Isla H. Myers-Smith’s research while affiliated with University of Edinburgh and other places

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Publications (163)


(a) Conceptual diagram of the project illustrating that pixels containing snow patches which persist later into the growing season will have seasonal NDVI curves of a different shape than pixels which contain lower snow persistence. Differences in shading within the pixels represent differences in ‘greenness’. (b) Hypotheses for this work, drawn from the differing conceptual NDVI curves. (c) Location of test plots within the Arctic/sub-Arctic, within their local context, and the drone plots themselves (1:15 000 scale).
NDVI curves for Sentinel-2 pixels with higher snow persistence generally have a lower and later peak than curves for pixels with lower snow persistence. Curves plotted from NDVI values fitted by a smoothed-spline model based on observed Sentinel-2 NDVI across a single season. The shaded grey area represents the range of days within which all pixels at each plot reached their peak NDVI, while the corresponding colour ribbon represents the mean snow persistence of all pixels which reached peak NDVI on each day within that period. The points represent the average peak NDVI for pixels in the upper and lower decile of snow persistence at each plot. The snow persistence colour gradient shows the relative snow persistence of that point standardised to the maximum and minimum snow persistence within each plot.
(a)–(c) Peak NDVI magnitude had a negative relationship with snow persistence in Sentinel-2 data at all three plots. Lines represent the predicted mean responses from the OLS regression. For Kluane Low (a) and Blæsedalen (c) these represent a linear fit (y ∼ x). For Kluane High (b) the line represents a logarithmic fit (y ∼ ln(x + 1). Full outputs for all OLS and INLA models of the relationship between snow persistence and peak NDVI magnitude are presented in tables S5, S6, S17 and S18. (d) Conceptual diagram showing the calculation of snow persistence as the integrated snow cover between the first and last imagery date at a given plot. The visualised snow persistence corresponds with the conceptual pixels in figure 1(a), where pixel A is representative of low snow persistence and pixel C is representative of high snow persistence.
(a)–(c) Peak NDVI timing had a positive relationship with snow persistence in Sentinel-2 data at all three plots. Lines for Kluane Low (a) and Blæsedalen (c) were fitted using a linear fit. The line for Kluane High (b) was fitted using a logarithmic model (y ∼ ln(x + 1). Full outputs for all OLS and INLA models of the relationship between snow persistence and peak NDVI timing are presented in tables S7, S8 and S19. (d) Dates of drone imagery used to generate snow persistence metric. Differences in the timing of observations between plots mean a universal metric could not be calculated.
Snow persistence was related to the magnitude and timing of peak NDVI in HLSS30 data at Blæsedalen. Mapped Sentinel-2 peak NDVI timing (a) visually corresponds with snow persistence (b) and this spatial patterning is preserved in HLSS30 peak NDVI timing (c). The shape and distribution of NDVI curves were similar between coarser HLSS30 data (d) and finer Sentinel-2 data (figure 2(c)). (e) HLSS30 peak NDVI magnitude had a relationship with snow persistence which is consistent with Sentinel-2 data (figure 3(c)). (f) HLSS30 peak NDVI timing had a relationship with snow persistence which is consistent with Sentinel-2 data (figure 4(c)). The snow persistence colour gradient shows the relative snow persistence of that point standardised to the maximum and minimum snow persistence for each data product (Sentinel-2, HLSS30) at the Blæsedalen plot. The points in panel (d) represent the average peak NDVI for pixels in the upper and lower decile of snow persistence at the Blæsedalen plot. The peak NDVI timing colour gradient shows the relative peak NDVI timing of that point standardised to the maximum and minimum peak NDVI day of year (DoY) for each data product at the Blæsedalen plot.
Snow persistence lowers and delays peak NDVI, the vegetation index that underpins Arctic greening analyses
  • Article
  • Full-text available

February 2025

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46 Reads

Calum G Hoad

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Isla H Myers-Smith

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Jeff T Kerby

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[...]

