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Article

Landscape Genomics and Climate Projections Reveal Genomic Offset and Provenance Vulnerability in Picea sitchensis

1
Forestry Development Department, Teagasc, Ashtown, D15KN3K Dublin, Ireland
2
Forestry Development Department, Teagasc, Athenry, H65R718 Galway, Ireland
3
DBN Plant Molecular Laboratory, National Botanic Gardens of Ireland, D09VY63 Dublin, Ireland
4
Botany, School of Natural Sciences, Trinity College Dublin, University of Dublin, D02PN40 Dublin, Ireland
5
Crops, Environment and Land Use Programme, Crop Science Department, Teagasc, Oak Park, R93XE12 Carlow, Ireland
*
Author to whom correspondence should be addressed.
Forests 2026, 17(7), 743; https://doi.org/10.3390/f17070743
Submission received: 2 June 2026 / Revised: 23 June 2026 / Accepted: 24 June 2026 / Published: 26 June 2026

Abstract

Sitka spruce (Picea sitchensis (Bong.) Carr.) is the dominant plantation conifer in Atlantic Europe, yet the genomic basis of provenance-level climate adaptation remains poorly resolved. We applied gradient forest analysis to 31,049 genome-wide SNPs from 1106 individual trees representing 79 native-range provenances in the IUFRO collection, using three environmental predictors retained after collinearity screening: Longitude, Temperature Seasonality, and Annual Precipitation. Longitude was the dominant driver of genomic turnover (mean R2 = 0.01168), followed by Temperature Seasonality (0.00672) and Annual Precipitation (0.00228), reflecting the long-distance coastal gradient of the native range. A redundancy analysis conditioned on ancestry principal components confirmed a significant multivariate genotype–environment association (F = 8.679, p = 0.001). Genomic offset was negatively correlated with all three provenance-level performance traits measured at the IUFRO common garden after 50 years of growth: height, stem diameter and stem quality, providing empirical validation of the genomic-climatic framework. Projecting the fitted model onto European planting sites using an 8-GCM CMIP6 ensemble showed mean offset increasing from 0.0021 (SSP2-4.5, 2041–2060) to 0.0041 (SSP5-8.5, 2061–2080), with the most climate-exposed cells under the high-emission late-century scenario approaching the upper tail of the source population offset distribution. The European planting region showed a higher projected offset than the North American source range under all scenarios. This supports the hypothesis that provenances from Oregon to southern British Columbia are most suited for planting in regions under future Atlantic European conditions.

1. Introduction

Sitka spruce (Picea sitchensis (Bong.) Carr.) occupies a unique position in Atlantic European forestry. It accounts for approximately 52% of the total forest area in Ireland, and in Britain, it is the single most planted conifer species, supporting timber industries in both regions worth hundreds of millions of euros annually [1,2]. The species was selected for Atlantic European planting in the early twentieth century because of its exceptional productivity under the cool, oceanic conditions that prevail across much of Ireland and Britain. At its best, Sitka spruce in Ireland can sustain mean annual volume increments exceeding 20 m3 ha−1 yr−1, making it among the most productive temperate conifers in the world outside its native range [3]. This productivity depends critically on a good match between provenance origin and planting environment. The interaction of these two elements is put under additional stress through the changing climate.
The challenge facing Sitka spruce management is fundamentally a temporal one. Trees planted today will not reach commercial maturity until the 2060s or 2080s, and the climatic conditions they will experience over their lifetimes are expected to diverge substantially from the current conditions. Modelled projections for Ireland and Britain under medium and high emission scenarios indicate warmer summers, more variable precipitation, and increased risk of late spring frost and summer drought stress; all conditions that could affect the suitability of provenances selected under historical climate guidelines [4]. Because forestry requires long-term planning and investment, provenance selection is effectively a long-term bet on future conditions. Getting that bet right requires a better mechanistic understanding of how genetic variation in Sitka spruce is structured along climatic gradients in the native range, and how that structure is connected to performance in European planting environments.
The native range of Sitka spruce extends for approximately 3000 km along the Pacific coast of North America, from Kodiak Island, Alaska (approximately 57° N) south to California (approximately 39° N) [5,6]. The distribution range is narrow, rarely exceeding 100 km inland, and is strongly oceanic throughout, reflecting its sensitivity to continentality and its dependence on the temperature-buffering influence of the Pacific. Despite this shared maritime character, the range spans an extraordinary latitudinal gradient in temperature, precipitation, and seasonality. In coastal Alaska, mean annual precipitation can exceed 3000 mm yr−1, mean January temperatures remain above freezing across much of the range, and temperature seasonality is low. Moving south through British Columbia, Washington, Oregon, and into California, the climate becomes progressively warmer and drier, the growing season lengthens, and temperature seasonality increases as the summer dry season becomes more pronounced [7]. Island populations, including those on Haida Gwaii, Kodiak Island, and Montague Island, experience particularly extreme maritime conditions and show distinctive patterns of genetic differentiation consistent with isolation and drift as well as possible environmental selection [6].
This range-wide gradient in climate has long been recognised as a key driver of genetically based differences between Sitka spruce provenances. Common garden studies conducted in Europe from the 1950s onwards documented substantial variation in growth rate, phenology, frost hardiness, and wood properties among provenances, with northern and island seed sources generally growing more slowly but exhibiting greater frost tolerance than southern or mainland sources [8,9]. These results supported a model in which Sitka spruce populations have differentiated along the native range climate gradient, with northern populations carrying alleles favouring survival under cold and short-season conditions and southern populations carrying alleles associated with faster growth and longer phenological activity. The mechanistic and genomic basis of this differentiation, however, has remained largely unexplored.
The International Union of Forestry Research Organisations (IUFRO) established a coordinated Sitka spruce provenance experiment using seed collected across the native range in 1968 and 1970 [10]. Material from 80 native-range provenances was established at common garden sites across Europe beginning in 1975, making this one of the longest-running and geographically broad conifer provenance experiments in existence. The Irish planting, at the John F. Kennedy Arboretum, Wexford (52.3° N, 6.9° W), represents a particularly valuable common garden because it has been maintained for over 50 years, allowing the full expression of provenance differences across most of the rotation. The Wexford site has a mean annual temperature of approximately 10 °C, annual precipitation of ca. 1050 mm, and a strong oceanic climate [11]; broadly comparable in character to the maritime regions of the native range, but warmer and drier than coastal Alaska and wetter than coastal California (Figure 1).
Genotyping-by-sequencing (GBS) data from the Irish IUFRO planting were reported in 2022 [10], and documented genome-wide genetic diversity and population structure across the collection. That study recovered the broad geographic signal expected from the native range and identified strong genetic distinctiveness of island populations, particularly Haida Gwaii. It also established NCBI BioProject PRJNA852515 as a public resource. The present study utilises data from that work, asking whether the genomic structure of the collection is shaped by climatic gradients and whether these genomic-climatic signals are predictive of performance in a European common garden experiment.
The integration of genome-wide marker data with environmental gradients offers a powerful approach to identifying the climatic drivers of genomic differentiation and to predicting the consequences of climate change for local adaptation [12,13]. Gradient forest (GF) is a nonlinear, machine-learning approach that models the relationship between allele frequency and environmental gradients across a set of loci, generating predictor importance scores that quantify which environmental variables are most associated with genomic turnover and a transformed environmental space in which similar genomic compositions cluster together [14,15]. Genomic offset (calculated as the Euclidean distance in GF-transformed environmental space between current and projected environments) has emerged as a useful summary statistic for quantifying the degree to which a population’s allele frequencies are mismatched to its environment, and has been applied across a range of tree species as an index of climate vulnerability [16,17].
One important limitation of using genomic offset is that it does not directly predict fitness; it is a relative measure of genomic-climatic distance that must be validated against empirical performance data to be ecologically interpretable. The IUFRO common garden at Wexford provides exactly this validation opportunity [18]. Because all 79 provenances were grown under identical site conditions for over 50 years, provenance-level differences in height, diameter, and stem quality reflect inherited genetic differences rather than site effects. Therefore, correlating genomic offset with these performance best linear unbiased estimators (BLUEs) provides a direct empirical test of whether the genomic-climatic framework captures biologically relevant variation in Sitka spruce.
This study uses the IUFRO Sitka spruce genomic resource, together with provenance-origin climate data and mature-tree performance BLUEs from the Wexford common garden, to test the following hypotheses:
  • Climatic gradients from the native range explain a significant component of genome-wide allele frequency variation, after accounting for population structure and geographic separation.
  • Temperature seasonality and annual precipitation are the most biologically meaningful climatic predictors of genomic turnover, reflecting the maritime specialisation of P. sitchensis.
  • Genomic differentiation is primarily polygenic, meaning that multi-locus summaries are more informative than individual candidate loci for describing climatic adaptation signals.
  • GF-derived genomic offset is negatively associated with provenance-level growth and quality performance at Wexford, providing empirical support for the biological relevance of the genomic climatic framework in this species.
These results are discussed in the context of climate adaptation and how they help inform planting decisions in regions under future Atlantic European conditions.

