly collected in the last two decades (Figure 1). However, a few dozen were originally collected in western Europe in earlier decades. For temporal analyses, these accessions were included based on the year they were collected in the wild, following (Wilczek et al. 2014).
FIGURE 1.

Sequenced accessions showing their distribution over time (A‐B) and coloured according to geography (C) or ADMIXTURE cluster (G) and with shapes indicating whether they were herbarium specimens (triangles) or sequenced from stock centre or newly collected accessions (circles). Neighbour joining tree (D) includes sample codes with country abbreviation and year collected from the wild (Table S1–S14). Two‐dimensional MDS for the entire dataset (E) highlights the divergence between Africa and Eurasia and (F) for Eurasia highlights the distinctness of the Iberian relicts. Specimens from countries of note are labelled on the tree. Cross validation error was lowest for ADMIXTURE K = 6 so these results are shown (G), with triangles at bottom indicating herbarium specimens. Shown are only accessions included in population genetic analyses (after filtering for balance between modern collections and herbarium).
Herbarium sampling was greatest for Germany, Spain, and Norway (n > 30 accessions each), with additional sampling from Russia, Ethiopia, and Britain (n > 10 accessions each). To uncover population genomic patterns in unstudied regions, we included samples from regions previously unrepresented in the literature: 5 countries (Kenya, Rwanda, Eritrea, the Democratic Republic of Congo, Nepal) and a large Mediterranean island (Sardinia). We also sequenced new populations from north of the Arctic circle, up to > 68° latitude in Norway. The herbarium samples ranged in year of collection from 1817 (Germany), 1838 (Ethiopia), 1860 (Russia) to as recent as 2011 (Tanzania) and 2010 (Spain). To compare with herbarium specimens from the same region, we made new field collections of 91 individuals, 21 from Ethiopia (in 2017/2018), 9 from Uganda (in 2018), and 61 from Norway (in 2009/2010).
Publicly available data were obtained from 199 accessions of the 1001 Genomes project, selected based on geographic proximity to herbarium specimens (Alonso‐Blanco et al. 2016) and from 70 African samples (65 individuals from wild populations and 5 herbarium specimens) (Durvasula et al. 2017). In total, our samples encompass 32 countries in Eurasia and Africa, representing a large part of the native range of Arabidopsis (Figure 1) (Yim et al. 2023). We then down‐sampled the modern collections from Morocco and Norway to balance with the sampling from herbarium specimens.
2.2. DNA Extraction, Library Preparation and Sequencing: Newly Generated Data
One hundred thirty newly obtained samples from herbaria were transported into a dedicated ancient DNA clean laboratory at Pennsylvania State University, USA. DNA was extracted using specialised protocols detailed in Supporting Information. After DNA extraction, we investigated the DNA fragmentation pattern for each sample and proceeded to perform library preparation based on the particular pattern of each sample. Using the following criterion, samples were categorised as high or low DNA fragmentation. Lowly fragmented samples showed DNA above the 500 bp ladder and were subjected to a short shearing step (30 s) using a M220 Focused Ultrasonicator (Covaris) prior to library preparation (detailed library preparation protocol in Supporting Information), while highly fragmented samples were unsheared.
A total of 95 fresh samples were included in this study (61 field samples from Norway, 30 from Africa and 4 from the INRA stock center). Thirteen fresh leaf samples were collected from the field in East Africa, while the remaining 17 were collected as seeds. Details for DNA extraction and library preparation are found in the Supporting Information. Samples were sequenced on Illumina platforms to obtain PE 150 bp reads.
2.3. Data Preprocessing and de Novo SNP Calling
Full details on filtering, mapping, and SNP calling are found in the Supporting Information. Herbarium samples were mostly newly generated data (130). To these, we added five samples from the African genomes (Durvasula et al. 2017) and 33 German genomes (Lang et al. 2024) also collected from herbarium vouchers. Raw data for the African genomes was obtained from the European Nucleotide Archive (ENA) of the European Molecular Biology Lab–European Bioinformatics Institute (EMBL–EBI) and German genomes from (Lang et al. 2024). Raw read sequence data were assessed with FastQC (http://www.bioinformatics.babraham.ac.uk/projects) to confirm that they met our quality standards. Genome sequencing coverage ranged from 81.41% to 98.91%. Mean depth of the covered portion of the genome showed a wide range, from 1 to 42.6 (median = 8.4, Table S2). For all herbarium samples, cytosine deamination profiles characteristic of ancient DNA were verified using mapDamage 2.0 (Jónsson et al. 2013) (Figure S1). SNP discovery was done using a pseudohaplotype approach (see Supporting Information for more detail) (Kistler et al. 2018).
2.4. Statistical Analysis
2.4.1. Population Structure
We first analysed global population structure by generating a set of high coverage and unlinked SNPs, that is, those that remained after excluding those with > 5% missing calls and filtering for linkage disequilibrium (PLINK indep‐pairwise filtering SNPs with R 2 > 0.1 in 50 SNP windows with 10 SNP steps between windows) (Chang et al. 2015). We calculated pairwise genetic distances between all samples (identity‐by‐state/Hamming distance, PLINK, flat missingness correction) to generate a neighbour joining tree and multidimensional scaling k = 2 plot. We also calculated genetic distances and MDS in two dimensions separately after repeating the missingness and linkage filtering for two regional sets: (1) east and south African genotypes and (2) Eurasian genotypes.
To further characterise population structure, we implemented ADMIXTURE genetic clustering, across a range of cluster numbers (1–15) (Alexander et al. 2009). We applied ADMIXTURE to all global samples combined as well as a subset of south and east African samples, the region sampled well by our new data but previously the least studied.
2.4.2. Isolation by Distance
We tested for geographic population structure and isolation by distance in spatially explicit analyses. To account for non‐independence among pairwise distance measures involving the same individual, we fit mixed‐effects models that include a random effect for each individual. We then compared them with null models based on AIC (ResistanceGA, (Peterman 2018), these results were consistent when we excluded samples with > 25% missing SNP calls).
