Doick Kieron J, Burauel Peter, Jones Kevin C, Semple Kirk T
Department of Environmental Science, Institute of Environmental and Natural Sciences, Lancaster University, Lancaster, LA1 4YQ, United Kingdom.
Environ Sci Technol. 2005 Sep 1;39(17):6575-83. doi: 10.1021/es050523c.
Organic matter is considered to be the single most importantfactor limiting availability and mobility of persistent organic pollutants (POPs) in soil. This study aimed to characterize the distribution of 14C-PCB (congeners 28 and 52) and 14C-PAH (fluoranthene and benzo[a]pyrene) residues in an Orthic Luvisol soil obtained from two lysimeter studies initiated in 1990 at the Agrosphere Institute (Forschungszentrum Jülich GmbH, Germany). The lysimeter soils contained a low-density OM fraction, isolated during soil washing, which contained a significant fraction (3-12%) of the total 14C-activity. Soils were also fractionated according to three particle sizes: >20, 20-2, and <2 microm. Relative affinity values of 14C-activity for the different particle sizes varied in the order 20-2 microm > (<2 microm) approximately (>20 microm) for the PCBs. Relative affinity values of 14C-activity for the different particle sizes varied in the order 20-2 microm > (<2 microm) > (>20 microm) for the PAHs. The distribution of 14C-PCB or 14C-PAH residues in the organic and inorganic matrixes of the particle-size fractions was determined using methyl isobutyl ketone (MIBK). 14C-PCB and 14C-PAH-associated activities were primarily located in the humin fraction of the 20-2 and <2 microm particle-size fractions of the soil. A small fraction was associated with the fulvic and humic acid fractions; these were quantitatively more important for the PAHs than the PCBs. There appeared to be a high degree of association of 14C-activity with the mineral fraction following MIBK separation of the humic fractions, ranging between 8 and 52% for 14C-PCBs and 57-80% for 14C-PAHs. The mineral (inorganic) component of the soils apparently played a significant (previously unreported) role in the sequestration of both PCBs 28 and 52 and the PAHs fluoranthene and benzo[a]pyrene.
有机物被认为是限制持久性有机污染物(POPs)在土壤中有效性和迁移性的唯一最重要因素。本研究旨在表征1990年在德国尤利希研究中心农业地球科学研究所启动的两项蒸渗仪研究中获得的一种雏形淋溶土中14C-多氯联苯(同族体28和52)和14C-多环芳烃(荧蒽和苯并[a]芘)残留的分布情况。蒸渗仪土壤含有在土壤洗涤过程中分离出的低密度有机物质部分,该部分含有总14C活性的很大一部分(3-12%)。土壤还根据三种粒径进行了分级:>20、20-2和<2微米。对于多氯联苯,不同粒径的14C活性相对亲和值的变化顺序为20-2微米>(<2微米)≈(>20微米)。对于多环芳烃,不同粒径的14C活性相对亲和值的变化顺序为20-2微米>(<2微米)>(>20微米)。使用甲基异丁基酮(MIBK)测定了粒径分级的有机和无机基质中14C-多氯联苯或14C-多环芳烃残留的分布。与14C-多氯联苯和14C-多环芳烃相关的活性主要位于土壤20-2和<2微米粒径分级的腐殖质部分。一小部分与富里酸和腐殖酸部分相关;这些对于多环芳烃在数量上比多氯联苯更重要。在腐殖质部分经MIBK分离后,14C活性与矿物部分似乎有高度的相关性,14C-多氯联苯的相关性在8%至52%之间,14C-多环芳烃的相关性在57%-80%之间。土壤的矿物(无机)成分显然在多氯联苯28和52以及多环芳烃荧蒽和苯并[a]芘的固存中发挥了重要作用(此前未报道)。