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Jakob J Assmann

Satellite imagery is critical for understanding land-surface change in the rapidly warming Arctic. Since the 1980s, studies have found positive trends in the normalised difference vegetation index (NDVI) derived from satellite imagery over the Arctic—commonly referred to as ‘Arctic greening’ and assumed to represent increased vegetation productivity. However, greening analyses use satellite imagery with pixel sizes ranging from tens to hundreds of metres and do not account for the integration of abiotic phenomena such as snow within vegetation indices. Here, we use high-resolution drone data from one Arctic and one sub-Arctic site to show that fine-scale snow persistence within satellite pixels is associated with both reduced magnitude and delayed timing of annual peak NDVI, the base metric of Arctic greening analyses. We found higher snow persistence within Sentinel-2 pixels is associated with a lower magnitude and later peak NDVI, with a mean difference in NDVI of 0.1 and seven days between high and low snow persistence pixels. These effects were stronger in NASA HLSS30 data, representative of Landsat data commonly used in greening analyses. Our findings indicate that unaccounted changes in fine-scale snow persistence may contribute to Arctic spectral greening and browning trends through either biotic responses of vegetation to snow cover or abiotic integration of snow within the estimated peak NDVI. In order to improve our understanding of Arctic land-surface change, studies should integrate very-high-resolution data to estimate the dynamics of late-season snow within coarser satellite pixels.

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Figure 1. The magnitude of boreal plant community colonisations (BCI) and plot abundance 455 increases (BAI) varied across the tundra. a) BCI estimated as the average of the plots within 456 a study area that experienced colonisations of boreal species (BCI > 0), b) BCI index of those 457 plots within each study area, c) BAI estimated as the average of the plots within a study area 458 that experienced an increase in the abundance of boreal species (BAI > 0), d) BAI index for 459 those plots within each study area. Points in a) and c) are coloured according to the 460 magnitude of increase (as BAI and BCI) as a study area average. Crosses in b) and d) indicate 461 the mean value of the plot borealization index at the study area level, which represent the 462 same value as coloured points in a) and c). Study areas in b) and d) are arranged by longitude. 463 Darker grey colours indicate overlap of multiple points. Note that these data show the 464 magnitude for plots that experienced increases in boreal species; for an analysis that includes 465 plots where boreal increases did not occur (BCI = 0 and BAI <= 0), see Figure S4. 466
Figure 3. Model estimates at the species level, with a) total number of times colonising plots 521 (model sample size = 220), and b) mean annual abundance increases across all plots (model 522 sample size = 129), as a function of class. Points indicate the mean model estimate for each 523 class, and error bars the 95% credible intervals. Sample sizes for categories in a) are: Boreal 524 specialist = 9, Boreal-tundra boundary = 113, Arctic specialist = 9, Ubiquitous = 89 species. 525 Sample sizes for categories in b) are: Boreal specialist = 5, Boreal-tundra boundary = 77, 526 Arctic specialist = 7, Ubiquitous = 40 species. 527
Figure 4. Colonising boreal species were shorter and more likely to be shrubs or graminoids, 544 though shrub species spanned the full range of height values. a) Boreal species that were 545 shorter colonised plots more often than taller species. Each point represents a plot, coloured 546 according to the functional group. The line and ribbon represent the model estimate and 95% 547 credible intervals of the univariate model (to allow for illustration of all the available height 548 values). b) Boreal shrubs and graminoids colonised more often than forbs. Model outputs are 549 represented as the mean estimate (points) and the 95% credible intervals (error bars). 550 Sample sizes for each category in the model are: forb = 62, graminoid = 32, shrub = 28 551 species. 552
Plant community borealization in the Arctic is driven by boreal-tundra boundary species

