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Long-term dynamics of watershed leaching and lake sediment sequestration of rare earth elements following deglaciation of two mountain watersheds.

Identifikátory výsledku

  • Kód výsledku v IS VaVaI

    <a href="https://www.isvavai.cz/riv?ss=detail&h=RIV%2F60077344%3A_____%2F16%3A00459979" target="_blank" >RIV/60077344:_____/16:00459979 - isvavai.cz</a>

  • Výsledek na webu

    <a href="http://dx.doi.org/10.1007/s10933-015-9872-0" target="_blank" >http://dx.doi.org/10.1007/s10933-015-9872-0</a>

  • DOI - Digital Object Identifier

    <a href="http://dx.doi.org/10.1007/s10933-015-9872-0" target="_blank" >10.1007/s10933-015-9872-0</a>

Alternativní jazyky

  • Jazyk výsledku

    angličtina

  • Název v původním jazyce

    Long-term dynamics of watershed leaching and lake sediment sequestration of rare earth elements following deglaciation of two mountain watersheds.

  • Popis výsledku v původním jazyce

    Sediment cores from Sargent Mountain Pond (SMP), Maine, USA and Plešné Lake (PL), Czech Republic, record the entire post-glacial terrestrial vegetation and chemical dynamics of the watershed and lake from 16,600 and 14,600 Cal Yr BP, respectively, to the present. Total rare earth element (REE) concentrations and fluxes to the sediment declined from deglaciation until forest developed prior to the Younger Dryas (YD) (12,600–11,600 Cal Yr BP) at SMP, and immediately after the YD at PL, peaked in value just after the YD, and then declined to the present. Before the YD, REE concentrations were dominated by detrital, soluble apatite. Weathering of apatite contributed the phosphorus (P) sequestered in the lake sediment. After the YD, REE concentrations and fluxes behave coherently with NaOH-extractable aluminum (Al) and P after forestation in each catchment. Concentrations of extractable REEs, P, and Al peak after the YD and decline coherently to the present. After afforestation and development of organic-rich forest soils, concentrations of dissolved organic carbon (DOC) in soil water and runoff increased. Concurrently, the weathering of apatite released phosphate and Ca to runoff, raising pH about 8. The soil DOC complexed with and mobilized Al and REEs, which were transported to the lakes in runoff. There, photooxidation of the Al–DOC and REE–DOC complexes caused release of ionic, inorganic Al and REEs, precipitation of Al hydroxide in the higher-pH environment, adsorption of REEs and phosphate by the Al hydroxide, and irreversible sedimentation. REE concentrations and fluxes declined from the YD to the present because the apatite was progressively depleted in the soil by weathering, while REEs were increasingly retained by secondary Al and Fe hydroxides in the soil.

  • Název v anglickém jazyce

    Long-term dynamics of watershed leaching and lake sediment sequestration of rare earth elements following deglaciation of two mountain watersheds.

  • Popis výsledku anglicky

    Sediment cores from Sargent Mountain Pond (SMP), Maine, USA and Plešné Lake (PL), Czech Republic, record the entire post-glacial terrestrial vegetation and chemical dynamics of the watershed and lake from 16,600 and 14,600 Cal Yr BP, respectively, to the present. Total rare earth element (REE) concentrations and fluxes to the sediment declined from deglaciation until forest developed prior to the Younger Dryas (YD) (12,600–11,600 Cal Yr BP) at SMP, and immediately after the YD at PL, peaked in value just after the YD, and then declined to the present. Before the YD, REE concentrations were dominated by detrital, soluble apatite. Weathering of apatite contributed the phosphorus (P) sequestered in the lake sediment. After the YD, REE concentrations and fluxes behave coherently with NaOH-extractable aluminum (Al) and P after forestation in each catchment. Concentrations of extractable REEs, P, and Al peak after the YD and decline coherently to the present. After afforestation and development of organic-rich forest soils, concentrations of dissolved organic carbon (DOC) in soil water and runoff increased. Concurrently, the weathering of apatite released phosphate and Ca to runoff, raising pH about 8. The soil DOC complexed with and mobilized Al and REEs, which were transported to the lakes in runoff. There, photooxidation of the Al–DOC and REE–DOC complexes caused release of ionic, inorganic Al and REEs, precipitation of Al hydroxide in the higher-pH environment, adsorption of REEs and phosphate by the Al hydroxide, and irreversible sedimentation. REE concentrations and fluxes declined from the YD to the present because the apatite was progressively depleted in the soil by weathering, while REEs were increasingly retained by secondary Al and Fe hydroxides in the soil.

Klasifikace

  • Druh

    J<sub>x</sub> - Nezařazeno - Článek v odborném periodiku (Jimp, Jsc a Jost)

  • CEP obor

    DJ - Znečištění a kontrola vody

  • OECD FORD obor

Návaznosti výsledku

  • Projekt

  • Návaznosti

    I - Institucionalni podpora na dlouhodoby koncepcni rozvoj vyzkumne organizace

Ostatní

  • Rok uplatnění

    2016

  • Kód důvěrnosti údajů

    S - Úplné a pravdivé údaje o projektu nepodléhají ochraně podle zvláštních právních předpisů

Údaje specifické pro druh výsledku

  • Název periodika

    Journal of Paleolimnology

  • ISSN

    0921-2728

  • e-ISSN

  • Svazek periodika

    55

  • Číslo periodika v rámci svazku

    3

  • Stát vydavatele periodika

    NL - Nizozemsko

  • Počet stran výsledku

    14

  • Strana od-do

    209-222

  • Kód UT WoS článku

    000373304100002

  • EID výsledku v databázi Scopus

    2-s2.0-84959142976