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Thermally-induced release of arsenic from minerals and phases relevant to polluted natural systems affected by wildfires

Identifikátory výsledku

  • Kód výsledku v IS VaVaI

    <a href="https://www.isvavai.cz/riv?ss=detail&h=RIV%2F67985831%3A_____%2F25%3A00617939" target="_blank" >RIV/67985831:_____/25:00617939 - isvavai.cz</a>

  • Nalezeny alternativní kódy

    RIV/00216208:11310/25:10494624

  • Výsledek na webu

    <a href="https://www.sciencedirect.com/science/article/pii/S0883292725000411?via%3Dihub" target="_blank" >https://www.sciencedirect.com/science/article/pii/S0883292725000411?via%3Dihub</a>

  • DOI - Digital Object Identifier

    <a href="http://dx.doi.org/10.1016/j.apgeochem.2025.106318" target="_blank" >10.1016/j.apgeochem.2025.106318</a>

Alternativní jazyky

  • Jazyk výsledku

    angličtina

  • Název v původním jazyce

    Thermally-induced release of arsenic from minerals and phases relevant to polluted natural systems affected by wildfires

  • Popis výsledku v původním jazyce

    Fire-induced arsenic (As) emission from contaminated biomass or soil is dependent on its solid-phase speciation. To quantify the nature of this release, environmentally relevant As-bearing compounds (sulfides, sulfosalts, As-oxides, arsenates, As-doped Fe-oxyhydroxides and organic material) were experimentally heated with a linear temperature increase (25–800 °C) and simultaneous detection of As and other emitted elements. Organic As-bearing materials (fungi, dimethylarsinic acid-DMAA) exhibited the peak of As release at the lowest temperatures of 275–350 °C, followed by arsenolite (As2O3) with the maximum As emission at ∼400 °C. Realgar (As4S4) and orpiment (As2S3) exhibited the maximum As release at 425–450 °C, while enargite (Cu3AsS4) and arsenopyrite (FeAsS) released As at much higher temperatures with emission peaks at ∼625 and > 725 °C, respectively. Similarly, As-bearing Fe-oxyhydroxides emitted As at temperatures exceeding 650 °C. Arsenic emission from arsenates was rather variable and peaked at ∼700 °C for conichalcite [CaCu(AsO4)(OH)], and scorodite (FeAsO4·2H2O), while for mimetite [Pb5(AsO4)3Cl], it peaked towards the upper limit of the temperature range. These results suggest that typical low intensity wildland fires would affect only organically bound As and arsenolite, while higher intensity wildland fires could cause the redistribution of As from all studied phases, thereby posing a significant environmental risk of As redistribution beyond contaminated sites.

  • Název v anglickém jazyce

    Thermally-induced release of arsenic from minerals and phases relevant to polluted natural systems affected by wildfires

  • Popis výsledku anglicky

    Fire-induced arsenic (As) emission from contaminated biomass or soil is dependent on its solid-phase speciation. To quantify the nature of this release, environmentally relevant As-bearing compounds (sulfides, sulfosalts, As-oxides, arsenates, As-doped Fe-oxyhydroxides and organic material) were experimentally heated with a linear temperature increase (25–800 °C) and simultaneous detection of As and other emitted elements. Organic As-bearing materials (fungi, dimethylarsinic acid-DMAA) exhibited the peak of As release at the lowest temperatures of 275–350 °C, followed by arsenolite (As2O3) with the maximum As emission at ∼400 °C. Realgar (As4S4) and orpiment (As2S3) exhibited the maximum As release at 425–450 °C, while enargite (Cu3AsS4) and arsenopyrite (FeAsS) released As at much higher temperatures with emission peaks at ∼625 and > 725 °C, respectively. Similarly, As-bearing Fe-oxyhydroxides emitted As at temperatures exceeding 650 °C. Arsenic emission from arsenates was rather variable and peaked at ∼700 °C for conichalcite [CaCu(AsO4)(OH)], and scorodite (FeAsO4·2H2O), while for mimetite [Pb5(AsO4)3Cl], it peaked towards the upper limit of the temperature range. These results suggest that typical low intensity wildland fires would affect only organically bound As and arsenolite, while higher intensity wildland fires could cause the redistribution of As from all studied phases, thereby posing a significant environmental risk of As redistribution beyond contaminated sites.

Klasifikace

  • Druh

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

  • CEP obor

  • OECD FORD obor

    10511 - Environmental sciences (social aspects to be 5.7)

Návaznosti výsledku

  • Projekt

    Výsledek vznikl pri realizaci vícero projektů. Více informací v záložce Projekty.

  • Návaznosti

    I - Institucionalni podpora na dlouhodoby koncepcni rozvoj vyzkumne organizace

Ostatní

  • Rok uplatnění

    2025

  • Kód důvěrnosti údajů

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

Údaje specifické pro druh výsledku

  • Název periodika

    Applied Geochemistry

  • ISSN

    0883-2927

  • e-ISSN

    1872-9134

  • Svazek periodika

    182

  • Číslo periodika v rámci svazku

    March

  • Stát vydavatele periodika

    GB - Spojené království Velké Británie a Severního Irska

  • Počet stran výsledku

    9

  • Strana od-do

    106318

  • Kód UT WoS článku

    001430935100001

  • EID výsledku v databázi Scopus

    2-s2.0-85217977562