February 2025

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201 Reads

Following rapid climate change across the Arctic, tundra plant communities are experiencing extensive compositional shifts. One of the most prevalent changes is the encroachment of boreal species into the tundra (‘borealization’). Borealization has been reported at individual sites, but has not been systematically quantified across the tundra biome. Here, we use a dataset of 1,137 plots at 113 subsites across 32 study areas resurveyed at least once between 1981 and 2023 and encompassing 287 vascular plant species. We i) quantified the borealization of tundra ecosystems as the colonisation and the increase in abundance of boreal specialist and boreal-tundra boundary species, ii) assessed biogeographical, climatic and local drivers of borealization, and iii) identified species contributing most to borealization and their associated traits. Around half of the plots experienced borealization, especially at sites closer to the treeline, at higher elevations (mountains), in warmer and wetter regions, and at sites that had undergone the lowest magnitude of climate change. Boreal species were more likely to expand in Eurasia, and at sites with lower initial abundances of boreal species. Boreal species that colonised more plots were generally short, and more likely to be shrubs and graminoids than forbs. Boreal specialist species colonised three times less frequently than boreal-tundra boundary species, yet abundance changes were similar across groups. These findings indicate that borealization is mainly driven by the spread of already established species in the tundra, and suggest that future changes to Arctic ecosystems might not involve rapid, widespread replacement of Arctic species by boreal species. These observed and future plant community composition changes could affect land-atmosphere interactions, trophic dynamics and local and Indigenous livelihoods.


Examples of browning events arising from climatic, biotic and physical disturbance events
(A) Empetrum nigrum shoot mortality following an extreme winter warming event in northern Norway. (B) Almost 100% mortality from frost-drought of the dominant dwarf shrub Calluna vulgaris, Norway. (C) Dead Cassiope tetragona following an icing event, Svalbard, High Arctic. (D) Droughted Sphagnum from a combined heat-wave drought, Utqiaġvik, Alaska. (E) Spread of an Epirrita autumnata caterpillar outbreak at treeline from birch woodland onto tundra. Grey vegetation in foreground is defoliated Betula nana (dwarf birch) shrubs, grey trees mid-picture are defoliated tree birch (B. pubescens spp. czerepanovii) that is the source of the outbreak (sub-arctic Sweden). (F) Dead shoots of E. nigrum infected with the snow mould Arwidssonia empetri. (G) Dead E. nigrum following a caterpillar outbreak of E. autumnata and Operophtera brumata. (H) Browning from lemming grazing. (I) Aftermath of fire in the Yukon-Kuskokwim delta, Alaska, showing a dead Sphagnum mound and significant removal of the peaty organic layer. Abundant resprouting of Eriophorum vaginatum (cotton grass) clearly visible in mid-ground. (J) Resprouting of E. vaginatum a year after fire. This heathland was fire-prone due to a previous frost-drought event that left dead, dry, flammable vegetation. (K) A large retrogressive thaw slump (a megaslump >20 ha), Peel Plateau, NW Canada. (L) Active layer detachments near Eureka, Ellesmere Island. Photos: (A, C, G) Rachael Treharne (B, J) Gareth Phoenix (D) Donatella Zona (E) Thomas Parker (F, H) Johan Olofsson (I) Chris Linder (K) Julian Murton (L) Antoni Lewkowicz.
Browning event impacts on ecosystem carbon sequestration in the first years immediately following the event
Change in Net Ecosystem Exchange (NEE): +1 means a doubling of the pre-event (undisturbed) C uptake flux. 0 is no change with sink strength declining to −1 where there is no net uptake, x−5 means a shift to C fluxes opposite in sign (i.e., losses) but up to five-fold greater magnitude than the original C uptake flux. (1) Browning events arising from physical disturbance can result in NEE much greater in magnitude and opposite in sign than of the pre-event healthy vegetation (i.e., a shift from a C sink to a much larger C source). However, these disturbance events where there is less browning (2) can also cause more modest shifts resulting in reduced C sink size rather than conversion to a source (e.g., active layer detachments where vegetation remains partially intact or where ecosystem respiration is reduced due to lack of vegetation and reduced soil organic matter content). This more moderate change in NEE is also typical for biotic and climatic events (3) that typically result in lower C sink size rather than conversion to a source. The limitation on NEE impacts of browning from climatic and biotic drivers partially arises because photosynthesis from resilient plant species compensates for loss of sensitive species. Unique among events (4) herbivore outbreaks can also result in greater C sequestration from a rapidly recovering plant community being able to take advantage of nutrient inputs from frass, potentially doubling the C uptake compared to the original undisturbed vegetation. RTS = retrogressive thaw slump; ALDS = active layer detachment slide; Herbiv = herbivore outbreak; HwD = heatwave-drought; EWW = extreme winter warming.
Overview of recovery rates of browning events
Recovery is in years since event. % browning is % loss of live biomass. HwD is heatwave-drought, EWW is extreme winter warming, F-D is frost drought. (1) Climatic events and herbivore outbreaks all have similarly fast recovery with the majority of live biomass recovered within 4 years. (2) Much longer recovery times are associated with physical disturbance events (abrupt permafrost thaw and fire), and while significant initial recovery after fire can occur on similar timescales to climatic events from re-sprouting plants, (3) full recovery can take decades. (4) Abrupt permafrost thaw has the longest recovery time due to recovery potential being severely reduced where plant biomass is completely removed above and below ground. Events may also lead to greening in the long term. % browning and recovery rates vary within a single event type, so for each event type the graph represents a ‘typical’ trajectory based on data and text descriptions in the cited papers.
Characteristics of browning events. Durations and reported ranges of % damage from real events, not field simulations. ‘nd’ indicates no data. Superscript letters refer to notes as follows: (a) based on recovery of biomass or cover; (b) note, total area of impact often not reported in surveys of amount of damage, (c) not quantified but based on similarity of impact compared to extreme winter warming; (d) combined drought and heatwave; (e) at small scales scorching can result in little biomass removal, though fire typically burns >70% vegetation cover; (f) a thermal erosion feature often continues to expand, so duration only refers to a single point; (g) area includes thermokarst lake and wetland development; (h) beaver dams listed separately since the browning mechanism is dam creation, not herbivory of biomass; (i) decades to centuries for complete biomass recovery. Nordic Arctic region here refers to Norway (including Svalbard for icing events), Sweden and Finland north of the Arctic Circle
Browning events in Arctic ecosystems: Diverse causes with common consequences

