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Pollutant dispersal and stability in a severely polluted floodplain: A case study in the Litavka River, Czech Republic

Identifikátory výsledku

  • Kód výsledku v IS VaVaI

    <a href="https://www.isvavai.cz/riv?ss=detail&h=RIV%2F00216208%3A11310%2F15%3A10312454" target="_blank" >RIV/00216208:11310/15:10312454 - isvavai.cz</a>

  • Nalezeny alternativní kódy

    RIV/61388980:_____/15:00445241 RIV/44555601:13520/15:43886744

  • Výsledek na webu

    <a href="http://dx.doi.org/10.1016/j.gexplo.2015.05.006" target="_blank" >http://dx.doi.org/10.1016/j.gexplo.2015.05.006</a>

  • DOI - Digital Object Identifier

    <a href="http://dx.doi.org/10.1016/j.gexplo.2015.05.006" target="_blank" >10.1016/j.gexplo.2015.05.006</a>

Alternativní jazyky

  • Jazyk výsledku

    angličtina

  • Název v původním jazyce

    Pollutant dispersal and stability in a severely polluted floodplain: A case study in the Litavka River, Czech Republic

  • Popis výsledku v původním jazyce

    The fluvial system of the Litavka River in the Czech Republic has been severely polluted by polymetallic ore mining and smelting that occurred mainly between the 1780s and 1970s. To decipher the mechanisms of the pollution transport pathways, we analysed river valley sediments from river headwaters upstream from the ore district through mining and smelting areas to downstream sites. We sampled recently inundated areas as well as sites just outside 100-year (Q100) inundation. In the river valley, it was necessary to distinguish anthropogenic alluvium (AA) floodplain sediments produced due to ore mining and processing. AA had changed K/Rb signal ratios (measured by energy dispersive X-ray fluorescence, ED XRF); Pb and Zn pollution; and 206Pb/207Pb isotope ratios. The main part of the primary pollution of the river system was deposited in 19th century and during the first half of the 20th century, a few kilometres far downstream from the primary pollution sources (waste deposits of ore mining processing and the smelter). AA has a Zn/Pb ratio of ~1.5 and a local enrichment factor (LEF) of up to ~160 for Pb and up to ~130 for Zn. The floodplain further downstream has received diluted primary pollution with the same Zn/Pb ratio and a LEF of up to ~80 for Pb and up to ~50 for Zn. Much less severe pollution is recognised in fallout-polluted soils at the river valley edges outside Q100 (Zn/Pb ~0.9, LEF ~7 for Pb and LEF ~2 for Zn). The secondary pollution currently exported from the watershed and floodplain is substantially enriched in Zn (Zn/Pb ~1.5-6). That is obviously a consequence of the higher mobility of Zn in the temporary reservoirs in the mining and smelting area and floodplain.

  • Název v anglickém jazyce

    Pollutant dispersal and stability in a severely polluted floodplain: A case study in the Litavka River, Czech Republic

  • Popis výsledku anglicky

    The fluvial system of the Litavka River in the Czech Republic has been severely polluted by polymetallic ore mining and smelting that occurred mainly between the 1780s and 1970s. To decipher the mechanisms of the pollution transport pathways, we analysed river valley sediments from river headwaters upstream from the ore district through mining and smelting areas to downstream sites. We sampled recently inundated areas as well as sites just outside 100-year (Q100) inundation. In the river valley, it was necessary to distinguish anthropogenic alluvium (AA) floodplain sediments produced due to ore mining and processing. AA had changed K/Rb signal ratios (measured by energy dispersive X-ray fluorescence, ED XRF); Pb and Zn pollution; and 206Pb/207Pb isotope ratios. The main part of the primary pollution of the river system was deposited in 19th century and during the first half of the 20th century, a few kilometres far downstream from the primary pollution sources (waste deposits of ore mining processing and the smelter). AA has a Zn/Pb ratio of ~1.5 and a local enrichment factor (LEF) of up to ~160 for Pb and up to ~130 for Zn. The floodplain further downstream has received diluted primary pollution with the same Zn/Pb ratio and a LEF of up to ~80 for Pb and up to ~50 for Zn. Much less severe pollution is recognised in fallout-polluted soils at the river valley edges outside Q100 (Zn/Pb ~0.9, LEF ~7 for Pb and LEF ~2 for Zn). The secondary pollution currently exported from the watershed and floodplain is substantially enriched in Zn (Zn/Pb ~1.5-6). That is obviously a consequence of the higher mobility of Zn in the temporary reservoirs in the mining and smelting area and floodplain.

Klasifikace

  • Druh

    J<sub>imp</sub> - Článek v periodiku v databázi Web of Science

  • CEP obor

  • OECD FORD obor

    10505 - Geology

Návaznosti výsledku

  • Projekt

  • Návaznosti

    S - Specificky vyzkum na vysokych skolach<br>I - Institucionalni podpora na dlouhodoby koncepcni rozvoj vyzkumne organizace

Ostatní

  • Rok uplatnění

    2015

  • 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 Geochemical Exploration

  • ISSN

    0375-6742

  • e-ISSN

  • Svazek periodika

    156

  • Číslo periodika v rámci svazku

    SEPTEMBER

  • Stát vydavatele periodika

    NL - Nizozemsko

  • Počet stran výsledku

    14

  • Strana od-do

    131-144

  • Kód UT WoS článku

    000358098700010

  • EID výsledku v databázi Scopus

    2-s2.0-84930753455