2. Materials and Methods

2.1. Study System and Common Garden Design

The population chosen, representing the native range of Picea sitchensis, was the IUFRO (International Union of Forest Research Organisation) collection [18]. Seed was collected in 1968 and 1970 from 80 provenances. The collection was planted in the John F Kennedy Arboretum in Wexford, Ireland (52.315° N, −6.941° W) in 1975. Planting was completed with 30 trees being planted per provenance. Thinning was performed in 2 operations at 20 and 25 years of age, and on average, approximately 40% of trees were removed. At the time of sample collection, there were 80 provenances in the common garden with 9–15 genotypes per provenance.

2.2. Genomic Data Processing and SNP Filtering

Genotyping-by-sequencing (GBS) data from 1177 genotypes of the IUFRO population, representing 80 provenance locations, were therefore obtained from previous work deposited in the NCBI BioProject PRJNA852515 [10]. These data were generated with 150bp paired-end GBS using Pst1-Apek1 as described in [19]. Sequences were aligned to the Q903-v1-1000 plus Picea sitchensis genome (GCA_010110895.2) [20] using BWA-mem v2.2 with default parameters [21]. Variant calling was completed using samtools v1.9 mpileup [22,23]. VCFtools was used for filtering [24].
For general analyses (structure, RDA, LFMM, variance partitioning, polygenic scoring, gradient forest), SNPs were filtered retaining biallelic sites only, removing indels, applying a minimum genotype quality of 20 and minimum sequencing depth of 5, retaining SNPs with no more than 20% missing data, removing individuals with more than 20% missing data, and retaining SNPs with minor allele frequency ≥ 0.05. This retained 1106 individuals and 31,049 SNPs.
Individual genotypes were then aggregated to provenance-level mean allele dosages to match the provenance-level resolution of environmental predictors, yielding 79 provenance observations after filtering.

2.3. Environmental Predictor Screening

Provenance climate variables were obtained for each collection locality from the WorldClim version 2 database [25]. Variables were screened for pairwise collinearity using Spearman correlation (threshold |r| ≥ 0.85) and variance inflation (VIF threshold 20). This reduced the predictor set to three representative variables: Annual Precipitation (representing the precipitation group), Temperature Seasonality (the standard deviation of monthly mean temperatures × 100, representing the temperature group), and Longitude (representing the primary geographic gradient along the native range) (Table 1, Figure S1).

2.4. Gradient Forest, Genomic Offset, and Genotype-Environment Association

GF was fitted using the ‘gradientForest’ R package v0.1-37 on provenance-level mean allele dosages across the 31,049 retained loci and the three selected environmental predictors [14]. Predictor importance was extracted as the mean R2 across all loci. Genomic offset was calculated as the Euclidean distance in GF-transformed environmental space between the observed provenance environment and a within-dataset shifted environment (shift = 0.5 SD of each predictor).
Genotype-environment association (GEA) was conducted using two complementary approaches. LFMM v2 (‘LEA’ package v1.4) was run per environmental predictor with a latent factor structure to control for population structure, using a q-value threshold of 0.10 to identify candidate SNPs [26]. Redundancy analysis (RDA, ‘vegan’ package v2.5) was applied as a multivariate GEA method, with partial models conditioned on ancestry principal components (PC1–PC3) as structure covariates [27]. Model significance was assessed by 999 permutations, and SNPs with absolute loading z-scores ≥ 3.0 were identified as candidates.

2.5. Trait BLUEs and Provenance-Level Performance

Provenance-level height, DBH, and quality BLUEs (representing stem straightness) were estimated from measurements taken at the Wexford IUFRO common garden using a mixed model of the form:
yij = μ + Provenancei + Blockj + εij
where provenance was treated as a fixed effect to obtain provenance level deviations from the site mean, and block accounted for the spatial layout of the trial. Individual BLUEs were then averaged to the provenance level and matched to genomic and environmental data by provenance identifier. Trait associations with environmental predictors, genomic PCA axes, candidate SNP dosages, GF axes, and genomic offset were assessed by linear regression (for continuous predictors) and Spearman correlation (for offset), with Benjamini–Hochberg q-values reported throughout [28].
Polygenic scores were computed by summing candidate SNP dosages across the union, consensus, and predictor-specific candidate sets. Piecewise structural equation modelling (‘piecewiseSEM’ package v 2.3.1) [29] was used as an exploratory path-consistency test to assess whether environment, genomic structure, multi-locus scores, and trait BLUEs formed a coherent directed graph. Isolation by distance (IBD) and isolation by environment (IBE) were assessed using generalised dissimilarity modelling (‘gdm’ package v1.6) [30].