To better understand the spatial scales of isolation by distance and its heterogeneity among the previously well studied Eurasian populations compared to the newly sampled regions of Africa, we calculated wavelet genetic dissimilarity (Lasky et al. 2024) which quantifies scale‐specific genetic turnover among populations. That is, wavelet dissimilarity is a measure of genetic distance at a specific spatial scale (determined by the dilation of the wavelet function). Wavelet genetic dissimilarity increases at greater scales under patterns of isolation by distance, patterns that may differ between regions based on their level of gene flow and population age (Lasky et al. 2024). Within Eurasia and two African regions, we calculated the average wavelet dissimilarity among sampled locations at a range of scales from 1 to 500 km.
2.4.3. Isolation by Time
We studied whether geographic population structure was stable over the period of the study (1817–2018). To test for major turnover in genetic composition, we focused on the well‐sampled regions in Europe and asked whether different genetic clusters emerged within regions over time. We implemented ADMIXTURE on Eurasian genotypes and chose K = 6 because it resolved many regional differences in genotype before a sharp increase in cross‐validation error at K = 7 (Figure S3). We then divided the well‐sampled areas into five discrete regions: Iberia, Britain, Norway, Northern Germany, and Southern Germany, each dominated by a different genetic cluster. We then used non‐parametric Spearman's rank correlations to test whether the proportional assignment of genotypes for the most dominant ADMIXTURE cluster within each region changed over time.
To test for more continuous temporal genomic change, we fit mixed effects models as with geographic distance, but added a covariate for separation in time (year of collection) to explain pairwise genetic distances. As with the pure geographic models, these models include individual‐specific random effects to account for individuals that may have particularly low or high genetic distance compared to all others. For three regions that were the best sampled (Germany, Norway, and Iberia), we also tested for turnover through time within the region while accounting for geographic distance.
2.4.4. Change in Allele Frequency at Specific Loci
We tested for evidence of directional allele frequency shifts in QTL underlying traits that are potentially important in environmental adaptation in Arabidopsis and showed evidence of temporal phenotypic change. We previously documented change in Arabidopsis herbarium phenotypes, including many of the sequenced specimens here (DeLeo et al. 2020). In particular, we found an increase in the date of collection and photothermal units accumulated by date of collection, signifying phenological shifts where plants were collected later in growing seasons across eastern Europe and central Asia (DeLeo et al. 2020). We also found an increase in leaf C:N ratio over time in a region from the Mediterranean to central Europe (DeLeo et al. 2020). While DeLeo et al. (2020) found no change in 13C discrimination (Δ13C) over time, Lang et al. (2024) recently showed changes in the frequency of alleles associated with stomatal traits over time; thus, we decided to include putative QTL for Δ13C. We used mixed‐model GWAS results for flowering time from (Alonso‐Blanco et al. 2016), for germination/dormancy from (Martínez‐Berdeja et al. 2020), and for leaf C:N and δ13C from (Gamba et al. 2024). For flowering time (the trait measured on the most genotypes), we further implemented regional GWAS separately for Iberia, Germany, and Fennoscandia (Norway, Sweden, Finland) (Alonso‐Blanco et al. 2016). We used univariate linear mixed models in GEMMA v.0.98.3 (Zhou and Stephens 2012) excluding loci with MAF < 0.05 and calculating Wald test p‐values.
To test for changes in selection over time at putative QTL for these traits, we first characterised temporal directional allele frequency trends across the genome. We used several analyses with different strengths. We first used non‐parametric Wilcoxon tests determining if alternate alleles had different median years of sample collection (function ‘wilcox.test’ in base R) (R Core Team 2023). Additionally, we used multiple logistic regression to test for allele frequency change over years while controlling for linear effects of latitude and longitude (function ‘glm’ in base R). Finally, we also included a test that included kinship random effects to identify loci with patterns deviating from the genomic background change through time (Akbari et al. 2024), while also accounting for spatial trends associated with latitude and longitude (using ‘mmer’ function in the ‘sommer’ package) (Covarrubias‐Pazaran 2016).
We tested for these allele frequency temporal dynamics across the native range (Eurasia and Africa) and also within well‐sampled regions (Iberia, Germany, Norway) because different regions may undergo different changes in selection or phenotypic change (DeLeo et al. 2020). We tested whether top GWAS loci were enriched for temporal allele frequency shifts. We determined the strength of temporal change in SNPs (defined by the bottom 0.05, 0.1, 0.25 p‐value quantiles for the temporal allele frequency change tests) among the GWAS top SNPs (25, 50 or 100 SNPs, after removing nearby SNPs within 25 kb). We compared this quantile to those generated from a null distribution generated from 1000 circular permutations (around the genome) of SNPs' trait temporal change p‐values.
2.4.5. Purifying and Background Selection
We tested whether there was evidence of distinct evolutionary processes acting on genic DNA versus non‐genic DNA, and we also tested conserved versus non‐conserved genes. First, we compared the 0.01 p‐value quantile of temporal allele frequency change for genic versus non‐genic markers. To generate a null distribution for this comparison, we conducted 1000 permutations of annotation of genic versus non‐genic (circularly around the genome).
Next, we used a list of Arabidopsis genes from orthogroups conserved across eudicots identified by (Sun et al. 2018): 16,799 conserved versus 10,856 non‐conserved genes. Conserved genes were defined based on orthogrouping of all genes from Arabidopsis and six other eudicot species (divergence > 120 mya, Ipomoea nil, Solanum tuberosum, Solanum lycopersicum, Capsicum annuum, Coffea canephora, Mimulus guttatus ) (Sun et al. 2018). Orthogroups that contained genes from at least six of these seven species were defined as conserved orthogroups. Arabidopsis genes within these conserved orthogroups were classified as conserved, while those not in conserved orthogroups were classified as non‐conserved.
