Näytä suppeat kuvailutiedot

dc.contributor.authorJylhä‐Ollila, Maija
dc.contributor.authorLaine‐Kaulio, Hanne
dc.contributor.authorSchilder, Jos
dc.contributor.authorNiinikoski‐Fuβwinkel, Paula
dc.contributor.authorKekäläinen, Timo
dc.contributor.authorJänis, Janne
dc.contributor.authorKoivusalo, Harri
dc.date.accessioned2021-02-18T08:15:59Z
dc.date.available2021-02-18T08:15:59Z
dc.date.issued2021
dc.identifier.citationJylhä‐Ollila, M., Laine‐Kaulio, H., Schilder, J., Niinikoski‐Fuβwinkel, P., Kekäläinen, T., Jänis, J., & Koivusalo, H. (2021). Carbon budget and molecular structure of natural organic matter in bank infiltrated groundwater. <i>Groundwater</i>, <i>59</i>(5), 644-657. <a href="https://doi.org/10.1111/gwat.13087" target="_blank">https://doi.org/10.1111/gwat.13087</a>
dc.identifier.otherCONVID_51510621
dc.identifier.urihttps://jyx.jyu.fi/handle/123456789/74285
dc.description.abstractManaged aquifer recharge (MAR) provides means to remove natural organic matter (NOM) from surface waters. Recent studies have explored the degree of NOM removal in groundwater. In this study, we further elaborate the NOM removal at a lakeside natural bank infiltration site that functions as a surrogate for MAR. Our objective was to quantify the carbon budget in the aquifer based on concentration measurements of dissolved (in)organic carbon, and the molecular changes in NOM using Fourier transform ion cyclotron resonance mass spectrometry (FT‐ICR MS). According to the carbon budget, only 25% of the dissolved carbon entering the aquifer was organic, and it predominantly originated from lake water. Of the inorganic majority, on average 40% was produced in the vadose zone above the groundwater table, 31% in the lake bank, 22% in the aquifer as a result of degrading organic matter of lake water, and 7% in the lake. Seasonal concentration variations suggested that the lake bank was the main carbon source in the summer, increasing the carbon concentration of infiltrating lake water, i.e., 3.0 mg/L, to 7.9 mg/L. FT‐ICR MS results showed 4960 to 5330 individual compounds in lake and groundwater. NOM removal in the aquifer was selective: the relative abundance of oxygen‐containing species decreased from 75% to 31%, while the relative abundance of sulfur‐containing species increased from 15% to 57%. The average molecular weights of both species remained unchanged. The study highlighted the role of lake bank processes and sulfur‐containing species in groundwater quality.en
dc.format.mimetypeapplication/pdf
dc.languageeng
dc.language.isoeng
dc.publisherWiley-Blackwell
dc.relation.ispartofseriesGroundwater
dc.rightsCC BY-NC 4.0
dc.subject.otherlake-groundwater interaction
dc.subject.othermanaged aquifer recharge
dc.subject.otherdissolved organic matter
dc.subject.othermolecular composition
dc.titleCarbon budget and molecular structure of natural organic matter in bank infiltrated groundwater
dc.typearticle
dc.identifier.urnURN:NBN:fi:jyu-202102181692
dc.contributor.laitosBio- ja ympäristötieteiden laitosfi
dc.contributor.laitosDepartment of Biological and Environmental Scienceen
dc.contributor.oppiaineAkvaattiset tieteetfi
dc.contributor.oppiaineAquatic Sciencesen
dc.type.urihttp://purl.org/eprint/type/JournalArticle
dc.type.coarhttp://purl.org/coar/resource_type/c_2df8fbb1
dc.description.reviewstatuspeerReviewed
dc.format.pagerange644-657
dc.relation.issn0017-467X
dc.relation.numberinseries5
dc.relation.volume59
dc.type.versionacceptedVersion
dc.rights.copyright© 2021 The Authors. Groundwater published by Wiley Periodicals LLC on behalf of National Ground Water Association.
dc.rights.accesslevelopenAccessfi
dc.subject.ysojärvet
dc.subject.ysotekopohjavesi
dc.subject.ysoorgaaninen aines
dc.subject.ysomassaspektrometria
dc.subject.ysopohjavesi
dc.subject.ysovedenpuhdistus
dc.subject.ysoliuennut orgaaninen hiili
dc.subject.ysopintavesi
dc.subject.ysopohjavesialueet
dc.format.contentfulltext
jyx.subject.urihttp://www.yso.fi/onto/yso/p9374
jyx.subject.urihttp://www.yso.fi/onto/yso/p11541
jyx.subject.urihttp://www.yso.fi/onto/yso/p14873
jyx.subject.urihttp://www.yso.fi/onto/yso/p10755
jyx.subject.urihttp://www.yso.fi/onto/yso/p2649
jyx.subject.urihttp://www.yso.fi/onto/yso/p15306
jyx.subject.urihttp://www.yso.fi/onto/yso/p29461
jyx.subject.urihttp://www.yso.fi/onto/yso/p11704
jyx.subject.urihttp://www.yso.fi/onto/yso/p9966
dc.rights.urlhttps://creativecommons.org/licenses/by-nc/4.0/
dc.relation.doi10.1111/gwat.13087
jyx.fundinginformationThis work was supported by the K.H. Renlund Foundation, the Ramboll Foundation, Finnish Cultural Foundation Päijät-Häme Regional Fund, the EU’s Horizon 2020 Research and Innovation Programme (Grant Agreement 731077), Maa- ja vesitekniikan tuki ry, and the Drainage Foundation sr. The FT-ICR MS facility was supported by Biocenter Finland/Biocenter Kuopio and the European Regional Development Fund (Grant A70135).
dc.type.okmA1


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