January 2025

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201 Reads

Arctic ecosystems are experiencing extreme climatic, biotic and physical disturbance events that can cause substantial loss of plant biomass and productivity, sometimes at scales of >1000 km². Collectively known as browning events, these are key contributors to the spatial and temporal complexity of Arctic greening and vegetation dynamics. If we are to properly understand the future of Arctic terrestrial ecosystems, their productivity, and their feedbacks to climate, understanding browning events is essential. Here we bring together understanding of browning events in Arctic ecosystems to compare their impacts and rates of recovery, and likely future changes in frequency and distribution. We also seek commonalities in impacts across these contrasting event types. We find that while browning events can cause high levels of plant damage (up to 100% mortality), ecosystems have substantial capacity for recovery, with biomass largely re-established within five years for many events. We also find that despite the substantial loss of leaf area of dominant species, compensatory mechanisms such as increased productivity of undamaged subordinate species lessen the impacts on carbon sequestration. These commonalities hold true for most climatic and biotic events, but less so for physical events such as fire and abrupt permafrost thaw, due to the greater removal of vegetation. Counterintuitively, some events also provide conditions for greater productivity (greening) in the longer-term, particularly where the disturbance exposes ground for plant colonisation. Finally, we find that projected changes in the causes of browning events currently suggest many types of events will become more frequent, with events of tundra fire and abrupt permafrost thaw expected to be the greatest contributors to future browning due to their severe impacts and occurrence in many Arctic regions. Overall, browning events will have increasingly important consequences for ecosystem structure and function, and for feedback to climate.