We first compared the 0.01 quantile of temporal allele frequency changes between all genic SNPs in conserved versus non‐conserved genes, using permutations of SNP annotation. The site frequency spectrum likely differs between genic and intergenic SNPs, and between SNPs in conserved versus non‐conserved genes, potentially influencing power to detect temporal change. Thus, we also tested these genomic contexts for enrichment of temporal allele frequency changes for ‘rare’ (0.05 ≥ MAF < 0.1) and ‘common’ (MAF > 0.4) SNPs in separate analyses.
We also conducted gene‐level tests. Because longer genes tend to show greater conservation (potentially stronger purifying selection) than shorter genes (Lipman et al. 2002), we divided genes into bins based on amino acid lengths. The effect of length on conservation was evident in the data from (Sun et al. 2018): non‐conserved genes' median length was 226 amino acids while the conserved median was 416 (Wilcoxon test, p < 10−16). To obtain a test statistic for the temporal change of each gene, we calculated the lower 0.1 tail (or 0.25, results were qualitatively the same) p‐values for temporal change for SNPs in the coding region. We then permuted gene conservation status circularly around the genome 1000 times and developed a null distribution of median difference in gene p‐values between conserved versus non‐conserved genes, matching for gene length (in five bins: < 200, 201–400, 401–600, 601–800, and 801–1000 amino acids long). We then compared the null permutations to the observed in a two‐tailed test for each gene length bin. Because little is known about how background selection might influence variation in temporal allele frequency change across the genome, we conducted forward genetic simulations of purifying and background selection (see Supporting Information for more detail).
2.4.6. Genomic Prediction of Trait Change
As an alternate approach to testing for directional evolution of ecologically important traits, we also used whole‐genome prediction. Whole‐genome prediction models can work well for polygenic traits and assume an infinitesimal model of trait variation (Hill and Kirkpatrick 2010) and have previously been successfully employed to predict local adaptation in Arabidopsis (Gienapp et al. 2017). To create a genomic prediction model, we used a training dataset of 421 sequenced A. thaliana genotypes (Alonso‐Blanco et al. 2016). Each genotype had flowering time data at constant temperatures of 10°C (FT10) and 16°C (FT16) (Alonso‐Blanco et al. 2016). The kinship matrix was generated with PLINK v1.90b6.26 (Chang et al. 2015) using a minor allele frequency filter of 0.05. The ‘kin.blup’ function from the rrBLUP package (Endelman 2011) was used to conduct genomic predictions for flowering time. To assess the accuracy, or extent of overfitting in our genomic prediction model, we cross‐validated our data for FT10 and FT16 by conducting tenfold genomic predictions. We then used multiple linear regression models to test for changes in predicted flowering times across years within each of three regions (Iberia, Germany, and Norway), while accounting for elevation, latitude, and longitude.
3. Results
3.1. An Expanded View of Arabidopsis Population Structure in Its Native Range
We first analysed global population structure using a set of high coverage, unlinked 201,299 SNPs. An MDS plot in two dimensions separates genotypes from North Africa, East and South Africa, and Eurasia (Figure 1C). ADMIXTURE cross‐validation error was minimised at K = 6. At K = 6, the samples split into North African, South and East African, Iberian, British/Central European, Scandinavian, and Eastern European/Asian groups (Figure 1E, see other K values in Figure S2).
The Sardinian sample was from low elevation near the coast and was assigned to a mix of Eurasian non‐relict and North African/Iberian relict ancestries. The Nepalese sample was estimated to have primarily Eurasian non‐relict ancestry, but with small portions of ancestry from both African groups, suggesting potential ancestry of a relict group. The MDS in two dimensions of Eurasian populations showed the Nepalese sample is toward one extreme alongside Russian, Kazakh, and Ukrainian populations (Figure 1D).
African Arabidopsis populations are understudied but clearly genetically distinct (Figure 1B,C) (Durvasula et al. 2017). Because these African populations are under threat from future climate change (Yim et al. 2023), and because the bulk of previously unstudied countries contributed by our herbarium samples were from East Africa, we conducted a focused analysis on African populations. A neighbour‐joining tree showed major differentiation among mountains (Figure 2A). This differentiation is consistent with the overall rarity of Arabidopsis and low suitability in low elevations in East Africa (Yim et al. 2023), suggesting very little gene flow between mountains over long periods. However, the Tanzanian (mostly lower elevation mountains), Mt. Suswa (Kenya), and South African populations were more similar to each other than were genotypes across other individual mountains, suggesting greater or more recent gene flow in these more southerly regions (Figure 2). There were signals of geographic barriers, with Ethiopian populations on either side of the Rift Valley being most different from each other (Figure 2).
FIGURE 2.

Accessions from East and South Africa, with shapes indicating whether they were herbarium specimens (triangles) or sequenced from fresh tissue from stock centre or newly collected accessions (circles). Mountains of origin are labelled on the neighbour‐joining tree (A) and map (B). (C) MDS in two dimensions with mountains labelled. (D) Cross validation error lowest for ADMIXTURE K = 4; so these results are shown, with triangles at bottom indicating herbarium specimens.
An MDS plot of East/South African samples (n = 52) divided Horn of Africa populations (Ethiopia & Eritrea) from those further south along the first dimension, while the second dimension separated populations on either side of the Rift Valley in Ethiopia from each other as well as those from further south (Figure 2C). ADMIXTURE K = 4 had the lowest cross‐validation error, splitting high‐elevation Ethiopian populations in Bale and Choke into two groups on either side of the rift valley, Mt. Elgon & Mt. Kenya shield volcanoes in Uganda & Kenya as another group. The Simien mountains, lower‐elevation samples in the Horn along with Mt. Suswa (Kenya), all Tanzanian populations, Mt. Karismbi (Democratic Republic of Congo & Rwanda) and South Africa were all in another group. The Rwandan & DRC samples are both from Mt. Karisimbi, which straddles these nations' borders, and these two genotypes were highly similar.
