Mean soil organic carbon stocks by 0–1 and 0–2 m depths intervals for various successional stages (Yng= young, Int= intermediate, DL= drained lake) within four soil landscapes

Figure 7. Mean soil organic carbon stocks by 0–1 and 0–2 m depths intervals for various successional stages (Yng= young, Int= intermediate, DL= drained lake) within four soil landscapes. SD bars are for combined 0–2 intervals and numbers are for sample sizes. Means with the same letter are not signi...

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Main Authors: M Torre Jorgenson, Shur, Yuri, Qianlai Zhuang, Manies, Kristen, Ewing, Stephanie, Wickland, Kim, O'Donnell, Jonathan, Kanevskiy, Mikhail, Harden, Jennifer, Striegl, Robert
Format: Still Image
Language:unknown
Published: IOP Publishing 2013
Subjects:
Ice
Online Access:https://dx.doi.org/10.6084/m9.figshare.1011743.v1
https://iop.figshare.com/articles/figure/_Mean_soil_organic_carbon_stocks_by_0_1_and_0_2_m_depths_intervals_for_various_successional_stages_Y/1011743/1
id ftdatacite:10.6084/m9.figshare.1011743.v1
record_format openpolar
spelling ftdatacite:10.6084/m9.figshare.1011743.v1 2023-05-15T16:36:46+02:00 Mean soil organic carbon stocks by 0–1 and 0–2 m depths intervals for various successional stages (Yng= young, Int= intermediate, DL= drained lake) within four soil landscapes M Torre Jorgenson Shur, Yuri Qianlai Zhuang Manies, Kristen Ewing, Stephanie Wickland, Kim O'Donnell, Jonathan Kanevskiy, Mikhail Harden, Jennifer Striegl, Robert 2013 https://dx.doi.org/10.6084/m9.figshare.1011743.v1 https://iop.figshare.com/articles/figure/_Mean_soil_organic_carbon_stocks_by_0_1_and_0_2_m_depths_intervals_for_various_successional_stages_Y/1011743/1 unknown IOP Publishing https://dx.doi.org/10.6084/m9.figshare.1011743 Creative Commons Attribution 4.0 International https://creativecommons.org/licenses/by/4.0/legalcode cc-by-4.0 CC-BY Environmental Science Image Figure graphic ImageObject 2013 ftdatacite https://doi.org/10.6084/m9.figshare.1011743.v1 https://doi.org/10.6084/m9.figshare.1011743 2021-11-05T12:55:41Z Figure 7. Mean soil organic carbon stocks by 0–1 and 0–2 m depths intervals for various successional stages (Yng= young, Int= intermediate, DL= drained lake) within four soil landscapes. SD bars are for combined 0–2 intervals and numbers are for sample sizes. Means with the same letter are not significantly different ( p > 0.05), no contrast when overall ANOVA results not significant. Abstract The diversity of ecosystems across boreal landscapes, successional changes after disturbance and complicated permafrost histories, present enormous challenges for assessing how vegetation, water and soil carbon may respond to climate change in boreal regions. To address this complexity, we used a chronosequence approach to assess changes in vegetation composition, water storage and soil organic carbon (SOC) stocks along successional gradients within four landscapes: (1) rocky uplands on ice-poor hillside colluvium, (2) silty uplands on extremely ice-rich loess, (3) gravelly–sandy lowlands on ice-poor eolian sand and (4) peaty–silty lowlands on thick ice-rich peat deposits over reworked lowland loess. In rocky uplands, after fire permafrost thawed rapidly due to low ice contents, soils became well drained and SOC stocks decreased slightly. In silty uplands, after fire permafrost persisted, soils remained saturated and SOC decreased slightly. In gravelly–sandy lowlands where permafrost persisted in drier forest soils, loss of deeper permafrost around lakes has allowed recent widespread drainage of lakes that has exposed limnic material with high SOC to aerobic decomposition. In peaty–silty lowlands, 2–4 m of thaw settlement led to fragmented drainage patterns in isolated thermokarst bogs and flooding of soils, and surface soils accumulated new bog peat. We were not able to detect SOC changes in deeper soils, however, due to high variability. Complicated soil stratigraphy revealed that permafrost has repeatedly aggraded and degraded in all landscapes during the Holocene, although in silty uplands only the upper permafrost was affected. Overall, permafrost thaw has led to the reorganization of vegetation, water storage and flow paths, and patterns of SOC accumulation. However, changes have occurred over different timescales among landscapes: over decades in rocky uplands and gravelly–sandy lowlands in response to fire and lake drainage, over decades to centuries in peaty–silty lowlands with a legacy of complicated Holocene changes, and over centuries in silty uplands where ice-rich soil and ecological recovery protect permafrost. Still Image Ice permafrost Thermokarst DataCite Metadata Store (German National Library of Science and Technology)
institution Open Polar
collection DataCite Metadata Store (German National Library of Science and Technology)
op_collection_id ftdatacite
language unknown
topic Environmental Science
spellingShingle Environmental Science
M Torre Jorgenson
Shur, Yuri
Qianlai Zhuang
Manies, Kristen
Ewing, Stephanie