2.6. CMIP6 Genomic Offset Projections

To extend the genomic offset analysis beyond the within-dataset synthetic shift, we projected the fitted GF model onto (i) a regular grid of European land cells representing the Atlantic European planting region and (ii) the North American coastal range of Sitka spruce, using CMIP6 future climate data as the environmental target. The current baseline climate was obtained from WorldClim v2 at 10 arc-min resolution. Future climate was derived from an ensemble of eight CMIP6 General Circulation Models under four scenarios × time-period combinations: SSP2-4.5 and SSP5-8.5 at 2041–2060 and 2061–2080 (ACCESS-CM2, BCC-CSM2-MR, CMCC-ESM2, EC-Earth3-Veg-LR, INM-CM5-0, IPSL-CM6A-LR, MIROC6, MPI-ESM1-2-HR) [25]. SSP2-4.5 represents a moderate-emissions pathway with some climate mitigation, whereas SSP5-8.5 represents a very high-emissions, fossil-fuel-intensive pathway with substantially greater projected warming. Ensemble mean future values were computed as the unweighted mean across all available GCMs.
The European grid spanned −15° to 35° longitude and 35° to 72° latitude (31,668 land cells at 10 arc-min). The North American grid spanned −160° to −110° longitude and 38° to 62° latitude (19,062 land cells), covering the full coastal range from northern California to the Gulf of Alaska. For each grid cell, within-site genomic offset was calculated as the Euclidean distance in GF-transformed space between the current and future environments at that cell. The GF model uses three predictors: Annual Precipitation, Temperature Seasonality, and Longitude. For within-site offset, longitude is identical in current and future environments at each cell and therefore contributes exactly zero to the Euclidean distance, so offset is driven entirely by changes in the two climate variables.

3. Results

3.1. The IUFRO Collection Spans the Full Climatic Breadth of the Sitka Spruce Range

The 80 provenances in the IUFRO collection represent the full climatic and geographic range of Sitka spruce, from the maritime islands of the Gulf of Alaska in the north to the transitional Mediterranean-maritime boundary in northern California in the south. Annual precipitation at provenance origin ranges from around 700 mm yr−1 in the driest southern California localities to over 4000 mm yr−1 in the wettest Alaskan coastal sites. Temperature seasonality spans from below 400 in the most oceanic Alaskan island locations to above 800 in more continental interior British Columbia [7]. These gradients translate into fundamentally different ecological contexts for Sitka spruce growth: northern island provenances experience short growing seasons, perennial cloud cover, and very little summer drought risk, whereas southern mainland provenances encounter longer growing seasons, warmer and drier summers, and greater interannual climate variability. The Wexford IUFRO common garden, with its cool maritime climate, sits climatically between the most maritime Alaskan conditions and the warmer, more seasonal southern portion of the range.
After strict genotype filtering, the analysis retained 1106 of the 1177 sampled individuals and 31,049 SNPs, aggregated to 79 provenance-level observations. A sensitivity analysis using a relaxed SNP missingness threshold (≤30%) retained 36,523 SNPs and produced nearly identical predictor importance rankings (Pearson r > 0.99 between branches; supplement), confirming that the results are robust to the choice of missingness threshold. The strict filters were, however, used in all subsequent analyses for consistency.

3.2. Genomic Turnover Across the Native Range Reflects Its Long Coastal Gradient

Gradient forest analysis across the 79 retained provenances identified Longitude as the strongest predictor of genomic turnover (mean R2 importance = 0.01168), with Temperature Seasonality second (0.00672) and Annual Precipitation third (0.00228) (Figure 2). The dominance of longitude reflects the fundamental structure of the Sitka spruce range: a long, narrow coastal strip in which geography, post-glacial history, and climate are tightly correlated along the north–south axis. The GF-transformed ordination separated Alaskan and island provenances strongly from Oregon and California populations, with British Columbian provenances distributed across an intermediate zone.
Although Longitude captured the largest share of genomic turnover, this result does not straightforwardly contradict Hypothesis 2. Longitude in this system functions as a composite proxy for the full suite of geographic, demographic, and historical processes that differentiate Alaskan from Californian provenances, including post-glacial recolonisation history, island isolation by marine barriers, and the northwest-to-southeast orientation of the native range coastline, rather than a purely geographic signal. Critically, Longitude also best resolves the island–mainland contrast: the major archipelago populations (Haida Gwaii, Kodiak, and Montague Island) lie substantially further west than adjacent mainland provenances at similar latitudes, and because these island populations are among the most genomically distinct in the IUFRO collection, a predictor that separates them from mainland sources accumulates disproportionately high GF importance. In this context, Longitude’s dominance reflects dataset geometry and demographic history as much as it does the primacy of geographic isolation over climate as a driver of adaptation. Temperature, Seasonality and Annual Precipitation each contributed independently after controlling for geography. This is biologically coherent: Sitka spruce is a maritime specialist, and the within-range gradient from hypermaritime Alaska to more seasonally variable Oregon and California represents genuine differentiation in the climatic conditions experienced across the species lifespan. Variance partitioning confirmed that population structure and longitude together explained the largest share of genome-wide variance (adjusted R2 ≈ 3.08% for structure alone after conditioning on environment and longitude), with climate variables explaining a smaller but testable independent fraction (adjusted R2 ≈ 0.20% for environment after conditioning on geography and structure). While these fractions are modest in absolute terms, they are consistent with expectations for a landscape genomic study of a large genome outcrossing conifer: adaptive differentiation at any single locus is subtle, and the total adaptive signal is distributed across tens of thousands of sites [31,32].

3.3. Climate Gradients Explain a Significant Multivariate Component of Allele Frequencies

Redundancy analysis conditioned on ancestry principal components (PC1–PC3) identified a significant multivariate association between allele frequencies and the selected environmental predictors (F = 8.679, p = 0.001, 999 permutations). The RDA biplot showed provenance ordination broadly consistent with the GF turnover pattern: Alaskan and island provenances separated from Oregon and California populations along axes reflecting temperature seasonality and precipitation. Both RDA axes were individually significant (p = 0.001), indicating that the climate-genome relationship is expressed along more than one dimension of allele-frequency variation (Figure 3).
LFMM identified 140 SNP-predictor associations at q ≤ 0.10 across the three environmental predictors, while RDA identified 469 SNPs with extreme loading z-scores (|z| ≥ 3.0). Together, these methods recovered 608 unique environment-associated candidate SNPs. However, only one SNP (Ps-1r180608s00050901:55515_A) was detected by both LFMM and RDA. This low cross-method overlap is a biologically expected result. Local climate adaptation in outcrossing conifers with very large genomes (the Sitka spruce genome is approximately 20 Gb) is believed to be primarily polygenic, with many loci of individually small effect distributed across the genome [33]. GBS datasets, which sample a small fraction of the genome at low and uneven coverage, are poorly powered to recover the same adaptive loci across different analytical frameworks [19,34]. The single consensus SNP and the broader candidate set should therefore be treated as hypothesis-generating resources for future targeted genotyping or functional study, not as a validated list of adaptive variants.

