Arden Burrell’s research while affiliated with Woodwell Climate Research Center and other places

What is this page?


This page lists works of an author who doesn't have a ResearchGate profile or hasn't added the works to their profile yet. It is automatically generated from public (personal) data to further our legitimate goal of comprehensive and accurate scientific recordkeeping. If you are this author and want this page removed, please let us know.

Publications (19)


Author Correction: Wildfires offset the increasing but spatially heterogeneous Arctic–boreal CO2 uptake
  • Article
  • Full-text available

February 2025

·

180 Reads

Nature Climate Change

Anna-Maria Virkkala

·

·

·

[...]

·

Download

Spatial variability in Arctic–boreal CO2 fluxes
a,b, Maps showing the mean annual terrestrial NEE (a) and its trends (b) based on site-level data, our upscaling, the atmospheric inversion ensemble and the CMIP6 process model ensemble. The in situ trends in b are based on sites that have more than seven years of data. Supplementary Fig. 2 shows the uncertainty in upscaled NEE and the significance of the trends. While the average upscaled NEE values go up to 116 g C m⁻² yr⁻¹, most of the values are below 60 g C m⁻² yr⁻¹.
Trends in CO2 budgets
a,b, Terrestrial CO2 budgets for 1-km (blue; 2001–2020) and 8-km (grey; 1990–2016) NEE as well as 1-km NEE + fire emissions (red; 2002–2020) across the ABZ (a) and the permafrost region (b). c, An overlay analysis of NEE, GPP and Reco trend maps identifying how trends in GPP and Reco relate to trends in NEE over 2001–2020 (includes significant and non-significant trends). d, Pixels burned during 2002–2020. The central values (that is, annual budgets; solid lines) in a and b are derived from the outputs of the final model using the complete training dataset. The standard deviations (shaded areas) are calculated from the outputs of 20 different models, each trained on a unique bootstrapped sample of the original training data. The magnitude of each trend was computed using the Theil–Sen approach, and the P value determined using the Mann–Kendall test.
Seasonal shifts in CO2 flux dynamics
a–c, Average upscaled monthly NEE (a), GPP (b) and Reco (c) in boreal and tundra biomes during the past two decades. Negative NEE values represent net uptake, and positive values indicate net release. The central mean values in the figures are derived from the outputs of the final model using the complete training dataset. The standard deviations (error bars) are calculated from the outputs of 20 different models, each trained on a unique bootstrapped sample of the original training data. Error bars are shown only for the 2011–2020 period but are similar for the 2001–2010 period. Note that NEE was 1.4 g C m⁻² month⁻¹ lower in September in 2011–2020 than in 2001–2010 in the boreal biome, but this is not shown in the figure.
Regional variability in CO2 budget trends
a,b, Terrestrial CO2 budgets for NEE and NEE + fire in key regions across the boreal (a) and tundra (b). Terrestrial CO2 budgets are shown for 1-km (blue; 2001–2020) and 8-km (grey; 1990–2016) NEE as well as 1-km NEE + fire emissions (red; 2002–2020). The inset in the Alaskan boreal plot in a shows the time series with a narrower y axis than that in the main figure to better depict interannual variability. The central lines in the figures are derived from the outputs of the final model using the complete training dataset. The standard deviations (shaded areas) are calculated from the outputs of 20 different models, each trained on a unique bootstrapped sample of the original training data. The magnitude of the trend was computed using the Theil–Sen approach, and the P value determined using the Mann–Kendall test.
Wildfires offset the increasing but spatially heterogeneous Arctic–boreal CO2 uptake