Environmental Conditions Modulate Warming Effects on Plant Litter Decomposition Globally

December 2024

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771 Reads

Ecology Letters

Empirical studies worldwide show that warming has variable effects on plant litter decomposition, leaving the overall impact of climate change on decomposition uncertain. We conducted a meta‐analysis of 109 experimental warming studies across seven continents, using natural and standardised plant material, to assess the overarching effect of warming on litter decomposition and identify potential moderating factors. We determined that at least 5.2° of warming is required for a significant increase in decomposition. Overall, warming did not have a significant effect on decomposition at a global scale. However, we found that warming reduced decomposition in warmer, low‐moisture areas, while it slightly increased decomposition in colder regions, although this increase was not significant. This is particularly relevant given the past decade's global warming trend at higher latitudes where a large proportion of terrestrial carbon is stored. Future changes in vegetation towards plants with lower litter quality, which we show were likely to be more sensitive to warming, could increase carbon release and reduce the amount of organic matter building up in the soil. Our findings highlight how the interplay between warming, environmental conditions, and litter characteristics improves predictions of warming's impact on ecosystem processes, emphasising the importance of considering context‐specific factors.



Earlier and increased growth of tundra willows after a decade of growth in a warmer common garden environment

November 2024

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31 Reads

1. The expansion of woody shrubs, known as shrubification, is one of the most widely observed patterns of vegetation change in the tundra. Yet, we do not know the relative importance of plant plasticity and genetic change in determining shrub responses to warming. Plastic responses to the environment can be rapid, while genetic differentiation is much slower. 2. We established a common garden experiment, using three tundra willow species (two tall willow shrubs: Salix richardsonii, S. pulchra, and one prostrate willow: S. arctica). We transplanted cuttings from southern (alpine, high elevation) and northern (Arctic) source populations to a 5ºC warmer environment in southern boreal Yukon, simulating projected future Arctic conditions. We monitored growth, phenology and functional traits in the common garden over a ten-year period from 2013 to 2023 and measured the same variables in the source populations. 3. The three willow species responded differently to a warmer environment. Southern S. richardsonii shrubs in the common garden grew almost seven times faster than the northern willows of the same species. Neither common garden populations of S. pulchra increased in height, but southern individuals grew wider. S. arctica growth patterns were similar between southern and northern common garden populations. All shrubs in the garden advanced their date of leaf bud burst by approximately one month compared to source populations. All northern willows growing in the garden also advanced senescence timing, resulting in less change to overall growing season length for northern willows. We suggest local adaptation to source population conditions as a likely cause of early senescence and limiting growth of northern willows in the common garden. 4. Synthesis: Our findings suggest longer growing seasons due to the advancement of leaf bud burst but not delayed senescence, and potential for rapid shrub growth as tundra ecosystems continue to warm. However, responses to warming vary by species and population, as we observed varied levels of plasticity for traits, phenology and growth. Local adaptation to past climatic conditions and slow genetic change may limit future shrub growth and determine which shrub species proliferate with future warming.


Snow persistence influences vegetation metrics central to Arctic greening analyses

July 2024

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20 Reads

Satellite imagery is critical for understanding land-surface change in the rapidly warming Arctic. Since the 1980s, studies have found positive trends in the normalised difference vegetation index (NDVI) derived from satellite imagery over the Arctic - commonly referred to as ‘Arctic greening’ and assumed to represent increased vegetation productivity. However, greening analyses use satellite imagery with pixel sizes ranging from tens to hundreds of metres and do not account for the integration of abiotic phenomena such as snow within vegetation indices. Here, we use high resolution drone data from one Arctic and one sub-Arctic site to show that fine-scale snow persistence within satellite pixels is associated with both reduced magnitude and delayed timing of annual peak NDVI, the base metric of Arctic greening analyses. We found higher snow persistence within Sentinel-2 pixels is associated with a lower magnitude and later peak NDVI, with a mean difference in NDVI of 0.088 and seven days between high and low snow persistence pixels. These effects were stronger in NASA HLSS30 data, representative of Landsat data commonly used in greening analyses. Our findings indicate that unaccounted changes in fine-scale snow persistence may contribute to Arctic spectral greening and browning trends through either ecological responses of vegetation to snow cover or abiotic interactions between snow and the estimated peak NDVI. In order to improve our understanding of Arctic land-surface change, studies should integrate very-high-resolution data to estimate the dynamics of late season snow within coarser satellite pixels.