3.4. High-Latitude and Island Provenances Show the Greatest Genomic-Climatic Displacement

GF-derived genomic offset, calculated as the Euclidean distance in transformed environmental space between each provenance’s current environment and a within-dataset shifted environment, showed a clear geographic pattern across the 79 provenances (mean offset = 0.00889; range 0.00659 to 0.01288) (Figure S2). The highest offset values were concentrated in the northernmost and most island-associated regions of the native range (Table 2). Kodiak Island had the highest mean offset (0.01175), followed by Montague Island (0.01161) and North Alaska (0.01062). These are among the most climatically extreme locations in the native range: Kodiak Island receives over 1500 mm of rainfall annually, has mean January temperatures only slightly below freezing, and experiences temperature seasonality that is among the lowest in the entire range. The allele frequencies of trees from these locations reflect selection history under these conditions, placing them furthest from the centre of the genomic-climatic space defined by the full collection.
The lowest offset values were found in Oregon and California provenances. Central Oregon (mean offset = 0.00669), North Oregon (0.00683), and California (0.00715) provenances are climatically closer to the centroid of the fitted genomic-climatic space, likely because the more temperate, seasonally variable conditions of the southern range are less extreme along the axes that drive turnover. These provenances cluster more closely in GF-transformed space, reflecting the lower rate of allele frequency change along the temperature and precipitation gradients in the southern portion of the range.
The pattern of genomic offset across regions echoes the classical provenance trial literature: island and northern mainland sources have long been observed to grow more slowly in European common gardens than southern mainland sources, while showing superior frost tolerance. The genomic offset analysis provides a genome-wide, multivariate basis for understanding provincial offset, as these provenances carry allele frequency distributions that reflect their adaptation to a very different climatic context than Atlantic Europe, or indeed the southern part of the native range.

3.5. Genomic-Climatic Mismatch Predicts Provenance Performance in Common Garden Experiment

The most direct test of the biological relevance of genomic offset came from its correlation with provenance-level performance BLUEs measured at the Wexford common garden after over 50 years of growth (Table 3). Genomic offset was negatively correlated with all three measured traits. The strongest association was with height BLUE (Spearman ρ = −0.659, q ≈ 0), meaning that provenances with the greatest genomic-climatic displacement tended to produce the shortest trees. DBH BLUE showed a comparable association (ρ = −0.449, q = 7.73 × 10−5), and stem quality BLUE, though weakly associated, was also significantly negatively correlated with offset (ρ = −0.348, q = 0.002). Translated into ecologically concrete terms: the provenances that are most genomically “out of place”, such as those from Kodiak Island, Montague Island, and North Alaska, are also, on average, the slowest growing and lowest quality at the Wexford common garden. Conversely, Oregon and California provenances, which show the lowest genomic offset, tend toward better performance on the growth metrics. This pattern is consistent with the expectation that genomic composition, shaped by natural selection along native-range climate gradients, predicts the degree of climatic misfit at a planting site, and that this misfit is associated with measurable growth penalties.

3.6. Polygenic Multilocus Scores Outperform Individual Candidate SNPs in Trait Prediction

Multi-locus polygenic scores, calculated by aggregating candidate SNP dosages across the full union candidate set, were strongly associated with both environmental gradients and performance traits. The union score was most strongly predicted by longitude (R2 = 0.777, q = 6.41 × 10−26), confirming that the aggregate genomic composition of provenances is tightly coupled to their position along the range-wide geographic-climatic gradient. Polygenic scores were also significantly associated with DBH BLUE (R2 = 0.540, q = 2.83 × 10−13) and height BLUE (R2 = 0.518, q = 2.85 × 10−13), associations substantially stronger than those of any individual candidate SNP.
The contrast between the cross-method candidate overlaps (one shared SNP) and the strong multi-locus associations reinforces a polygenic interpretation. Each individual SNP captures only a tiny fraction of the allele-frequency variation that is structured along climate gradients, and the analytical power to recover the same loci across methods is correspondingly low. But when hundreds of such loci are aggregated into a score, the noise cancels, and the signals emerge clearly. Polygenic score analyses using random SNP sets of matched size showed that candidate-based scores consistently outperformed random sets, although the difference was modest, as is typical when a large fraction of the genome is weakly but consistently differentiated along range-wide gradients. Exploratory piecewise structural equation models, fitted to test whether environment, genomic composition, and provenance performance form a coherent indirect-effect path, explained 89.8%, 71.6%, and 40.9% of the variance in height, DBH, and quality BLUEs, respectively. However, the direct path coefficient from adaptive genomic score to trait was not consistently large once environmental and structure covariates were included, indicating that much of the trait-genome association is mediated through shared geographic and climatic gradients rather than through a clean causal genomic pathway. This result is expected given the observational design and the polygenic nature of the traits.

3.7. CMIP6 Genomic Offset Projections for the European Planting Region and the North American Source Range

Projecting the fitted GF model onto the European planting region under the CMIP6 ensemble climate produced genomic offset estimates that were consistent across scenarios and ecologically interpretable relative to the within-dataset baseline. Under the moderate scenario SSP2-4.5 at mid-century (2041–2060), the mean European offset was 0.00211 (max 0.00817), rising to 0.00274 (max 0.00915) by 2061–2080 (Figure 4; Table 4). Under the high-emission scenario SSP5-8.5, the mean offset reached 0.00308 at 2041–2060 and 0.00409 (max 0.01236) by 2061–2080. All four scenarios produced a consistent geographic pattern, with higher offsets in continental and southern European grid cells and lower offsets in Atlantic coastal regions and central/eastern European grid cells, reflecting the strong oceanicity gradient in projected temperature seasonality change.
The North American source range showed a broadly similar but uniformly lower offset across all scenarios (Figure 5). Under SSP2-4.5 2041–2060, the mean NA offset was 0.0019 (max 0.0068); under SSP5-8.5 2061–2080, it reached 0.0035 (max 0.0110). In every scenario, the European planting region had a higher mean offset than the North American source range, indicating that the European grid experiences greater projected climate-driven genomic mismatch than the populations from which the GF model was trained.
Expressed relative to the within-dataset baseline (mean 0.00889, range 0.00659–0.01288), the European CMIP6 offsets represent 24% of the baseline mean under SSP2-4.5 mid-century and 46% under SSP5-8.5 late-century. Critically, the maximum European offset under SSP5-8.5 2061–2080 (0.0124) approaches the upper tail of the source population offset distribution (maximum 0.01288), meaning that the most climate-exposed European planting cells under the worst-case scenario are projected to lie at the outer edge of the genomic-climatic variation characterised by the Sitka spruce source collection.
Climate delta maps showed that the primary driver of increased offset across Europe was rising temperature seasonality (mean increase under SSP5-8.5 2061–2080 of approximately 50–100 °C × 100 units across much of the continent), rather than precipitation change, which was more spatially heterogeneous, and in some Atlantic regions showed modest increases rather than decreases. This pattern is consistent with the GF model, placing the highest importance on Temperature Seasonality as a climate predictor of genomic turnover in the native range. Under moderate GCM scenarios, European sites remain within the climate space represented by southern source populations, suggesting that provenances from Oregon, Washington, and southern British Columbia are climatically matched to near-future European conditions.