3.2. Patterns of Population Structure to Assess the Provenance of a Historically Important Specimen
Genotypes from different elevations of the same mountain were typically more closely related than they were to genotypes from similar elevations on different mountains (Figure 2), as is true for most mountain ranges in Eurasia and Africa (Gamba et al. 2024). However, an exception was our oldest specimen in the region, from 1838, collected by Wilhelm G. Schimper at a location in the Simien Mountains. The location, according to Schimper, was ‘Demerki’, (sometimes ‘Demerkit’) a name not apparently in current use, or a corruption of another name. The ‘Demerki’ sample falls in the neighbour‐joining tree alongside a 1969 Eritrean sample from 1800 m asl (see ‘low elevation Simien’ in Figure 2). ADMIXTURE on African accessions at K = 5 (only slightly lower cross validation error than the K = 4 shown in Figure 2) also assigns the ‘Demerki’ and Eritrean genotypes 30%–40% ancestry from the group of genotypes from Tanzania, many at lower elevations (unlike the higher elevation Simien genotypes which show no such ancestry). Because of this similarity with lower elevation genotypes, we infer that ‘Demerki’ was likely a site in Simien at lower elevation than 3500 m.
Based on the low genetic similarity, the demographic history of these Horn of Africa populations < 2500 m asl (including populations known from herbarium specimens from Djibouti & Somalia) (Yim et al. 2023) appears distinct from the mostly higher elevation populations elsewhere in East Africa. Similarly, the 1953 sample from 1750 m asl in the Western Usambaras mountains in Tanzania was highly genetically differentiated from the other Tanzanian populations at higher elevations (Figure 2). Thus, in East African low mountain ranges near the Indian Ocean, Arabidopsis populations seem distinct from populations nearby at much higher elevations, possibly due to a distinct history, such as greater or more recent gene flow among populations and adaptations to low elevations.
3.3. Isolation by Distance
We found significant isolation by distance globally, including all accessions with coordinates (Figure 3, n = 404, linear mixed models with individual random effects, null AIC = −799,279, distance AIC = −853,089; general linear model of distance R 2 = 0.41). For non‐relict accessions in Eurasia, we also found significant isolation by distance (n = 303, null AIC = −509,158, distance AIC = −526,778; general linear model of distance R 2 = 0.36). Isolation by distance was also significant across East Africa (Figure 3, n = 50, null AIC = −8998, distance AIC = −9765). Within the two most sampled East African mountains, we also found significant isolation by distance: Mt. Elgon, Uganda (max. distance = 18 km, n = 10, null AIC = −432, distance AIC = −442) and the Bale Mts., Ethiopia (max. Distance = 43 km, n = 14, null AIC = −821, distance AIC = −873).
FIGURE 3.

Isolation by distance across the range of Arabidopsis. (A) Pairwise genetic distances within regions, comparing Eurasian non‐relicts to East African populations and (B) a truncated version focused on distances < 1000 km. (C) Comparing pairwise genetic distance within two of the best sampled regions in East Africa with Eurasian non‐relicts. (D) Scale‐specific wavelet genetic dissimilarity (line = mean among sampled locations, ribbon = ±1 SD) showed the much greater genetic turnover at scales ~100–500 km for both East African regions compared to Eurasian non‐relicts.
Alonso‐Blanco et al. (2016) found relict accessions showed a steeper increase in genetic distance over geographic distance, compared to non‐relict accessions, suggesting longer histories of isolation for relicts. We compared East African samples to non‐relict Eurasian samples and found a similar pattern: at distances > 250 km, East African samples were more genetically distinct than were non‐relict accessions from Eurasia at the same distance (Figure 3). At a distance of ~700 km, we found the greatest genetic distance in East Africa, separating populations from the Great Lakes region from those farther north in the Horn of Africa. These were more genetically distinct than were accessions from Nepal versus Portugal, > 7800 km apart (the most geographically distant non‐relict Eurasian samples). These results were also supported by wavelet dissimilarity analysis, which quantified scale‐specific genetic turnover among populations. Horn populations showed the greatest turnover at ~50–500 km scales, with Great Lakes populations just slightly lower (Figure 3). By contrast, Eurasian non‐relicts showed much lower genetic turnover up to ~500 km scales.
3.4. Genetic Change Through Time and Space
We saw no dramatic changes in ancestry over time. This can be observed in the neighbour‐joining tree and ordinations (Figure 1) where herbarium specimens from a given region are most closely related to modern collections from the same region. Additionally, genetic clustering of Eurasian accessions by ADMIXTURE with K = 6 showed little change in estimated ancestry assignments over the study period (Figure 4). None of the regionally dominant genetic clusters changed in the proportion of sample composition over time (Spearman's rank correlation, year versus proportion of most regionally dominant cluster, all p > 0.08; also true when using K = 3, the K with lowest cross validation error in Eurasia). This indicates there were no major turnover events in population composition over the period of our study.
FIGURE 4.

Genetic cluster membership over time (inset barplots) for regional subsets of genotypes (dashed boxes) with individual genotypes shown as pie charts indicating cluster assignment by ADMIXTURE with K = 6. Each genetic cluster that was most common in a region showed no significant change in the proportion of assigned ancestry for local genotypes over time (Spearman's rank correlation test, all p > 0.08). Herbarium specimens and stock centre genotypes are included here.
To examine changes in the distributions of deeper levels of genomic differentiation, we tested for changes in the distribution of relicts in Iberia, where they were at modest frequency (13%, Alonso‐Blanco et al. 2016). Alonso‐Blanco et al. (2016) noted that Iberian relict accessions in the 1001 Genomes panel tended to be found in landscapes with low anthropogenic disturbance and dry summers. We found in our Iberian herbarium sequences that this pattern was consistent across the 20th century (Figure 5B). Dividing Iberian samples into those from 1908 to 1968 and those from 1971 to 2010 (leaving equal sample size groups), and adding the 1001 Genomes genotypes (Alonso‐Blanco et al. 2016), we found that relicts were in significantly drier summer climates but with no significant change in this pattern over time (precipitation in warmest quarter two‐way ANOVA, relict p = 0.0358, time group p = 0.5111, relict X time group interaction p = 0.9458).
