Seasonal Variations of Dissolved Iron Concentration in Active Layer and Rivers in Permafrost Areas, Russian Far East

Dissolved iron (dFe) in boreal rivers may play an important role in primary production in high-latitude oceans. However, iron behavior in soils and dFe discharge mechanism from soil to the rivers are poorly understood. To better understand iron dynamics on the watershed scale, we observed the season...

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Published in:Water
Main Authors: Yuto Tashiro, Muneoki Yoh, Takayuki Shiraiwa, Takeo Onishi, Vladimir Shesterkin, Vladimir Kim
Format: Text
Language:English
Published: Multidisciplinary Digital Publishing Institute 2020
Subjects:
Online Access:https://doi.org/10.3390/w12092579
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spelling ftmdpi:oai:mdpi.com:/2073-4441/12/9/2579/ 2023-08-20T04:09:10+02:00 Seasonal Variations of Dissolved Iron Concentration in Active Layer and Rivers in Permafrost Areas, Russian Far East Yuto Tashiro Muneoki Yoh Takayuki Shiraiwa Takeo Onishi Vladimir Shesterkin Vladimir Kim agris 2020-09-15 application/pdf https://doi.org/10.3390/w12092579 EN eng Multidisciplinary Digital Publishing Institute Water Quality and Contamination https://dx.doi.org/10.3390/w12092579 https://creativecommons.org/licenses/by/4.0/ Water; Volume 12; Issue 9; Pages: 2579 permafrost wetland dissolved iron Amur river Text 2020 ftmdpi https://doi.org/10.3390/w12092579 2023-08-01T00:07:09Z Dissolved iron (dFe) in boreal rivers may play an important role in primary production in high-latitude oceans. However, iron behavior in soils and dFe discharge mechanism from soil to the rivers are poorly understood. To better understand iron dynamics on the watershed scale, we observed the seasonal changes in dFe and Dissolved Organic Carbon (DOC) concentrations in the river as well as dFe concentration in soil pore waters in permafrost watershed from May to October. During snowmelt season, high dFe production (1.38–4.70 mg L−1) was observed in surface soil pore waters. Correspondingly, riverine dFe and DOC concentrations increased to 1.10 mg L−1 and 32.3 mg L−1, and both were the highest in the year. After spring floods, riverine dFe and DOC concentrations decreased to 0.15 mg L−1 and 7.62 mg L−1, and dFe concentration in surface soil pore waters also decreased to 0.20–1.28 mg L−1. In late July, riverine dFe and DOC concentrations increased to 0.33 mg L−1 and 23.6 mg L−1 in response to heavy rainfall. In August and September, considerable increases in dFe concentrations (2.00–6.90 mg L−1) were observed in subsurface soil pore waters, probably because infiltrated rainwater developed reducing conditions. This dFe production was confirmed widely in permafrost wetlands in valley areas. Overall, permafrost wetlands in valley areas are hotspots of dFe production and greatly contribute to dFe and DOC discharge to rivers, especially during snowmelt and rainy seasons. Text permafrost MDPI Open Access Publishing Water 12 9 2579
institution Open Polar
collection MDPI Open Access Publishing
op_collection_id ftmdpi
language English
topic permafrost
wetland
dissolved iron
Amur river
spellingShingle permafrost
wetland
dissolved iron
Amur river
Yuto Tashiro
Muneoki Yoh
Takayuki Shiraiwa
Takeo Onishi
Vladimir Shesterkin
Vladimir Kim
Seasonal Variations of Dissolved Iron Concentration in Active Layer and Rivers in Permafrost Areas, Russian Far East
topic_facet permafrost
wetland
dissolved iron
Amur river
description Dissolved iron (dFe) in boreal rivers may play an important role in primary production in high-latitude oceans. However, iron behavior in soils and dFe discharge mechanism from soil to the rivers are poorly understood. To better understand iron dynamics on the watershed scale, we observed the seasonal changes in dFe and Dissolved Organic Carbon (DOC) concentrations in the river as well as dFe concentration in soil pore waters in permafrost watershed from May to October. During snowmelt season, high dFe production (1.38–4.70 mg L−1) was observed in surface soil pore waters. Correspondingly, riverine dFe and DOC concentrations increased to 1.10 mg L−1 and 32.3 mg L−1, and both were the highest in the year. After spring floods, riverine dFe and DOC concentrations decreased to 0.15 mg L−1 and 7.62 mg L−1, and dFe concentration in surface soil pore waters also decreased to 0.20–1.28 mg L−1. In late July, riverine dFe and DOC concentrations increased to 0.33 mg L−1 and 23.6 mg L−1 in response to heavy rainfall. In August and September, considerable increases in dFe concentrations (2.00–6.90 mg L−1) were observed in subsurface soil pore waters, probably because infiltrated rainwater developed reducing conditions. This dFe production was confirmed widely in permafrost wetlands in valley areas. Overall, permafrost wetlands in valley areas are hotspots of dFe production and greatly contribute to dFe and DOC discharge to rivers, especially during snowmelt and rainy seasons.
format Text
author Yuto Tashiro
Muneoki Yoh
Takayuki Shiraiwa
Takeo Onishi
Vladimir Shesterkin
Vladimir Kim
author_facet Yuto Tashiro
Muneoki Yoh
Takayuki Shiraiwa
Takeo Onishi
Vladimir Shesterkin
Vladimir Kim
author_sort Yuto Tashiro
title Seasonal Variations of Dissolved Iron Concentration in Active Layer and Rivers in Permafrost Areas, Russian Far East
title_short Seasonal Variations of Dissolved Iron Concentration in Active Layer and Rivers in Permafrost Areas, Russian Far East
title_full Seasonal Variations of Dissolved Iron Concentration in Active Layer and Rivers in Permafrost Areas, Russian Far East
title_fullStr Seasonal Variations of Dissolved Iron Concentration in Active Layer and Rivers in Permafrost Areas, Russian Far East
title_full_unstemmed Seasonal Variations of Dissolved Iron Concentration in Active Layer and Rivers in Permafrost Areas, Russian Far East
title_sort seasonal variations of dissolved iron concentration in active layer and rivers in permafrost areas, russian far east
publisher Multidisciplinary Digital Publishing Institute
publishDate 2020
url https://doi.org/10.3390/w12092579
op_coverage agris
genre permafrost
genre_facet permafrost
op_source Water; Volume 12; Issue 9; Pages: 2579
op_relation Water Quality and Contamination
https://dx.doi.org/10.3390/w12092579
op_rights https://creativecommons.org/licenses/by/4.0/
op_doi https://doi.org/10.3390/w12092579
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