Wickland, Kim
O'Donnell, Jonathan
Kanevskiy, Mikhail
Harden, Jennifer
Striegl, Robert
Mean soil organic carbon stocks by 0–1 and 0–2 m depths intervals for various successional stages (Yng= young, Int= intermediate, DL= drained lake) within four soil landscapes
topic_facet Environmental Science
description Figure 7. Mean soil organic carbon stocks by 0–1 and 0–2 m depths intervals for various successional stages (Yng= young, Int= intermediate, DL= drained lake) within four soil landscapes. SD bars are for combined 0–2 intervals and numbers are for sample sizes. Means with the same letter are not significantly different ( p > 0.05), no contrast when overall ANOVA results not significant. Abstract The diversity of ecosystems across boreal landscapes, successional changes after disturbance and complicated permafrost histories, present enormous challenges for assessing how vegetation, water and soil carbon may respond to climate change in boreal regions. To address this complexity, we used a chronosequence approach to assess changes in vegetation composition, water storage and soil organic carbon (SOC) stocks along successional gradients within four landscapes: (1) rocky uplands on ice-poor hillside colluvium, (2) silty uplands on extremely ice-rich loess, (3) gravelly–sandy lowlands on ice-poor eolian sand and (4) peaty–silty lowlands on thick ice-rich peat deposits over reworked lowland loess. In rocky uplands, after fire permafrost thawed rapidly due to low ice contents, soils became well drained and SOC stocks decreased slightly. In silty uplands, after fire permafrost persisted, soils remained saturated and SOC decreased slightly. In gravelly–sandy lowlands where permafrost persisted in drier forest soils, loss of deeper permafrost around lakes has allowed recent widespread drainage of lakes that has exposed limnic material with high SOC to aerobic decomposition. In peaty–silty lowlands, 2–4 m of thaw settlement led to fragmented drainage patterns in isolated thermokarst bogs and flooding of soils, and surface soils accumulated new bog peat. We were not able to detect SOC changes in deeper soils, however, due to high variability. Complicated soil stratigraphy revealed that permafrost has repeatedly aggraded and degraded in all landscapes during the Holocene, although in silty uplands only the upper permafrost was affected. Overall, permafrost thaw has led to the reorganization of vegetation, water storage and flow paths, and patterns of SOC accumulation. However, changes have occurred over different timescales among landscapes: over decades in rocky uplands and gravelly–sandy lowlands in response to fire and lake drainage, over decades to centuries in peaty–silty lowlands with a legacy of complicated Holocene changes, and over centuries in silty uplands where ice-rich soil and ecological recovery protect permafrost.
format Still Image
author M Torre Jorgenson
Shur, Yuri
Qianlai Zhuang
Manies, Kristen
Ewing, Stephanie
Wickland, Kim
O'Donnell, Jonathan
Kanevskiy, Mikhail
Harden, Jennifer
Striegl, Robert
author_facet M Torre Jorgenson
Shur, Yuri
Qianlai Zhuang
Manies, Kristen
Ewing, Stephanie
Wickland, Kim
O'Donnell, Jonathan
Kanevskiy, Mikhail
Harden, Jennifer
Striegl, Robert
author_sort M Torre Jorgenson
title Mean soil organic carbon stocks by 0–1 and 0–2 m depths intervals for various successional stages (Yng= young, Int= intermediate, DL= drained lake) within four soil landscapes
title_short Mean soil organic carbon stocks by 0–1 and 0–2 m depths intervals for various successional stages (Yng= young, Int= intermediate, DL= drained lake) within four soil landscapes
title_full Mean soil organic carbon stocks by 0–1 and 0–2 m depths intervals for various successional stages (Yng= young, Int= intermediate, DL= drained lake) within four soil landscapes
title_fullStr Mean soil organic carbon stocks by 0–1 and 0–2 m depths intervals for various successional stages (Yng= young, Int= intermediate, DL= drained lake) within four soil landscapes
title_full_unstemmed Mean soil organic carbon stocks by 0–1 and 0–2 m depths intervals for various successional stages (Yng= young, Int= intermediate, DL= drained lake) within four soil landscapes
title_sort mean soil organic carbon stocks by 0–1 and 0–2 m depths intervals for various successional stages (yng= young, int= intermediate, dl= drained lake) within four soil landscapes
publisher IOP Publishing
publishDate 2013
url https://dx.doi.org/10.6084/m9.figshare.1011743.v1
https://iop.figshare.com/articles/figure/_Mean_soil_organic_carbon_stocks_by_0_1_and_0_2_m_depths_intervals_for_various_successional_stages_Y/1011743/1
genre Ice
permafrost
Thermokarst
genre_facet Ice
permafrost
Thermokarst
op_relation https://dx.doi.org/10.6084/m9.figshare.1011743
op_rights Creative Commons Attribution 4.0 International
https://creativecommons.org/licenses/by/4.0/legalcode
cc-by-4.0
op_rightsnorm CC-BY
op_doi https://doi.org/10.6084/m9.figshare.1011743.v1
https://doi.org/10.6084/m9.figshare.1011743
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