TY - JOUR
T1 - Controls on winter ecosystem respiration in temperate and boreal ecosystems
AU - Wang, T.
AU - Ciais, P.
AU - Piao, S. L.
AU - Ottlé, C.
AU - Brender, P.
AU - Maignan, F.
AU - Arain, A.
AU - Cescatti, A.
AU - Gianelle, D.
AU - Gough, C.
AU - Gu, L.
AU - Lafleur, P.
AU - Laurila, T.
AU - Marcolla, B.
AU - Margolis, H.
AU - Montagnani, L.
AU - Moors, E.
AU - Saigusa, N.
AU - Vesala, T.
AU - Wohlfahrt, G.
AU - Koven, C.
AU - Black, A.
AU - Dellwik, E.
AU - Don, A.
AU - Hollinger, D.
AU - Knohl, A.
AU - Monson, R.
AU - Munger, J.
AU - Suyker, A.
AU - Varlagin, A.
AU - Verma, S.
N1 - Funding Information:
∗Speaker. †The speaker is supported by the China Postdoctoral Science Foundation under Grant No. 2016M601134, and the International Postdoctoral Exchange Fellowship Program between the Office of the National Administrative Committee of Postdoctoral Researchers of China (ONACPR) and DESY
PY - 2011
Y1 - 2011
N2 - Winter CO 2 fluxes represent an important component of the annual carbon budget in northern ecosystems. Understanding winter respiration processes and their responses to climate change is also central to our ability to assess terrestrial carbon cycle and climate feedbacks in the future. However, the factors influencing the spatial and temporal patterns of winter ecosystem respiration (R eco) of northern ecosystems are poorly understood. For this reason, we analyzed eddy covariance flux data from 57 ecosystem sites ranging from ∼35° N to ∼70° N. Deciduous forests were characterized by the highest winter R eco rates (0.90 ± 0.39 g C m -2 d -1), when winter is defined as the period during which daily air temperature remains below 0 °C. By contrast, arctic wetlands had the lowest winter R eco rates (0.02 ± 0.02 g C m -2 d -1). Mixed forests, evergreen needle-leaved forests, grasslands, croplands and boreal wetlands were characterized by intermediate winter R eco rates (g C m -2 d -1) of 0.70(±0.33), 0.60(±0.38), 0.62(±0.43), 0.49(±0.22) and 0.27(±0.08), respectively. Our cross site analysis showed that winter air (T air) and soil (T soil) temperature played a dominating role in determining the spatial patterns of winter R eco in both forest and managed ecosystems (grasslands and croplands). Besides temperature, the seasonal amplitude of the leaf area index (LAI), inferred from satellite observation, or growing season gross primary productivity, which we use here as a proxy for the amount of recent carbon available for R eco in the subsequent winter, played a marginal role in winter CO 2 emissions from forest ecosystems. We found that winter R eco sensitivity to temperature variation across space (Q S) was higher than the one over time (interannual, Q T). This can be expected because Q S not only accounts for climate gradients across sites but also for (positively correlated) the spatial variability of substrate quantity. Thus, if the models estimate future warming impacts on R eco based on Q S rather than Q T, this could overestimate the impact of temperature changes.
AB - Winter CO 2 fluxes represent an important component of the annual carbon budget in northern ecosystems. Understanding winter respiration processes and their responses to climate change is also central to our ability to assess terrestrial carbon cycle and climate feedbacks in the future. However, the factors influencing the spatial and temporal patterns of winter ecosystem respiration (R eco) of northern ecosystems are poorly understood. For this reason, we analyzed eddy covariance flux data from 57 ecosystem sites ranging from ∼35° N to ∼70° N. Deciduous forests were characterized by the highest winter R eco rates (0.90 ± 0.39 g C m -2 d -1), when winter is defined as the period during which daily air temperature remains below 0 °C. By contrast, arctic wetlands had the lowest winter R eco rates (0.02 ± 0.02 g C m -2 d -1). Mixed forests, evergreen needle-leaved forests, grasslands, croplands and boreal wetlands were characterized by intermediate winter R eco rates (g C m -2 d -1) of 0.70(±0.33), 0.60(±0.38), 0.62(±0.43), 0.49(±0.22) and 0.27(±0.08), respectively. Our cross site analysis showed that winter air (T air) and soil (T soil) temperature played a dominating role in determining the spatial patterns of winter R eco in both forest and managed ecosystems (grasslands and croplands). Besides temperature, the seasonal amplitude of the leaf area index (LAI), inferred from satellite observation, or growing season gross primary productivity, which we use here as a proxy for the amount of recent carbon available for R eco in the subsequent winter, played a marginal role in winter CO 2 emissions from forest ecosystems. We found that winter R eco sensitivity to temperature variation across space (Q S) was higher than the one over time (interannual, Q T). This can be expected because Q S not only accounts for climate gradients across sites but also for (positively correlated) the spatial variability of substrate quantity. Thus, if the models estimate future warming impacts on R eco based on Q S rather than Q T, this could overestimate the impact of temperature changes.
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U2 - 10.5194/bg-8-2009-2011
DO - 10.5194/bg-8-2009-2011
M3 - Article
AN - SCOPUS:79960767036
SN - 1726-4170
VL - 8
SP - 2009
EP - 2025
JO - Biogeosciences
JF - Biogeosciences
IS - 7
ER -