Graphical Abstract.
Intercomparison of global foliar trait maps reveals fundamental differences and limitations of upscaling approaches

June 2024

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604 Reads

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1 Citation

Remote Sensing of Environment

Foliar traits such as specific leaf area (SLA), leaf nitrogen (N), and phosphorus (P) concentrations play important roles in plant economic strategies and ecosystem functioning. Various global maps of these foliar traits have been generated using statistical upscaling approaches based on in-situ trait observations. Here, we intercompare such global upscaled foliar trait maps at 0.5° spatial resolution (six maps for SLA, five for N, three for P), categorize the upscaling approaches used to generate them, and evaluate the maps with trait estimates from a global database of vegetation plots (sPlotOpen). We disentangled the contributions from different plant functional types (PFTs) to the upscaled maps and quantified the impacts of using different plot-level trait metrics on the evaluation with sPlotOpen: community weighted mean (CWM) and top-of-canopy weighted mean (TWM). We found that the global foliar trait maps of SLA and N differ drastically and fall into two groups that are almost uncorrelated (for P only maps from one group were available). The primary factor explaining the differences between these groups is the use of PFT information combined with remote sensing-derived land cover products in one group while the other group mostly relied on environmental predictors alone. The maps that used PFT and corresponding land cover information exhibit considerable similarities in spatial patterns that are strongly driven by land cover. The maps not using PFTs show a lower level of similarity and tend to be strongly driven by individual environmental variables. Upscaled maps of both groups were moderately correlated to sPlotOpen data aggregated to the grid-cell level (R = 0.2-0.6) when processing sPlotOpen in a way that is consistent with the respective trait upscaling approaches, including the plot-level trait metric (CWM or TWM) and the scaling to the grid cells with or without accounting for fractional land cover. The impact of using TWM or CWM was relevant, but considerably smaller than that of the PFT and land cover information. The maps using PFT and land cover information better reproduce the between-PFT trait differences of sPlotOpen data, while the two groups performed similarly in capturing within-PFT trait variation. Our findings highlight the importance of explicitly accounting for within-grid-cell trait variation, which has important implications for applications using existing maps and future upscaling efforts. Remote sensing information has great potential to reduce uncertainties related to scaling from in-situ observations to grid cells and the regression-based mapping steps involved in the upscaling.


Tundra vegetation community, not microclimate, controls asynchrony of above and belowground phenology

June 2024

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99 Reads

The below-ground growing season often extends beyond the above-ground growing season in tundra ecosystems. However, we do not yet know where and when this occurs and whether these phenological asynchronies are driven by variation in local vegetation communities or by spatial variation in microclimate. Here, we combined above- and below-ground plant phenology metrics to compare the relative timings and magnitudes of leaf and root growth and senescence across microclimates and plant communities at five sites across the tundra biome. We observed asynchronous growth between above-ground and below-ground plant tissue, with the below-ground season extending up to 74% beyond the onset of above-ground leaf senescence. Plant community type, rather than microclimate, was a key factor controlling the timing, productivity and growth rates of roots, with graminoid roots exhibiting a distinct ‘pulse’ of growth later into the growing season than shrub roots. Our findings indicate the potential of vegetation change to influence below-ground carbon storage as roots remain active in unfrozen soils for longer as the climate warms. Taken together, increased root growth in soils that remain thawed later into the growing season, in combination with ongoing tundra vegetation change including increased shrubs and graminoids, can act together to alter below-ground productivity and carbon cycling in the tundra biome.