January 2025

·

290 Reads

·

2 Citations

Nature Climate Change

The Arctic–Boreal Zone is rapidly warming, impacting its large soil carbon stocks. Here we use a new compilation of terrestrial ecosystem CO2 fluxes, geospatial datasets and random forest models to show that although the Arctic–Boreal Zone was overall an increasing terrestrial CO2 sink from 2001 to 2020 (mean ± standard deviation in net ecosystem exchange, −548 ± 140 Tg C yr⁻¹; trend, −14 Tg C yr⁻¹; P < 0.001), more than 30% of the region was a net CO2 source. Tundra regions may have already started to function on average as CO2 sources, demonstrating a shift in carbon dynamics. When fire emissions are factored in, the increasing Arctic–Boreal Zone sink is no longer statistically significant (budget, −319 ± 140 Tg C yr⁻¹; trend, −9 Tg C yr⁻¹), and the permafrost region becomes CO2 neutral (budget, −24 ± 123 Tg C yr⁻¹; trend, −3 Tg C yr⁻¹), underscoring the importance of fire in this region.


Regional changes over North Amerca and Eurasia, and their tundra and boreal sub‐regions. Indicators are: (a) near‐surface air temperature (AT; °C); (b) non‐frozen season (NFS; days per year); (c) active‐layer thickness (ALT; m); (d) precipitation (PPT; mm); (e) non‐winter vapor pressure deficit (VPD; kPa); (f) sum of winter snow cover (SC; million km²); (g) soil moisture (SM; cm³ cm⁻³); (h) surface fractional water coverage (FW; %); (i) Non‐frozen season normalized difference vegetation index (NDVI; unitless); (j) Non‐frozen season vegetation optical depth (VOD; unitless); (k) pixel‐percent tree cover (TC; %); (l) pixel‐percent non‐tree cover (NTC; %).
Percent of total regional area showing a significant increasing (red) or decreasing (blue) trend in indicator status over the ~1997–2020 period, according to boreal forest (BF), boreal wetland (BWL), boreal non‐forest (including shrubland and grassland, G/S), and tundra (TUN) for Eurasia and North America. Indicators include: (a) annual average AT (°C); (b) annual total NFS (days); (c) annual maximum ALT (m); (d) annual total PPT (mm); (e) annual total winter SC (Mkm²); (f) annual average VPD (kPa); (g) annual average non‐frozen season FW (% pixel coverage) ; (h) annual non‐frozen season SM (cm³/cm³); (i) annual non‐frozen season NDVI (unitless); (j) annual non‐frozen VOD (unitless).
Multivariate change hotspot maps for the 1997–2020 period (unless otherwise indicated), according to select directional changes in thermal, moisture, and vegetation indicators. Thermal includes: average increase in annual AT (°C); increase in annual NFS (days); and increase in annual ALT (m). Moisture includes: decrease in annual PPT (mm); increase in annual VPD (kPa); decrease in annual non‐frozen season SM (cm³ cm⁻³). Vegetation includes decreases in annual non‐frozen season average NDVI (unitless; 1998–2020) and VOD (unitless; 1998–2017). Panels (a), (c), (e) show identified change “hotspots” based on pixel‐level analyses; (b), (d), (f) show indicator change across individual ecoregions.
Regional Hotspots of Change in Northern High Latitudes Informed by Observations From Space

January 2025

·

168 Reads

The high latitudes cover ∼20% of Earth's land surface. This region is facing many shifts in thermal, moisture and vegetation properties, driven by climate warming. Here we leverage remote sensing and climate reanalysis records to improve understanding of changes in ecosystem indicators. We applied non‐parametric trend detections and Getis‐Ord Gi* spatial hotspot assessments. We found substantial terrestrial warming trends across Siberia, portions of Greenland, Alaska, and western Canada. The same regions showed increases in vapor pressure deficit; changes in precipitation and soil moisture were variable. Vegetation greening and browning were widespread across both continents. Browning of the boreal zone was especially evident in autumn. Multivariate hotspot analysis indicated that Siberian ecoregions have experienced substantial, simultaneous, changes in thermal, moisture and vegetation status. Finally, we found that using regionally‐based trends alone, without local assessments, can yield largely incomplete views of high‐latitude change.