FIGURE 5.

There is modest temporal genetic turnover (A) shown through residuals from a geographic mixed model versus time difference, with a linear model (black) and spline (red) fitted, while (B) at coarser levels of relatedness the distribution of relicts in drier parts of Iberia remains consistent through time. Note the changing y‐axis scales in (A) to show the statistically significant, albeit noisy, temporal turnover. (B) excludes Pyrenees because we did not have these populations sampled from herbaria.
Despite the stability in regionally dominant genetic clusters, we found evidence for modest continuous genetic turnover through time (Figure 5A). Among all regions, AIC favoured a model of isolation by distance and isolation by time (n = 404, linear mixed model with distance only AIC = −853,089, distance and time AIC = −853,491; general linear model with distance only R 2 = 0.41, distance + time R 2 = 0.42). However, changes in genetic distance with time separation could partly result from changes in our relative sampling of different regions (e.g., 11% of herbarium samples before 1933, the median year, were relict lineages, vs. 32% 1933 and onward) or geographic heterogeneity in temporal change. To avoid this problem, we focused the analysis on some genetic clusters and geographic regions.
Among Eurasian non‐relicts, a model with both time and geographic distance was again favoured over a geography model only (n = 319, linear mixed model with geographic distance only AIC = −577,470, geographic and time distance AIC = −577,688; general linear model with distance only R 2 = 0.36, distance + time R 2 = 0.38). To put the genetic turnover through time into a comparable context, we calculated the increase in genetic distance with 100 years separating samples in terms of the geographic distance expected to give the same genetic distance. While at first glance the slope of temporal genetic turnover in Figure 5 may seem slight, the estimated turnover across 100 years in Eurasian non‐relicts was equivalent to that occurring over 185 km of geographic distance (for all accessions the figure was 299 km).
In Germany (n = 94), the model with isolation by distance and time was favoured, such that with 100 years separating samples the genetic distance was expected to be of the same magnitude as the genetic distance between samples 70 km apart in geographic distance (mixed model geography AIC = −50,286, geography + time AIC = −50,314; general linear model with distance only R 2 = 0.12, distance + time R 2 = 0.13). For Norwegian (n = 44) and non‐relict Iberian samples (n = 44) a model of isolation‐by‐distance (but not time) was favoured by AIC (Norway: geography AIC = −9496, geography + time AIC = −9496; non‐relict Iberia geography AIC = −9835, geography + time AIC = −9833).
3.5. Temporal Change in Allele Frequency of Putative Quantitative Trait Loci
In general, we found little consistent evidence that putative QTL for several ecologically important traits (GWAS SNPs) were enriched for directional allele frequency change. A list of top SNPs showing directional allele frequency change and nearby genes is included Table S3. For Eurasian genotypes (n = 339; 1,209,375 SNPs) several traits showed nominally significant (α = 0.05) enrichments for some combinations of top GWAS SNPs and allele frequency change statistical model, but none of these were significant after controlling for FDR = 0.05 (Table S4). The same was true in regional analyses using species‐wide GWAS (none significant at FDR = 0.05, Tables S5–S7). However, because the genetic basis of variation may change among regions, we also tested SNPs from regional GWAS. We found Iberian flowering time (10°C) SNPs were strongly enriched in temporal allele frequency turnover (n = 58 genotypes, top 25 SNPs, FDR = 0.05, Table S8, Figure 6). We did not find any enrichment in Fennoscandia flowering time SNPs' turnover in Norway (n = 45 genotypes, Table S9). By contrast, German flowering time GWAS SNPs showed significantly reduced change over time, for both 10°C and 16°C (n = 96 genotypes, Table S10, Figure 6).
FIGURE 6.

Allele frequency trajectories for different subsets of SNPs (lines) and regions, modelled using generalised additive models (GAMs) for visualisation. Allele frequency trajectories are signed so that the y‐axis indicates the increase in frequency of the allele more common in recent years (the ‘new allele’) compared to the beginning of the time series. SNPs with significant temporal allele frequency change in linear mixed models controlling for kinship and geography (p < 0.05 for A–D, p < 0.01 for E, F) are shown in black. The random SNPs and the genic/intergenic SNPs shown are single draws from the indicated categories.
3.6. Lower Directional Allele Frequency Change in Genes, Especially Conserved Genes
Next, we tested enrichment of SNPs in genic regions for directional allele frequency change. We found across Eurasia, genic SNPs showed significantly less directional allele frequency change than intergenic SNPs genes (permutation test for 0.01 quantile of logistic and mixed model year effects, p = 0.006 and p < 0.002, respectively, example in Figure 6E,F). Additionally, genic SNPs of conserved genes showed significantly less directional allele frequency change than genic SNPs of non‐conserved genes (permutation test for 0.01 quantile of logistic and mixed model year effects, p < 0.002 for both). These patterns were generally consistent within regions (Table S11). These results were consistent when we restricted the analysis to only SNPs with MAF 5%–10% and those with MAF > 40% (Table S12).
At the gene level, we also found that the conserved genes showed evidence for different types of selection depending on gene length (Figure S4). Eudicot conserved genes less than 200 AA sometimes had higher directional allele frequency change (p < 0.05 for some models and regions, Table S13). By contrast, eudicot conserved genes from 200 to 400 AA were not significantly different from non‐conserved genes. Furthermore, genes in amino acid length bins from 400 to 1000 showed significantly less directional allele frequency change than null expectations (p < 0.05 many models and regions, Table S13). We found these patterns were consistent within Germany and Iberia, but not statistically significant in Norway (Table S13).