4. Discussion

4.1. A Polygenic Genomic-Climatic Signal Along the Sitka Spruce Range Gradient

The central finding of this study is that genomic variation across the IUFRO Sitka spruce provenance collection is structured along the climatic and geographic gradients of the native range, and that the degree of a provenance’s genomic-climatic displacement predicts its growth performance in a European common garden (Wexford). This is not a simple correlation between geographic distance and performance; it reflects a multivariate genomic signal, embedded in tens of thousands of loci, that is coherently aligned with the temperature, precipitation, and geographic gradients that shape the native range. The dominance of longitude in the GF analysis should be interpreted carefully and correctly. It does not mean that longitude drives genomic differentiation. Rather, longitude in this dataset is a proxy for the full complex of ecological, demographic, and historical processes that differentiate Alaskan populations from Californian ones. These include post-glacial recolonisation history (Sitka spruce recolonised northward from glacial refugia south of the ice sheets, generating a gradient of ancestry from south to north), isolation of island populations by marine barriers, the longitudinal gradient in climate, and potentially historical differences in disturbance regime and competitive environment [5,6,9,10]. A gradient forest cannot distinguish between these mechanisms. What it establishes is that allele frequencies change nonlinearly and systematically along this gradient and that the pattern is not solely an artefact of demographic history; Temperature, Seasonality and Annual Precipitation contribute independently to turnover after accounting for longitude. The emergence of longitude rather than latitude can be explained by two features of the Sitka spruce range. First, the native range follows a coastline that runs northwest to southeast: from the Gulf of Alaska through Haida Gwaii and coastal British Columbia to Oregon and northern California. Because the coast curves progressively eastward as it runs south, latitude and longitude are highly collinear along the range transect, and both variables were placed in the same geographic predictor group during collinearity screening. Only one representative was retained for GF fitting. Second, and critically, longitude better captures the distinctiveness of the archipelago populations than latitude does. The major island groups (Haida Gwaii, Kodiak Island and Montague Island) lie substantially further west than the adjacent mainland coast at similar latitudes. Latitude would position Haida Gwaii provenances close to nearby BC mainland provenances at comparable degrees north, whereas longitude separates them clearly. Because island populations are among the most genomically distinct groups in the IUFRO collection, a predictor that resolves island–mainland contrasts will accumulate higher GF importance than one that does not.
Temperature Seasonality is, mechanistically, the most compelling climatic predictor in this analysis. Sitka spruce is a textbook maritime specialist: it cannot tolerate the temperature extremes of continental climates, and its growth and survival are tightly linked to the narrow, year-round thermal window of oceanic conditions. The gradient from maritime Alaska (low seasonality, buffered temperatures) to more seasonally variable Oregon and California is directly relevant to physiological traits, including cold hardiness, bud phenology, and drought avoidance. Genetic variation in bud set timing, which determines both frost risk and growing season length, has been shown to be strongly differentiated among Sitka spruce provenances and to respond to temperature gradients in the native range [35]. The allele-frequency gradients captured here along the Temperature Seasonality axis are likely to include many loci involved in these phenological responses, even if individual loci cannot be resolved with confidence at current SNP marker density.

4.2. Alaskan and Island Provenances Underperform in Irish Common Garden Experiment

The negative correlation between genomic offset and provenance-level performance at the Wexford common garden is consistent with a straightforward ecological interpretation. The highest-offset provenances (Kodiak Island, Montague Island, and North Alaska) originate from environments that are climatically more extreme and more different from Wexford than any other part of the native range. Kodiak Island, for example, has an annual precipitation over three times that of Wexford, a mean summer temperature several degrees lower, and a growing season substantially shorter. Trees from Kodiak carry allele frequencies reflecting generations of selection for survival and reproduction under these conditions: early bud set to avoid autumn frost, conserved phenology tuned to a short growing season, and high carbon allocation to frost protection. At Wexford, with its warmer, longer growing season and more moderate summer climate, these traits are mismatched to the local environment. Early bud set means a shorter effective growing season. Conservative phenology means less exploitation of the relatively mild Irish autumn. The result is lower annual height and diameter increment, expressed consistently over the 50+ year period of the trial. This pattern aligns precisely with what has long been known empirically from Sitka spruce provenance trials across Atlantic Europe: the “Queen Charlotte Sound” and southern Alaskan provenances recommended for Irish and British planting are precisely those from the intermediate-offset zone in our analysis.
The quality BLUE correlation, while weaker (ρ = −0.348), adds a further dimension. Quality in conifers is related to wood density, branch characteristics, and stem form, traits that are under some genetic control [36] and that also differ systematically among Sitka spruce provenances. Island provenances have long been noted for heavier branching and more variable stem form under European plantation conditions [3], which may partly explain the quality offset signal.

4.3. Polygenic Adaptation and the Limits of Single-Locus Approaches

The near-complete lack of overlap between LFMM and RDA candidate SNPs (one shared locus from 608 unique candidates) (Supplementary Table S1) is one of the clearest biological messages of this study. In a large genome, outcrossing conifer with an approximately 20 Gb genome, climatic adaptation is not expected to involve a small number of large-effect loci. Comparative studies of climate adaptation in Picea, Pinus, Pseudotsuga, and related genera have consistently found that adaptive differentiation is polygenic, with many hundreds or thousands of loci each contributing a tiny fraction of the total variance in adaptive traits [33,37]. The GBS approach samples approximately 0.1% of the Sitka spruce genome at low and uneven coverage. Given this sparse sampling, the power to detect the same small-effect adaptive locus by two methods independently, at the q ≤ 0.10 threshold used here, is very low. Low overlap is therefore not evidence of a failed analysis; it is evidence of the expected biology.
The practical implication is that single-locus approaches are unlikely to generate reliable provenance recommendations for Sitka spruce in the near term. The polygenic score results support this conclusion from the positive direction: when many candidate loci are aggregated, the signal becomes robust (R2 up to 0.78 for score versus longitude; R2 up to 0.54 for score versus DBH BLUE) and biologically coherent (Figure 6). Future studies with denser marker panels, for example, using the emerging Sitka spruce reference genome and targeted sequence capture, may be able to resolve individual adaptive loci more reliably. Until then, multi-locus genomic summaries and GF-derived offset provide the most appropriate tools for characterising and comparing provenance-level genomic-climatic profiles.