Multiple Pleistocene refugia for Arctic Bell-Heather revealed with genomic analyses of modern and historic plants

May 2024

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110 Reads

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1 Citation

Journal of Biogeography

Aim Arctic plants survived the Pleistocene glaciations in unglaciated refugia. The number, ages, and locations of these refugia are often unclear. We use high‐resolution genomic data from present‐day and Little‐Ice‐Age populations of Arctic Bell‐Heather to re‐evaluate the biogeography of this species and determine whether it had multiple independent refugia or a single refugium in Beringia. Location Circumpolar Arctic and Coastal British Columbia (BC) alpine. Taxon Cassiope tetragona L., subspecies saximontana and tetragona , outgroup C. mertensiana (Ericaceae). Methods We built genotyping‐by‐sequencing (GBS) libraries using Cassiope tetragona tissue from 36 Arctic locations, including two ~250‐ to 500‐year‐old populations collected under glacial ice on Ellesmere Island, Canada. We assembled a de novo GBS reference to call variants. Population structure, genetic diversity and demography were inferred from PCA, ADMIXTURE, fastsimcoal2, SplitsTree, and several population genomics statistics. Results Population structure analyses identified 4–5 clusters that align with geographic locations. Nucleotide diversity was highest in Beringia and decreased eastwards across Canada. Demographic coalescent analyses dated the following splits with Alaska: BC subspecies saximontana (5 mya), Russia (~1.4 mya), Europe (>200–600 kya), and Greenland (~60 kya). Northern Canada populations appear to have formed during the current interglacial (7–9 kya). Admixture analyses show genetic variants from Alaska appear more frequently in present‐day than historic plants on Ellesmere Island. Conclusions Population and demographic analyses support BC, Alaska, Russia, Europe and Greenland as all having had independent Pleistocene refugia. Northern Canadian populations appear to be founded during the current interglacial with genetic contributions from Alaska, Europe and Greenland. We found evidence, on Ellesmere Island, for continued recent gene flow in the last 250–500 years. These results suggest that a re‐analysis of other Arctic species with shallow population structure using higher resolution genomic markers and demographic analyses may help reveal deeper structure and other circumpolar glacial refugia.


Citations (71)


... A recently published work simulated global maps of three leaf traits via optimality models based on eco-evolutionary optimality theory 35 . However, the various published global trait maps do not always show consistent global patterns, reflecting differences in data sources and upscaling methods 35,36 . ...

Reference:

Global patterns of plant functional traits and their relationships to climate
Intercomparison of global foliar trait maps reveals fundamental differences and limitations of upscaling approaches

Remote Sensing of Environment

... In our study, we employed the TBI to quantify the dynamics of decomposition and stabilisation of organic matter in both impacted and reference soils during the dry and wet seasons (Keuskamp et al. 2013;Sarneel et al. 2024). The TBI calculates two primary parameters: the decomposition rate constant (k) and the stabilisation factor (S). k measures the initial rate at which labile organic material decomposes, providing insights into the short-term dynamics of carbon processing within the soil. ...

Reading tea leaves worldwide: Decoupled drivers of initial litter decomposition mass‐loss rate and stabilization

Ecology Letters

... The study of animal effects on elemental cycling is interdisciplinary and advances in animal tracking (camera traps and movebank) and environmental logging data (loggers and pendants) platforms are contributing to the growth of empirical studies in zoogeochemistry Ellis-Soto et al. 2021). Several recent reviews have synthesised evidence of the effects of animals on different components of elemental cycles (e.g., stocks and fluxes) in different ecosystems (Bakker et al. 2016;Barbero-Palacios et al. 2024;Pringle et al. 2023;Schmitz et al. 2018Schmitz et al. , 2023Schmitz and Leroux 2020;Subalusky and Post 2019;Trepel, le Roux, et al. 2024). These quantitative reviews show the promise of data availability to estimate model parameters and validate model outputs (Supporting Information S4). ...

Herbivore diversity effects on Arctic tundra ecosystems. A systematic review

Environmental Evidence

... and stabilized substrates (S = 0.006-0.35) across the study sites, a result that implies the role of site-specific microenvironments in affecting decomposition across ecosystems (Gallois et al. 2023, Morffi-Mestre et al. 2023. Although the driving factors varied between mountains (Fig. 5-6), our results showed a relatively consistent and high importance of microclimate for both k and S in colder environments, i.e., the western mountains GMT and YMT. ...