The forward genetic simulations we conducted were variable in whether they showed genic regions under background selection having greater or less temporal allele frequency changes estimated with our approach (Figure S5). This variability is in contrast to the more consistent effect of background selection of increasing genome‐wide temporal autocorrelation in allele frequency (Buffalo and Coop 2020). In our simulations, genic SNPs (where deleterious mutations could occur; intergenic SNPs were all neutral) showed a significant depletion in temporal allele frequency changes in some simulations, while in other simulations they showed a significant enrichment in temporal allele frequency changes over intergenic SNPs.
3.7. Temporal Change in Allele Frequency: Genomic Prediction
Out‐of‐sample genomic predictions of flowering time were accurate with 10‐fold cross validation (FT10 r = 0.70, FT16 r = 0.68). As a positive control, in genome‐predicted flowering times we recovered a known cline: Iberia showed strong elevational clines (multiple linear regression; FT10 t = 5.3, p < 10−6; FT16 t = 4.8, p < 10−5) as observed from common garden experiments (Gamba et al. 2024; Montesinos‐Navarro et al. 2011). When adding a year term to regressions, however, we only found a slightly significant advancement in predicted flowering time at 10°C over time in Germany (t = −2.5, p = 0.0135) but otherwise, we did not find any significant change in predicted phenology over time (Table S14). This general lack of clear evolution of flowering time is consistent with the collection date of herbarium specimens, which have not changed in western Europe, in contrast with eastern Europe to central Asia where dates were later in later years, regions not well sampled here (DeLeo et al. 2020).
4. Discussion
To understand the importance of genetic variation in adaptation and phenotypic variation, it is important to characterise broader patterns of relatedness and genome‐wide variation across a species. However, generating comprehensive population genomic surveys of widespread species is challenging due to the logistics of studies at such scales. For example, the Arabidopsis 1001 Genomes project made great progress by resequencing genotypes from across most of the European range (Alonso‐Blanco et al. 2016), but greatly under‐sampled regions of Asia and Africa (Durvasula et al. 2017; Hsu et al. 2019; Roy 2018; Zou et al. 2017). Historically, research on Arabidopsis natural genetic variation has had a strong European bias (Hoffmann 2002; Koornneef et al. 2004). However, African populations in particular show high genetic divergence from each other and from Eurasian populations (Durvasula et al. 2017; Gamba et al. 2024) and here we add substantially to the known diversity and its distribution in Africa. Additionally, high elevation African populations (samples in this study mostly from > 4000 m asl) occupy outlier environments (Gamba et al. 2024), suggesting a great resource of undiscovered locally adapted genes and traits. Our use of museum sequencing allowed us to rapidly fill in important gaps in unstudied populations of Arabidopsis.
Temporal change in population size and allele frequency has often been inferred indirectly using current snapshots of population genetic composition (Nielsen et al. 2005; Schiffels and Durbin 2014; Slatkin and Hudson 1991). An exception is the rapidly growing field of ancient human genetics, which is starting to reveal the sometimes dramatic changes in population structure and ancestry over the last several thousand years (Allentoft et al. 2024; LaPolice et al. 2024; Olalde et al. 2018). However, there are few similar studies in other species outside of agricultural species (Kreiner et al. 2022; Smith et al. 2019; Swarts et al. 2017; Verdugo et al. 2019). By contrast, museums house millions of wild specimens covering centuries of sampling, providing a major resource to learn about evolution in response to contemporary environmental changes (Burbano and Gutaker 2023; Lopez et al. 2020). Here, we used Arabidopsis specimen sequences to demonstrate temporal population genomic turnover, although we see little evidence of dramatic turnover in the ancestry of the type seen in humans. Nevertheless, this turnover is heterogeneous across the genome, identifiably so, despite the limited outcrossing in this species. We showed how many genes conserved over many millions of years show distinct patterns of turnover during the study period (1817–2018).
4.1. Global Population Structure
By sequencing museum specimens, we were able to fill in major gaps in global population structure especially in Africa, and important additions in Norway, Sardinia, and Nepal. We found that east and southern African Arabidopsis represent a group of populations highly distinct from those in North Africa and Eurasia, with major divergence between populations from different mountains across east Africa (Gamba et al. 2024). We showed that the level of genetic divergence between African populations increases with spatial distance at a rate much greater than that seen in Eurasia. This is consistent with the hypothesis that these populations have been spread across East Africa for a long period of time and represent a potential origin of the Arabidopsis thaliana species (Durvasula et al. 2017; Fulgione and Hancock 2018).
The high divergence between mountains was especially true for high elevation populations in the Horn of Africa where the East African Rift Valley separates the two groups of greatest divergence; consistent with findings in Trifolium (Wondimu et al. 2014). Furthermore, the apparently high diversity of Arabidopsis from Bale (Figure 2) is consistent with these mountains also being a centre of diversity for Trifolium and Carduus (Wondimu et al. 2014) perhaps because of the topography of Bale: a high elevation plateau with the widest extent of Afroalpine habitat in the region. Within some of the relatively lower elevation populations in southern Kenya and northern Tanzania, we found less divergence, suggesting more recent gene flow between populations. The separation of these genotypes from those nearby on Mt. Kenya & Mt. Elgon is consistent with findings in Dendrosenecio in this region (Tusiime et al. 2020). Our study helps set the stage for future investigation of adaptive and phenotypic variation in the diverse populations of East Africa.
The sample collected by W.G. Schimper from ‘Demerki’ Ethiopia likely has a low elevation (< 3000 m) provenance. Sources have disputed the location of the historically important ‘Demerki’ specimens, as being Däräsge Maryam at 2990 m (Dorothea McEwan pers. comm.) or alternatively at 3500 m (Gillett 1972), and many have georeferenced it at the peak of the massif (4400 m asl), though the specimen itself does not indicate elevation. The location is of interest given the extensive collections (> 600 Schimper specimens labelled ‘Demerki’ in GBIF), including many types, made by Schimper in a time period from which few other specimens survive (Gillett 1972).