4.4. Significance of Results for Sitka Spruce Management in a Changing Climate

The results of this study are relevant to two interrelated management questions: (1) which provenances are best suited to current Atlantic European planting conditions? and (2) how might that suitability shift as the climate changes? The CMIP6 offset projections now allow both questions to be addressed with external future climate data rather than a synthetic within-dataset shift.
For current conditions, the genomic offset analysis confirms that the provenance groups currently recommended for Irish and British planting occupy an intermediate genomic offset zone in the IUFRO collection, neither the extreme Alaskan island provenances nor the driest California sources. This is consistent with their documented performance in European trials and with provenance guidance [1,2]. The CMIP6 projections directly address the prospective management question. Under SSP2-4.5 at mid-century (2041–2060), the mean European planting-site offset (0.00211) is approximately 24% of the mean within-source-range offset, well within the variation already represented among source populations. This is reassuring for near-term planting decisions based on current provenance recommendations: moderate warming over the next 35 years does not project European sites outside the climate envelope characterised by the GF model. Under SSP5-8.5 by 2061–2080, however, mean offset rises to 0.00409, and the most climate-exposed European cells approach the upper tail of the source population distribution (max European offset 0.01236 versus source range max 0.01288). Under this scenario, some European planting environments may be moving into a climate space that is poorly represented by any currently characterised Sitka spruce source population.
Importantly, the North American source range itself shows a lower projected offset than the European planting region under all scenarios (NA SSP5-8.5 2061–2080 mean 0.0035 versus European 0.0041) (Figure 5). This asymmetry reflects the greater projected increase in temperature seasonality across continental Europe relative to the already-maritime North American coastal range. In practical terms, it means that the European planting environment is expected to diverge more from current Sitka spruce genomic-climatic norms than the source populations themselves, amplifying the urgency of provenance diversification for higher-emission trajectories.
The climate space analysis (Figure 4) shows that the near-future European environment (SSP2-4.5 2041–2060) broadly overlaps with the current climate of Oregon, Washington, and southern British Columbia source populations, precisely the provenances that already show the lowest within-dataset offset and the strongest performance in the Wexford common garden. This convergence supports a clear and actionable provenance hypothesis: provenances from the Oregon–southern BC corridor, which originate from environments with higher temperature seasonality and lower annual precipitation than currently recommended northern sources, may already carry allele frequencies relevant to projected future Atlantic European conditions. Targeted assisted gene flow trials incorporating these provenances would provide a direct empirical test of this hypothesis [38].

4.5. Limitations and Future Directions

Several important limitations constrain the inferences that can be drawn from this study. First, the BLUE–offset correlations are based on a single common garden site. Wexford is an extremely valuable resource, but replication across multiple European planting environments would strengthen the generality of the findings and permit identification of genotype–environment interactions that a single site cannot reveal [39].
Second, the GF model was trained on provenances spanning only the North American coastal range, and the CMIP6 offset projections for the European planting region involve geographic extrapolation. Longitude, the strongest GF predictor, is far outside its training range for European grid cells. However, because within-site genomic offset compares current and future climate at the same cell, longitude is identical in both environments and contributes exactly zero to the Euclidean distance. The European projections are therefore driven entirely by changes in Temperature Seasonality and Annual Precipitation and are not contaminated by longitude extrapolation. The offset magnitudes should nonetheless be read relative to the source range baseline (mean 0.00889) rather than as standalone predictions of adaptation deficit.
Finally, the common garden material is now over 50 years old. Regeneration of the experiment from seed, incorporating advances in both genomics and climate projection, would provide an invaluable resource for the next generation of provenance research in Sitka spruce.

5. Conclusions

This study provides the first landscape genomic analysis of the IUFRO Sitka spruce provenance collection, integrating genome-wide allele frequency data with native-range climate gradients and provenance-level common garden performance. The results show that Sitka spruce provenances are genomically differentiated along with the temperature seasonality and precipitation gradients of the native range, that this differentiation is primarily polygenic, and that GF-derived genomic offset is negatively associated with growth and quality performance at the Wexford common garden. Island and high-latitude provenances show the greatest genomic-climatic displacement and the poorest performance, while Oregon and California provenances show the lowest displacement. These patterns are consistent with known trial results and with the ecology of a maritime species whose range spans a 3000 km climatic gradient.
The practical contribution of this work is not to replace the established provenance trial evidence base (decades of careful field experiments remain the gold standard for provenance recommendation) but to provide a genomic and mechanistic context for interpreting provenance performance differences and for generating hypotheses about how provenance suitability may shift as Atlantic European climates change. By combining strict genotype filtering, structure-aware landscape genomics, and long-term common garden data, this study establishes a framework for integrating molecular resources with applied forestry decisions in Picea sitchensis and, more broadly, in other conifers for which similar provenance and genomic resources exist.

Supplementary Materials

The following supporting information can be downloaded at: https://www.mdpi.com/article/10.3390/f17070743/s1. Figure S1: Environmental predictor correlation heatmap, Figure S2: Genomic offset by major population; Table S1: LFMM and RDA SNPs.

Author Contributions

Conceptualisation, N.F., T.R.H., C.T.K. and S.B.; methodology, N.F., T.R.H., S.B., C.T.K. and T.B.; validation, T.R.H., N.F., C.T.K. and S.B.; formal analysis, T.B.; data curation, T.B.; writing—original draft preparation, T.B.; writing—review and editing, T.B., T.R.H., N.F., C.T.K. and S.B.; visualisation, T.B.; funding acquisition, T.R.H., N.F., C.T.K. and S.B. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by the Department of Agriculture, Food and the Marine under grant award 17/C/297.

Data Availability Statement

Genomic data were obtained from NCBI BioProject PRJNA852515. Phenotypic data are available upon request. Detailed code can be found at: https://github.com/ByrneTforestry/sitka-spruce-landscape-genomic/blob/main/README_methods_condensed.md (accessed on 1 June 2025).

Acknowledgments

The authors would like to thank the staff at the JFK Arboretum for access to the forest.

Conflicts of Interest

The authors declare no conflicts of interest.

Abbreviations

The following abbreviations are used in this manuscript:
BCBritish Columbia
BLUEBest Linear Unbiased Estimator
BWABurrows-Wheeler Aligner
CMIP6Coupled Model Intercomparison Project Phase 6
DBHDiameter at Breast Height
GBSGenotyping-by-sequencing
GCMGeneral Circulation Model
GDMGeneralised Dissimilarity Modelling
GEAGenotype-environment association
GFGradient Forest
IBDIsolation by Distance
IBEIsolation by Environment
IUFROInternational Union of Forestry Research Organisations
LFMMLatent Factor Mixed Model
MAFMinor Allele Frequency
NCBINational Centre for Biotechnology Information
PCPrincipal Component
RDARedundancy Analysis
SDStandard Deviation
SEMStructural Equation Model
SNPSingle Nucleotide Polymorphism
SSPShared Socioeconomic Pathway
VIFVariance Inflation Factor