Summer litter decomposition is moderated by scale‐dependent microenvironmental variation in tundra ecosystems
  • Citing Article
  • July 2023

Oikos

... The observation that evergreen dwarf shrubs are more severely affected by extreme winter warming, frost drought, and icing compared to deciduous shrubs indicates that a greater deciduousness could arise from repeated events, analogous to increases in deciduousness of boreal forests arising from greater fire frequency [129,130]. This could facilitate Arctic greening through deciduous shrubification [78,131]. Furthermore, recovery of biomass may also be partially facilitated by subordinate species including greater tolerance of bryophytes and lichens, which may further benefit from the opening of the damaged shrub canopy [121] (though see [128]). ...

Plant traits poorly predict winner and loser shrub species in a warming tundra biome

... However, unlike the results of our study, shifts in plant phenology and links to reproductive fitness in alpine tundra systems might be more sensitive to other (non-temperature) parameters, such as snowmelt timing and, possibly, photoperiod (Rixen et al., 2022). Furthermore, although the 'borealization' of Arctic ecosystems is predicted under climate change, recent global syntheses argue that this pattern has not occurred in any consistent way (García Criado et al., 2023), potentially diminishing the ability to extend these generalities to non-tundra ecosystems. Further research is needed to determine how these changes in fitness as a result of advancing phenology will or will not scale up to changes in the abundance of tundra species worldwide. ...

Plant diversity dynamics over space and time in a warming Arctic

... The overall biodiversity, or specific diversity metrics, can show contrasting trends, including increases, decreases, or stability, depending on the spatial and temporal scales considered (McGill et al. 2015). This highlights the ongoing debate about the direction and variability of biodiversity change, which is also influenced by different drivers of change, including biotic and abiotic factors (Dornelas et al. 2023, Staude et al. 2023. Therefore, explicit assessments across these scales while accounting for drivers of change are fundamental for understanding the patterns and impacts of biodiversity change, and for informing conservation and ecosystem management efforts (McGill et al. 2015, Blowes et al. 2019, Dornelas et al. 2023. ...

Looking back on biodiversity change: lessons for the road ahead

... The environmental variable-driven statistical approach employs environmental factors (typically encompassing climate, soil, and terrain) in conjunction with field-observed trait data to develop a statistical model, which is then upscaled to a broader extent (reviewed by Dechant et al., 2023). Since these environmental variables have already been observed or interpolated at a global scale, these approaches allow for more straightforward upscaling of traits and offer greater detail compared to the PFT lookup table approach. ...

Intercomparison of global foliar trait maps reveals fundamental differences and limitations of upscaling approaches

... This implies that while warming decreases litter decomposition in warm and dry systems, the effectiveness of carbon storage is likely compromised due to warmer temperatures and dry conditions (Yi, Wei, and Hendrey 2014;Hartley et al. 2021). While previous studies have reported clear interactions between increasing temperature and moisture (Aerts 2006;Thomas et al. 2023), our research shows that these interactions manifest differently in various macro-environments. Our results highlight that macro-environmental factors can significantly influence how site-specific factors like the degree of warming affect litter decomposition, especially in warm and wet conditions, which in our dataset had the largest range of degree of warming. ...

Litter quality outweighs climate as a driver of decomposition across the tundra biome
  • Citing Preprint
  • March 2023

... Yet, our understanding of successional trajectories on reefs is restricted largely to solid, stable hard carbonate surfaces despite coral rubble, the fragmented skeletal remains of reef-building organisms, typically covering large areas of reef following disturbances. These remains are known as legacy materials-the remnants of dead foundation species, that is, hard corals in the case of tropical reefs-that can have a marked effect on ecosystem function and recovery trajectories (Albertson et al., 2024;Barnhill et al., 2022;Saldaña et al., 2024). Coral rubble can be colonized and recruited upon following disturbances, contributing to reef structure and recovery (Perry, 2001), yet unbound and unstable rubble can limit coral reef recovery for decades (Clark & Edwards, 1995;Fox et al., 2019). ...

Incorporating dead material in ecosystem assessments and projections
  • Citing Article
  • February 2023

Nature Climate Change