Global dryland mean NDVImax and AI trends of models under different scenarios
a Global dryland mean NDVImax trends from the past to the different future scenarios. b Global dryland mean AI trends from the past to the different future scenarios. Each light-colored line represents the simulation result from an individual model (same color represents same scenario: light green (historical), light blue (SSP-1.26), light pink (SSP-2.45), light red (SSP-5.85)), the dark-colored lines (observation, his_mean, 126_mean, 245_mean, 370_mean and 585_mean) represent global dryland mean of observed data, multi-model mean drive from 24 models of historical scenario and different future scenarios respectively.
NDVImax changes and model contribution under scenario SSP5-8.5 between period 2031–2050 and 1982–2001
a NDVImax changes. Pixels where at least 50% of models indicate significant changes (p < 0.05), and 75% of models agree on the direction of change are plotted as green to brown. Pixels where 50% of models show significant changes, but less than 75% of models agree on the direction of change are plotted as white. Nonsignificant positive changes are plotted as cyan, nonsignificant negative changes are plotted as violet. b Percentage of models simulating negative changes. All non-dryland areas and areas that failed to build linear relationship (e.g., no rainfall or lack NDVI values in the time series) are masked as gray.
AI changes under scenario SSP5-8.5 between period 2031–2050 and 1982–2001
An increase in AI indicating wetter conditions (plotted in pink), a decrease in AI indicating drier conditions (plotted in blue). All non-dryland and failed to build linear relationship areas (e.g., no rainfall or lack NDVI values in the time series) are masked as gray.
Climate variables changes under scenario SSP5-8.5 between period 2031–2050 and 1982–2001
a Monthly total precipitation changes (blue represents increase, brown represents decrease). b Monthly mean temperature changes (red represents increase). c Monthly total PET changes (red represents increase, white represent decrease). All non-dryland and failed to build linear relationship areas (e.g., no rainfall or lack NDVI values in the time series) are masked as gray.
Less than 4% of dryland areas are projected to desertify despite increased aridity under climate change

June 2024

·

142 Reads

·

6 Citations

Drylands have low biological productivity compared to non-drylands, making many human activities within them sensitive to long-term trends. Trends in the Aridity Index over several decades indicate increasing aridity in the drylands, which has been linked to increasing occurrence of desertification. Future projections show continued increases in aridity due to climate change, suggesting that drylands will expand. In contrast, satellite observations indicate an increase in vegetation productivity. Given the past inconsistency between the Aridity Index changes and observed vegetation changes, the future evolution of vegetation productivity within the drylands remains an open question. Here we used a data driven approach to show that increasing aridity in drylands won’t lead to a general loss of vegetation productivity. Most of the global drylands are projected to see an increase in vegetation productivity due to climate change through 2050. The aridity index will not be a good indicator of drylands in future climates. We found a broad boost to dryland vegetation productivity due to the carbon dioxide (CO2) fertilization effect that is negated by climate changes in at most 4% of global drylands to produce desertification. These regions include parts of north-east Brazil, Namibia, western Sahel, Horn of Africa and central Asia.


The predictability of near‐term forest biomass change in boreal North America

January 2024

·

112 Reads

·

2 Citations

Climate change is driving substantial changes in North American boreal forests, including changes in productivity, mortality, recruitment, and biomass. Despite the importance for carbon budgets and informing management decisions, there is a lack of near‐term (5–30 year) forecasts of expected changes in aboveground biomass (AGB). In this study, we forecast AGB changes across the North American boreal forest using machine learning, repeat measurements from 25,000 forest inventory sites, and gridded geospatial datasets. We find that AGB change can be predicted up to 30 years into the future, and that training on sites across the entire domain allows accurate predictions even in regions with only a small amount of existing field data. While predicting AGB loss is less skillful than gains, using a multi‐model ensemble can improve the accuracy in detecting change direction to >90% for observed increases, and up to 70% for observed losses. Higher stem density, winter temperatures, and the presence of temperate tree species in forest plots were positively associated with AGB change, whereas greater initial biomass, continentality (difference between mean summer and winter temperatures), prevalence of black spruce ( Picea mariana ), summer precipitation, and early warning metrics from long‐term remote sensing time series were negatively associated with AGB change. Across the domain, we predict nondisturbance‐induced declines in AGB at 23% of sites by 2030. The approach developed here can be used to estimate near‐future forest biomass in boreal North America and inform relevant management decisions. Our study also highlights the power of machine learning multi‐model ensembles when trained on a large volume of forest inventory plots, which could be applied to other regions with adequate plot density and spatial coverage.