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Figure 1. Geographic distribution of the IUFRO Sitka spruce provenance collection. Map of the North American Pacific coast showing the 80 collection localities used in the IUFRO Sitka spruce provenance experiment. Points are coloured by major population grouping (Alaska mainland, British Columbia, Oregon and California. Approximate latitudinal extent of the native range is 3000 km from Kodiak Island (~57° N) to Mendocino County, California (~39° N).
Figure 1. Geographic distribution of the IUFRO Sitka spruce provenance collection. Map of the North American Pacific coast showing the 80 collection localities used in the IUFRO Sitka spruce provenance experiment. Points are coloured by major population grouping (Alaska mainland, British Columbia, Oregon and California. Approximate latitudinal extent of the native range is 3000 km from Kodiak Island (~57° N) to Mendocino County, California (~39° N).
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Figure 2. Gradient forest predictor importance and cumulative importance curves. Mean R2 importance of the three retained environmental predictors (Longitude, Temperature Seasonality, Annual Precipitation). Values represent the weighted mean improvement in prediction attributable to each predictor.
Figure 2. Gradient forest predictor importance and cumulative importance curves. Mean R2 importance of the three retained environmental predictors (Longitude, Temperature Seasonality, Annual Precipitation). Values represent the weighted mean improvement in prediction attributable to each predictor.
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Figure 3. Redundancy analysis biplot of environment-associated allele frequency variation. Partial RDA biplot from the model conditioned on ancestry principal components (PC1–PC3 as covariates), retaining only the component of allele frequency variation associated with the three environmental predictors.
Figure 3. Redundancy analysis biplot of environment-associated allele frequency variation. Partial RDA biplot from the model conditioned on ancestry principal components (PC1–PC3 as covariates), retaining only the component of allele frequency variation associated with the three environmental predictors.
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Figure 4. Genomic offset projections for the European planting region under SSP climate predictions. Four-panel map of the European planting region showing within-site genomic offset between current (WorldClim v2 baseline) and future (8-GCM CMIP6 ensemble mean) under four scenario × time-period combinations: SSP2-4.5 2041–2060 (top left), SSP2-4.5 2061–2080 (top right), SSP5-8.5 2041–2060 (bottom left), SSP5-8.5 2061–2080 (bottom right). The shared colour scale runs from dark purple (offset ≈ 0) through red to bright yellow (offset ≥ 0.008).
Figure 4. Genomic offset projections for the European planting region under SSP climate predictions. Four-panel map of the European planting region showing within-site genomic offset between current (WorldClim v2 baseline) and future (8-GCM CMIP6 ensemble mean) under four scenario × time-period combinations: SSP2-4.5 2041–2060 (top left), SSP2-4.5 2061–2080 (top right), SSP5-8.5 2041–2060 (bottom left), SSP5-8.5 2061–2080 (bottom right). The shared colour scale runs from dark purple (offset ≈ 0) through red to bright yellow (offset ≥ 0.008).
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Figure 5. Genomic offset across native-range provenances under SSP climate prediction. Map of the North American native range showing provenance-level genomic offset (within-dataset shift of 0.5 SD per predictor) as a colour gradient from low (blue) to high (yellow) under four scenario × time-period combinations: SSP2-4.5 2041–2060 (top left), SSP2-4.5 2061–2080 (top right), SSP5-8.5 2041–2060 (bottom left), SSP5-8.5 2061–2080 (bottom right). Island populations are indicated with outlined symbols.
Figure 5. Genomic offset across native-range provenances under SSP climate prediction. Map of the North American native range showing provenance-level genomic offset (within-dataset shift of 0.5 SD per predictor) as a colour gradient from low (blue) to high (yellow) under four scenario × time-period combinations: SSP2-4.5 2041–2060 (top left), SSP2-4.5 2061–2080 (top right), SSP5-8.5 2041–2060 (bottom left), SSP5-8.5 2061–2080 (bottom right). Island populations are indicated with outlined symbols.
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Figure 6. Trait-specific standardised path coefficients from piecewise structural equation models. Horizontal bar charts showing standardised path coefficients in each trait-specific piecewise SEM: (i) the equation predicting the adaptive genomic score from environmental principal components (envPC1–3) and ancestry principal components (PC1–3), shown in red; and (ii) the equation predicting each trait BLUE from the adaptive genomic score, envPC1–3, and PC1–3, shown in the trait-specific colour (green: DBH BLUE; teal: height BLUE; purple: quality BLUE). Each panel corresponds to one trait response ((left): DBH BLUE; (centre): height BLUE; (right): quality BLUE). Bar length is proportional to the absolute standardised coefficient; bars extending left indicate negative effects and bars extending right indicate positive effects. The x-axis is fixed at ±0.6 across all panels for comparability. Environmental PC1 (envPC1) was the strongest predictor of the adaptive genomic score across all trait models, with a consistently large negative coefficient, indicating that provenances at the high-envPC1 end of the gradient carry lower adaptive genomic scores. The direct path from adaptive genomic score to each trait BLUE (bottom row in each panel) was small relative to the indirect effects mediated through environmental and structure covariates, indicating that most of the trait–genome association is captured through shared environmental and demographic gradients rather than a direct causal genomic pathway.
Figure 6. Trait-specific standardised path coefficients from piecewise structural equation models. Horizontal bar charts showing standardised path coefficients in each trait-specific piecewise SEM: (i) the equation predicting the adaptive genomic score from environmental principal components (envPC1–3) and ancestry principal components (PC1–3), shown in red; and (ii) the equation predicting each trait BLUE from the adaptive genomic score, envPC1–3, and PC1–3, shown in the trait-specific colour (green: DBH BLUE; teal: height BLUE; purple: quality BLUE). Each panel corresponds to one trait response ((left): DBH BLUE; (centre): height BLUE; (right): quality BLUE). Bar length is proportional to the absolute standardised coefficient; bars extending left indicate negative effects and bars extending right indicate positive effects. The x-axis is fixed at ±0.6 across all panels for comparability. Environmental PC1 (envPC1) was the strongest predictor of the adaptive genomic score across all trait models, with a consistently large negative coefficient, indicating that provenances at the high-envPC1 end of the gradient carry lower adaptive genomic scores. The direct path from adaptive genomic score to each trait BLUE (bottom row in each panel) was small relative to the indirect effects mediated through environmental and structure covariates, indicating that most of the trait–genome association is captured through shared environmental and demographic gradients rather than a direct causal genomic pathway.
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Table 1. Selected environmental predictors. Variables were drawn from WorldClim v2 bioclimatic layers and provenance geographic coordinates. Candidate predictors were first grouped by ecological role (precipitation, temperature, longitude) and within-group Spearman correlation filtering (|r| ≥ 0.85) was applied to remove redundant variables, retaining one representative per group. Variance inflation factors (VIF) were computed jointly from the 3 × 3 Spearman correlation matrix of the final selected predictors; the exclusion threshold was VIF ≥ 20. All three retained predictors were well below this threshold, confirming the absence of problematic multicollinearity.
