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A POTENTIAL LINK BETWEEN THE TURNOVER OF SOIL ORGANIC MATTER AND THE RELEASE OF AGED ORGANIC CONTAMINANTS

机译:土壤有机物的周转与老化有机污染物释放之间的潜在联系

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摘要

Soil column experiments were conducted to investigate the release of aged organic contaminants (adsorbable organo-halogens, [AOX]) and the potential effects of microbial turnover of soil organic matter onto the contaminant release from two different soils of former wastewater infiltration sites. Under reference conditions, the total carbon flux ranged from 6 to 9 mg/kg/ d from the two soils. More than 92% of it was due to mineralization (CO_2) and below 8% to the dissolved organic carbon (DOC) in the column effluent. Despite very different organohalogen levels in the two soils, the fluxes of AOX were similar (1 μg/kg/d). Microbial activity was altered by changing temperature and the solution pH and by drying. In all experiments where increased microbial respiration (CO_2 production) was observed, the release of organic contaminants in the column effluent also increased. Fluxes of nickel, zinc, and phosphate showed a completely different pattern, suggesting that their retention in soil is determined by chemical parameters. A linear correlation analysis provided clear evidence that AOX and DOC fluxes are closely linked to each other. However, the superimposition of abiotic and biotic processes in the soils did not allow a causal relation to be established between the mineralization of soil organic matter and the release of organic contaminants sequestered in the soil. Our findings suggest that microbial activity may have a significant impact on the extent to which contaminated soils may act as a source of persistent organic pollutants.
机译:进行了土壤柱实验,以调查老化的有机污染物(可吸收的有机卤素,[AOX])的释放以及土壤有机物的微生物转化对从原废水渗透位点的两种不同土壤中释放污染物的潜在影响。在参考条件下,两种土壤的总碳通量范围为6至9 mg / kg / d。其中超过92%是由于矿化(CO_2)引起的,而低于8%是由于色谱柱流出物中的溶解有机碳(DOC)引起的。尽管两种土壤中的有机卤素含量差异很大,但AOX的通量却相似(1μg/ kg / d)。通过改变温度和溶液的pH值以及干燥来改变微生物的活性。在所有观察到微生物呼吸(CO_2产生)增加的实验中,色谱柱流出物中有机污染物的释放也增加了。镍,锌和磷酸盐的通量显示出完全不同的模式,表明它们在土壤中的保留取决于化学参数。线性相关分析提供了清晰的证据,表明AOX和DOC通量彼此紧密联系。但是,土壤中非生物和生物过程的叠加并不能在土壤有机物的矿化与固存在土壤中的有机污染物的释放之间建立因果关系。我们的发现表明,微生物活动可能对受污染的土壤作为持久性有机污染物源的程度产生重大影响。

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