Burned area and carbon emissions across northwestern boreal North America from 2001–2019

July 2023

·

384 Reads

·

17 Citations

Fire is the dominant disturbance agent in Alaskan and Canadian boreal ecosystems and releases large amounts of carbon into the atmosphere. Burned area and carbon emissions have been increasing with climate change, which have the potential to alter the carbon balance and shift the region from a historic sink to a source. It is therefore critically important to track the spatiotemporal changes in burned area and fire carbon emissions over time. Here we developed a new burned-area detection algorithm between 2001–2019 across Alaska and Canada at 500 m (meters) resolution that utilizes finer-scale 30 m Landsat imagery to account for land cover unsuitable for burning. This method strictly balances omission and commission errors at 500 m to derive accurate landscape- and regional-scale burned-area estimates. Using this new burned-area product, we developed statistical models to predict burn depth and carbon combustion for the same period within the NASA Arctic–Boreal Vulnerability Experiment (ABoVE) core and extended domain. Statistical models were constrained using a database of field observations across the domain and were related to a variety of response variables including remotely sensed indicators of fire severity, fire weather indices, local climate, soils, and topographic indicators. The burn depth and aboveground combustion models performed best, with poorer performance for belowground combustion. We estimate 2.37×106 ha (2.37 Mha) burned annually between 2001–2019 over the ABoVE domain (2.87 Mha across all of Alaska and Canada), emitting 79.3 ± 27.96 Tg (±1 standard deviation) of carbon (C) per year, with a mean combustion rate of 3.13 ± 1.17 kg C m-2. Mean combustion and burn depth displayed a general gradient of higher severity in the northwestern portion of the domain to lower severity in the south and east. We also found larger-fire years and later-season burning were generally associated with greater mean combustion. Our estimates are generally consistent with previous efforts to quantify burned area, fire carbon emissions, and their drivers in regions within boreal North America; however, we generally estimate higher burned area and carbon emissions due to our use of Landsat imagery, greater availability of field observations, and improvements in modeling. The burned area and combustion datasets described here (the ABoVE Fire Emissions Database, or ABoVE-FED) can be used for local- to continental-scale applications of boreal fire science.


Figure 5. Total burned area (a), total carbon emissions (b), mean combustion (c), and mean burn depth (d) between 2001-2019 aggregated to a 70 km grid. Note that burned area (a) covers all of Alaska and Canada, whereas all other metrics cover the ABoVE extended domain.
Figure 8. Monthly burned area across states, and Canadian provinces and territories between 2001-2019. January, February, November and December have been omitted due to low fire occurrence.
Burned Area and Carbon Emissions Across Northwestern Boreal North America from 2001–2019