Table 1. Selected environmental predictors. Variables were drawn from WorldClim v2 bioclimatic layers and provenance geographic coordinates. Candidate predictors were first grouped by ecological role (precipitation, temperature, longitude) and within-group Spearman correlation filtering (|r| ≥ 0.85) was applied to remove redundant variables, retaining one representative per group. Variance inflation factors (VIF) were computed jointly from the 3 × 3 Spearman correlation matrix of the final selected predictors; the exclusion threshold was VIF ≥ 20. All three retained predictors were well below this threshold, confirming the absence of problematic multicollinearity.
Full NameUnitsVIFSelection Basis
Annual precipitationmm yr−11.407Group representative; selected from precipitation cluster after |r| ≥ 0.85 correlation filtering
Temperature seasonality (SD of monthly mean temperatures × 100)°C × 1001.497Group representative; VIF computed after correlation filtering
Longitude of provenance originDecimal degrees1.075Retained as the primary geographic gradient; orthogonal to climate predictors after filtering
Table 2. Gradient forest genomic offset by provenance group. Within-dataset genomic offset calculated as the Euclidean distance in GF-transformed environmental space between each provenance’s observed environment and a synthetic shifted environment (shift = 0.5 SD per predictor across the three retained predictors: Annual Precipitation, Temperature Seasonality, and Longitude). n represents provenances per group.
Table 2. Gradient forest genomic offset by provenance group. Within-dataset genomic offset calculated as the Euclidean distance in GF-transformed environmental space between each provenance’s observed environment and a synthetic shifted environment (shift = 0.5 SD per predictor across the three retained predictors: Annual Precipitation, Temperature Seasonality, and Longitude). n represents provenances per group.
GroupCategorynMean OffsetSD Offset
All provenancesOverall790.008890.0014
North Alaska (incl. Kodiak & Montague)Major population130.010860.00127
South Alaska/BC mainlandMajor population320.008950.00067
US Pacific coast (BC south to California)Major population340.008080.00117
All island provenances (Kodiak + Montague + Haida Gwaii)Island vs. mainland130.009420.00131
Alaska mainland (excl. islands)Island vs. mainland320.009540.00122
Kodiak IslandIsland region10.01175
Montague IslandIsland region20.011610.00026
WashingtonCommercially Important70.008360.00094
Haida GwaiiCommercially Important/Island region100.008750.00036
Oregon + CaliforniaSouthern range100.006910.00027
Table 3. Spearman correlations between GF-derived genomic offset and provenance-level trait BLUEs at the Wexford common garden. Spearman ρ was calculated between within-dataset genomic offset and provenance-level best linear unbiased predictor (BLUE) values for height, stem diameter (DBH), and stem quality. BLUEs represent provenance deviations from the site mean estimated from a mixed model accounting for block effects, averaged across individual trees within each provenance. A negative ρ indicates that provenances with greater genomic-climatic displacement tend to perform worse at Wexford.
Table 3. Spearman correlations between GF-derived genomic offset and provenance-level trait BLUEs at the Wexford common garden. Spearman ρ was calculated between within-dataset genomic offset and provenance-level best linear unbiased predictor (BLUE) values for height, stem diameter (DBH), and stem quality. BLUEs represent provenance deviations from the site mean estimated from a mixed model accounting for block effects, averaged across individual trees within each provenance. A negative ρ indicates that provenances with greater genomic-climatic displacement tend to perform worse at Wexford.
Traitρp Valuenq Value
Height BLUE−0.659080790
DBH BLUE−0.44865.16 × 10−5777.73 × 10−5
Quality BLUE−0.348130.00203770.00203
Table 4. CMIP6 genomic offset projections for the European planting region under four scenarios × time-period combinations. Within-site genomic offset was calculated as the Euclidean distance in GF-transformed environmental space between current (WorldClim v2 baseline) and future (CMIP6 ensemble mean) climate across the European planting grid (−15° to 35° E, 35° to 72° N). Future climate was derived from the unweighted ensemble mean of eight CMIP6 GCMs under two emission scenarios (SSP2-4.5, SSP5-8.5) at two time periods (2041–2060, 2061–2080). Offset is driven entirely by projected changes in Temperature Seasonality and Annual Precipitation. The source range baseline row shows the within-dataset offset (0.5 SD synthetic shift across 79 IUFRO provenances) and serves as a reference scale for interpreting the magnitude of European projections. The percentage column expresses each scenario mean as a proportion of the source range mean (0.00889), providing direct comparability between the CMIP6 projections and the native-range offset distribution.
Table 4. CMIP6 genomic offset projections for the European planting region under four scenarios × time-period combinations. Within-site genomic offset was calculated as the Euclidean distance in GF-transformed environmental space between current (WorldClim v2 baseline) and future (CMIP6 ensemble mean) climate across the European planting grid (−15° to 35° E, 35° to 72° N). Future climate was derived from the unweighted ensemble mean of eight CMIP6 GCMs under two emission scenarios (SSP2-4.5, SSP5-8.5) at two time periods (2041–2060, 2061–2080). Offset is driven entirely by projected changes in Temperature Seasonality and Annual Precipitation. The source range baseline row shows the within-dataset offset (0.5 SD synthetic shift across 79 IUFRO provenances) and serves as a reference scale for interpreting the magnitude of European projections. The percentage column expresses each scenario mean as a proportion of the source range mean (0.00889), providing direct comparability between the CMIP6 projections and the native-range offset distribution.
ScenarioTime PeriodMean OffsetMax Offset% of Source Range Mean *
SSP2-4.52041–20600.00210.008224%
SSP2-4.52061–20800.00270.009231%
SSP5-8.52041–20600.00310.009535%
SSP5-8.52061–20800.00410.012446%
Source range baseline †0.00890.0129100%
* Percentage of source range mean offset (0.00889). † Within-dataset shift (0.5 SD per predictor) across 79 IUFRO provenances. All European scenarios used 8-GCM CMIP6 ensemble mean over 31,668 land cells (10 arc-min; −15° to 35° E, 35° to 72° N).
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Byrne, T.; Farrelly, N.; Kelleher, C.T.; Hodkinson, T.R.; Barth, S. Landscape Genomics and Climate Projections Reveal Genomic Offset and Provenance Vulnerability in Picea sitchensis. Forests 2026, 17, 743. https://doi.org/10.3390/f17070743

AMA Style

Byrne T, Farrelly N, Kelleher CT, Hodkinson TR, Barth S. Landscape Genomics and Climate Projections Reveal Genomic Offset and Provenance Vulnerability in Picea sitchensis. Forests. 2026; 17(7):743. https://doi.org/10.3390/f17070743

Chicago/Turabian Style

Byrne, Tomás, Niall Farrelly, Colin T. Kelleher, Trevor R. Hodkinson, and Susanne Barth. 2026. "Landscape Genomics and Climate Projections Reveal Genomic Offset and Provenance Vulnerability in Picea sitchensis" Forests 17, no. 7: 743. https://doi.org/10.3390/f17070743

APA Style

Byrne, T., Farrelly, N., Kelleher, C. T., Hodkinson, T. R., & Barth, S. (2026). Landscape Genomics and Climate Projections Reveal Genomic Offset and Provenance Vulnerability in Picea sitchensis. Forests, 17(7), 743. https://doi.org/10.3390/f17070743

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