We also added a genome from a large Mediterranean island previously unstudied: Sardinia, which was a mix of Eurasian non‐relict and Iberian/Moroccan relict‐like ancestries. This relict ancestry is consistent with Sardinia being a refugium during glacial periods as recently indicated in our paleoclimatic projection of Arabidopsis distribution (Yim et al. 2023) and with previous findings that relict ancestry is greater in low elevations in the Mediterranean (Alonso‐Blanco et al. 2016). Thus, it is likely that with greater sampling additional diversity of relict ancestry will be found across the Mediterranean. Previous studies had included very few sequences of Norwegian genotypes; here, we show that they are a group of relatively similar genotypes, similar to others from Northern Europe including Sweden, Britain, and Germany.
4.2. Temporal Population Turnover
One of the most powerful benefits of sequencing museum specimens is to be able to obtain longitudinal samples of populations through time at multiple locations and populations. Some recent examples of major turnover in ancestry include ancient humans in Europe (Allentoft et al. 2024; LaPolice et al. 2024; Olalde et al. 2018), Centaurea plants under expansion of a polyploid lineage (Rosche et al. 2024), and domesticated pigs following their introduction into Europe (Frantz et al. 2019). Notably, these examples either can travel large distances under locomotion (mammals) or wind and animal attachment (Centaurea). Indeed, using modelling based on temporal autocorrelation in allele frequency change (Simon and Coop 2024) estimated that the great majority of human genetic turnover in European populations was attributable to gene flow, with some contribution from drift. In non‐relict Eurasian Arabidopsis, we found more modest but detectable turnover through a period of 100 years equivalent to that estimated to occur between populations 185 km apart at the same point in time. This magnitude may seem high given Arabidopsis is primarily self‐fertilising and with little mechanism of seed dispersal. However, there is water dispersal by some genotypes using mucilage (Saez‐Aguayo et al. 2014), and hitchhiking on humans, livestock, large mammals, and birds could play a role. Furthermore, individual Arabidopsis populations might show strong drift in landscapes where they colonise recently disturbed patches and potentially go extinct as succession proceeds (Baron et al. 2015; Lorts and Lasky 2020). Further work is required to understand processes contributing to population genomic turnover. Additionally, a weakness of museum specimens is that they were not specifically sampled for this type of study, and so the heterogeneity in sampling through time may limit our ability to detect population genetic changes. Each region showed distinct spatiotemporal gaps in sampling (Figure 4), potentially limiting our ability to accurately characterise allele frequency and population structure dynamics. Furthermore, the need to remove only small parts of tissue from specimens and consequent relatively intensive lab work limits the ability to scale up sample sizes.
4.3. Locus‐Specific Turnover in Allele Frequency
Outside of experimental evolution with microbes, there have been relatively few previous time‐series studies dissecting patterns of directional allele frequency change over many generations at specific loci across the genome (Akbari et al. 2024; Exposito‐Alonso, Vasseur, et al. 2018; Lang et al. 2024; Le et al. 2022; Mathieson et al. 2015). Our sequence data allowed us to test for evidence of non‐random patterns in allele frequency change. In general, we did not see much evidence for changes in the frequency of GWAS SNPs for traits such as flowering time, δ13C, and seed dormancy, known to be important to local environmental adaptation in Arabidopsis (and presumably under shifting selection with environmental change) (Dittberner et al. 2018; Gamba et al. 2024; Martínez‐Berdeja et al. 2020; Stinchcombe et al. 2004).
There may be multiple reasons we did not see more such evidence of adaptive temporal allele frequency shifts. GWAS appear to work well in many Arabidopsis traits (Alonso‐Blanco et al. 2016; Atwell et al. 2010; Baxter et al. 2010) so it seems likely the GWAS results used contained true QTL, although false positives and negatives may remain. Limited recombination in Arabidopsis may limit resolution to see temporal changes across the genome, but between many individual Arabidopsis populations, there are many past recombination events that limit LD and provide resolution for GWAS. Furthermore, whole genome predictions on flowering time at two temperatures did not show genome‐wide shifts in these traits. One plausible explanation may be that while traits of plants in nature have changed over time (DeLeo et al. 2020), the shifts in selection and genetic architecture of traits may be sufficiently heterogeneous among populations to limit our ability to see evidence of adaptation across regions and continents (Gamba et al. 2024; Lopez‐Arboleda et al. 2021). Finally, the method of looking at enrichment in GWAS SNPs for temporal allele frequency shifts may be of limited power. Our strategy for testing for adaptation at these loci is similar to that of (Akbari et al. 2024), although we do not rely on the determination of a significance threshold for calling individual loci as under selection. In Arabidopsis, (Lang et al. 2024) developed a polygenic score for individual stomatal genes to show shifts in allele frequency suggesting shifts to decreased stomatal density—a potential strategy to be implemented in the future for more traits.
We did identify the top flowering time GWAS SNPs in Iberia as enriched for shifts in allele frequency over time, potentially signifying changes in selection. Flowering time is a trait often under shifting selection among environments in many species (Ågren et al. 2017; Munguía‐Rosas et al. 2011) and has been identified as a trait showing temporal change following environmental events (Franks et al. 2007). However, it is hard to identify the specific change in selection pressures potentially acting in this case. While climate has changed in Iberia over this period (Corte‐Real et al. 1998; Esteban‐Parra et al. 1998), land use may also influence selection on flowering time in Arabidopsis. There has been dramatic land use change, such as the dramatic abandonment of farmland in the mountains of Spain over the 20th century, > 90% in some regions (Lasanta et al. 2017).