September 2022

·

367 Reads

·

4 Citations

Fire is the dominant disturbance agent in Alaskan and Canadian boreal ecosystems and releases large amounts of carbon into the atmosphere. Burned area and carbon emissions have been increasing with climate change, which have the potential to alter the carbon balance and shift the region from a historic sink to a source. It is therefore critically important to track the spatiotemporal changes in burned area and fire carbon emissions over time. Here we developed a new burned area detection algorithm between 2001–2019 across Alaska and Canada at 500 meters (m) resolution that utilizes finer-scale 30 m Landsat imagery to account for land cover unsuitable for burning. This method strictly balances omission and commission errors at 500 m to derive accurate landscape- and regional-scale burned area estimates. Using this new burned area product, we developed statistical models to predict burn depth and carbon combustion for the same period within the NASA Arctic-Boreal Vulnerability Experiment (ABoVE) core and extended domain. Statistical models were constrained using a database of field observations across the domain and were related to a variety of response variables including remotely-sensed indicators of fire severity, fire weather indices, local climate, soils, and topographic indicators. The burn depth and aboveground combustion models performed best, with poorer performance for belowground combustion. We estimate 2.37 million hectares (Mha) burned annually between 2001–2019 over the ABoVE domain (2.87 Mha across all of Alaska and Canada), emitting 79.3 +/- 27.96 (+/- 1 standard deviation) Teragrams of carbon (C) per year, with a mean combustion rate of 3.13 +/- 1.17 kilograms C m-2. Mean combustion and burn depth displayed a general gradient of higher severity in the northwestern portion of the domain to lower severity in the south and east. We also found larger fire years and later season burning were generally associated with greater mean combustion. Our estimates are generally consistent with previous efforts to quantify burned area, fire carbon emissions, and their drivers in regions within boreal North America; however, we generally estimate higher burned area and carbon emissions due to our use of Landsat imagery, greater availability of field observations, and improvements in modeling. The burned area and combustion data sets described here (the ABoVE Fire Emissions Database, or ABoVE-FED) can be used for local to continental-scale applications of boreal fire science.


Climate change, fire return intervals and the growing risk of permanent forest loss in boreal Eurasia

March 2022

·

225 Reads

·

33 Citations

The Science of The Total Environment

Climate change has driven an increase in the frequency and severity of fires in Eurasian boreal forests. A growing number of field studies have linked the change in fire regime to post-fire recruitment failure and permanent forest loss. In this study we used four burned area and two forest loss datasets to calculate the landscape-scale fire return interval (FRI) and associated risk of permanent forest loss. We then used machine learning to predict how the FRI will change under a high emissions scenario (SSP3–7.0) by the end of the century. We found that there are currently 133,000 km² forest at high, or extreme, risk of fire-induced forest loss, with a further 3 M km² at risk by the end of the century. This has the potential to degrade or destroy some of the largest remaining intact forests in the world, negatively impact the health and economic wellbeing of people living in the region, as well as accelerate global climate change.


Citations (14)


... While the combination of agricultural management and climate may explain the enhanced seasonal amplitude of the atmospheric CO 2 , research has yet to explicitly quantify the relative contributions of each. Existing efforts use a synthesis of literature and expert opinion 15 , which is limited by the lack of explicit agricultural management representation in models and therefore quantitative attribution. Additionally, no previous work has disentangled specific contributions of individual agricultural management practices like irrigation and fertilization. ...

Reference:

Agricultural fertilization significantly enhances amplitude of land-atmosphere CO2 exchange
Seasonal CO2 amplitude in northern high latitudes
  • Citing Article
  • October 2024

Nature Reviews Earth & Environment

... In response, some species might expand their geographic ranges toward more favorable conditions or can reduce their habitats into narrow ranges, affecting plant community structure (Konowalik and Kolanowska 2018;Xu et al. 2013). Some plant species have already migrated toward areas with better conditions for survival and reproduction (Feeley et al. 2020) while others have managed to maintain or even expand their ranges despite adverse climate conditions in semi-arid regions (Gelviz-Gelvez et al. 2015;Zhang et al. 2024). Thus, species responses to climate change can vary widely. ...

Less than 4% of dryland areas are projected to desertify despite increased aridity under climate change

... Areas that have undergone firemediated forest loss and species dominance changes have generally failed to return to a composition and structure like that prior to fire, suggesting these changes are persistent (Asselin et al. 2006;Walker et al. 2023). Climate-driven advances in the treeline have been limited and variable Trant & Hermanutz 2014), and do not compensate for fire-mediated forest loss (Burrell et al. 2024;. ...

