Fukushima Masami, Tanabe Yasuaki, Yabuta Hikaru, Tanaka Fumiko, Ichikawa Hiroyasu, Tatsumi Kenji, Watanabe Akira
National Institute of Advanced Industrial Science and Technology, AIST, Tsukuba, Japan.
J Environ Sci Health A Tox Hazard Subst Environ Eng. 2006;41(8):1483-94. doi: 10.1080/10934520600754748.
To elucidate the role of a soil humic acid (HA) in the transport of polychlorinated organic pollutants (PCOPs), such as polychlorinated dibenzo-p-dioxins, polychlorinated dibenzofurans and coplanar-polychlorinated biphenyls, their partition coefficients (Kdoc) into an HA were compared with their adsorption coefficients (KOC) for a soil with a higher organic carbon (OC) content. The soil sample (ando soil) used in the present study was collected in the same location as the HA. The log Kdoc values were positively correlated with logarithm of octanol-water partition coefficients (log KOW) of the PCOPs, indicating that the partitioning of PCOPs into the HA was mainly due to hydrophobic interactions. However, the correlation between log Kdoc and log KOC was negative. This can be attributed to the enhanced water solubility of the PCOPs as the result of the dissolved organic matter from the soil. That is, when the more hydrophobic PCOPs with higher log KOW values are partitioned into the HA, then the larger quantities of PCOPs that are partitioned into the HA are able to dissolve in the aqueous phase. These results suggest that, in a soil with a higher OC content, the HA can serve as more effective carrier of PCOPs from the soil to an aquatic environment.
为阐明土壤腐殖酸(HA)在多氯有机污染物(PCOPs)(如多氯二苯并 - p - 二噁英、多氯二苯并呋喃和共平面多氯联苯)迁移中的作用,将它们在HA中的分配系数(Kdoc)与其在有机碳(OC)含量较高的土壤中的吸附系数(KOC)进行了比较。本研究中使用的土壤样品(暗棕色土壤)与HA采集于同一地点。PCOPs的log Kdoc值与正辛醇 - 水分配系数(log KOW)的对数呈正相关,这表明PCOPs在HA中的分配主要是由于疏水相互作用。然而,log Kdoc与log KOC之间的相关性为负。这可归因于土壤中溶解的有机物导致PCOPs的水溶性增强。也就是说,当log KOW值较高的疏水性更强的PCOPs分配到HA中时,分配到HA中的PCOPs有更多能够溶解在水相中。这些结果表明,在有机碳含量较高的土壤中,HA可以作为PCOPs从土壤到水生环境的更有效载体。