The loci showing the strongest allele frequency turnover identified several genes with known roles in environmental response (Table S3). For example, the second SNP with the most significant change in Eurasia was closest to plant U‐box E3 ligase 12 (PUB12) which plays a role in immunity and abscisic acid signalling (Kong et al. 2015; Yamaguchi et al. 2017). The top SNP in Germany was EXTRA LARGE G PROTEIN 3 (XLG3) which is involved in pathogen associated molecular pattern signalling (Wang et al. 2023). The number 5 SNP in Norway is in a cluster of SMALL AUXIN UP RNA (SAUR26/27/28) genes that regulate temperature responsive growth affected by known cis‐regulatory variants and with allele frequency clines along temperature gradients (Wang et al. 2019). These loci merit further investigation to determine the effects of this allelic variation.
4.4. Purifying and Background Selection and Temporal Shifts in Allele Frequency
We found that genic regions and conserved genes with longer amino acid sequences showed low temporal allele frequency change over time, potentially due to purifying selection and background selection on linked sites. The former pattern stands in contrast to the theoretical genome‐wide results of (Buffalo and Coop 2020) who found that background selection causes temporal autocorrelation in allele frequency change across the genome. Regardless of the genome‐wide pattern, in Arabidopsis, there are clearly differences among genomic contexts in their temporal dynamics. It is notable that genic SNPs are enriched in signals of local adaptation in Arabidopsis (Hancock et al. 2011; Lasky et al. 2012, 2018), opposite to what we found for temporal dynamics, perhaps because temporal allele frequency changes across the genome are dominated by background selection and not adaptation to changing environments.
One hypothesis to explain our finding is the following. Alleles at appreciable frequency for our analysis (i.e., MAF > 5%) in conserved genes are neutral; background selection limits their diversity within populations, but many of these neutral (e.g., synonymous) variants are fixed between populations. Over time, background selection limits change in the locally fixed alleles at these loci, but the allele frequency in our analysis (due to variation between populations) remains the same. Thus, there is low temporal allele frequency turnover in conserved genes. In less conserved (shorter) genes, variants of appreciable frequency are neutral or slightly deleterious (leading to consistent decrease in frequency as predicted by Buffalo and Coop 2020) or under positive selection, potentially due to environmental change (leading to consistent increase in frequency). Relatedly, (Cvijović et al. 2018) showed in an asexual model how background selection leads to distinct trajectories of neutral allele frequency depending on initial frequency, and so differences among loci in the site frequency spectrum can lead to distinct temporal trajectories. However, more theory is required to develop predictions for differences in allele frequency trajectories across genomes subject to spatially variable purifying, background, and positive selection. The fact that conserved Arabidopsis genes were depleted in temporal allele frequency changes suggests that Arabidopsis demographic and genome parameters may be in a space where background selection reduces temporal allele frequency change. Other species with different demography and genomes may show distinct patterns.
5. Conclusions
Natural history collections contain a vast wealth of samples that can generate insights into how organisms and populations are changing over time. However, in recent years, their survival has been threatened as institutions cut support. Our results highlight the continued vitality of these collections and potential benefits to directly revealing evolutionary change through time. Arabidopsis is changing as likely are all species, and future work will dissect ecological and evolutionary mechanisms driving this change.
Author Contributions
The study was conceived and designed by L.L. and J.R.L. L.L., P.L.M.L., A.H., M.Y., P.W., J.K., C.B., and J.R.L. collected data. L.L., P.L.M.L., S.M.L., Y.X., E.V.C., D.G., and J.R.L. analysed data. L.L. and J.R.L. led writing. All authors contributed to writing.
Conflicts of Interest
The authors declare no conflicts of interest.
Supporting information
Figures S1–S5: mec70081‐sup‐0001‐FiguresS1‐S5.docx.
Tables S1–S14: mec70081‐sup‐0002‐TablesS1‐S14.zip.
Acknowledgements
This research was made possible by assistance from several curators and museums, specifically Real Jardín Botánico, Kew Gardens, Komarov Botanical Garden, Oslo Museum of Natural History, Stuttgart State Museum of Natural History, and Herbarium Tubingense. Plant material was exported from Uganda with permission of The Ministry of Agriculture, Animal Industry and Fisheries' Plant Quarantine and Inspection Services; permit UQIS 4414/93/PC (E). Material was exported from Ethiopia with permission of the Ethiopian Biodiversity Institute, Ref. no. EBE71/7065/2018. Material was imported to the USA under USDA APHIS permits P37‐17‐01651 and P37‐18‐00230. Sequencing of Norwegian accessions was supported by NSF DEB‐1743273 to C.G.O. and J.K.M. We thank D. Weigel and the Max Planck Society for funding the sequencing of German herbarium specimens. L.L. is partially supported by California State University, San Bernardino, and by National Science Foundation award BIO‐BRC 2217793. Funding was provided by National Institutes of Health grant R35GM138300 to J.R.L.
Handling Editor: Jeremy B Yoder
Funding: This work was supported by National Institute of General Medical Sciences, R35GM138300.
Data Availability Statement
Genetic data: Individual genotype data are available on DataDryad (DOI: 10.5061/dryad.31zcrjdz1). Raw reads are available at NCBI SRA as project number PRJNA1269104. Sample metadata: Metadata can be found in Supporting Information of this manuscript. Code: Scripts are available on GitHub (https://github.com/jesserlasky/Arabidopsis_herbarium) and on DataDryad (DOI: 10.5061/dryad.31zcrjdz1).
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Associated Data
This section collects any data citations, data availability statements, or supplementary materials included in this article.
Supplementary Materials
Figures S1–S5: mec70081‐sup‐0001‐FiguresS1‐S5.docx.
Tables S1–S14: mec70081‐sup‐0002‐TablesS1‐S14.zip.
Data Availability Statement
Genetic data: Individual genotype data are available on DataDryad (DOI: 10.5061/dryad.31zcrjdz1). Raw reads are available at NCBI SRA as project number PRJNA1269104. Sample metadata: Metadata can be found in Supporting Information of this manuscript. Code: Scripts are available on GitHub (https://github.com/jesserlasky/Arabidopsis_herbarium) and on DataDryad (DOI: 10.5061/dryad.31zcrjdz1).