The predictability of near‐term forest biomass change in boreal North America
  • Citing Article
  • January 2024

... For example, images obtained from global-coverage satellites utilized to detect burned areas typically have a spatial resolution of several hundred meters 14 , implying a systematic underestimation bias due to undetected small fires, especially over the tropics [15][16][17][18] . Moreover, highintensity fires burn litter and organic horizons of soil, which poses challenges 19 for remote sensing detection and accurate estimation of fuel consumption. Further, peat burning from smoldering processes occurs in natural and disturbed peat in the Arctic and tropics, which is extremely difficult to detect via burned area observations. ...

Burned area and carbon emissions across northwestern boreal North America from 2001–2019

... Our fire carbon emission estimate for boreal ecosystems (CO 2 and CH 4 , 123 TgC yr 1 ) is slightly lower than that of 142 Tg CO 2 -C yr 1 previously reported by Veraverbeke et al. (2021). Using GFED4s data, our estimate might underestimate fire CO 2 emissions, as shown in Potter et al. (2022), where GFED4s emissions were 36% lower than those obtained using the ABoVE-FED data-driven product. ...

Burned Area and Carbon Emissions Across Northwestern Boreal North America from 2001–2019

... Furthermore, because it is essential to accurately estimate the time of fire spread cessation, data fusion of high spatial resolution data (e.g., Landsat, Sentinel-2) with high temporal resolution data (e.g., MODIS and VIIRS) will be essential to improve future perimeter attribution (Boschetti et al. 2015). Finally, future investigations could also incorporate measures of fire severity in order to separate surface-and stand-replacing crown fires (Burrell et al. 2022;Kharuk et al. 2016). These estimates could then be linked to fuel consumption and recovery after fire. ...

Climate change, fire return intervals and the growing risk of permanent forest loss in boreal Eurasia

The Science of The Total Environment

... Our study also highlights the dominance of wildfire as a driver of forest loss, in line with findings from other studies [80]. Similarly, although wildfires play an important role in fire-adapted temperate and boreal forests, increasing fire frequency and severitydriven in part by climate change -can impede their ability to recover [10]. In non-fire adapted ecosystems, such as the humid tropics, fires can lead to forest degradation [7]. ...

Post-fire Recruitment Failure as a Driver of Forest to Non-forest Ecosystem Shifts in Boreal Regions
  • Citing Chapter
  • June 2021

... Some researchers have found a significant correlation between the vegetation restoration following wildfires and meteorological factors such as precipitation and temperature [28][29][30][31]. The topography (e.g., slope, altitude, and elevation) of a forest burnt area may influence surface evapotranspiration following a wildfire, which can also impact the rate of vegetation restoration in various spatial patterns [32][33][34][35]. ...

Climate Variability May Delay Post-Fire Recovery of Boreal Forest in Southern Siberia, Russia

... Though human activities play a significant role in deriving the increase in NDVI, it is climate change that casts a more profound shadow over human efforts to enhance vegetation activities (Zhao et al., 2023). Basically, this may be due to the temporal relationship between vegetation and precipitation on a yearly basis at the local scale is constrained by the composition and function of the local plant community (Ukkola et al., 2021). Overall, the result underscores the intricate interplay between human-induced vegetation dynamics and climate variables. ...

Annual precipitation explains variability in dryland vegetation greenness globally but not locally
  • Citing Article
  • June 2021

Global Change Biology

... Drylands span all continents, covering approximately 40% of the world's land surface, and are home to around 38% of the Earth's population (Burrell et al., 2020). These regions, characterized by low but highly variable precipitation, are particularly vulnerable to the impacts of climate change, including increased temperatures, altered precipitation patterns, and heightened risk of drought and desertification (Stavi et al., 2021;Thalheimer et al., 2021). ...

Anthropogenic climate change has driven over 5 million km2 of drylands towards desertification