Earth Surface Sciences, Institute for Biodiversity and Ecosystem Dynamics, Universiteit van Amsterdam, Nieuwe Achtergracht 166, 1018 WV, Amsterdam, The Netherlands.
Environ Sci Pollut Res Int. 2010 Jun;17(5):1070-9. doi: 10.1007/s11356-009-0263-9. Epub 2009 Dec 2.
BACKGROUND, AIM, AND SCOPE: The behavior of polycyclic aromatic hydrocarbons (PAHs) is affected by dissolved organic matter (DOM) present in pore water of soils and sediments. Since partitioning to DOM reduces the bioavailable or freely dissolved PAH concentration in pore water, it is important to assess the effect of environmental variables on the magnitude of dissolved organic matter to water partition coefficients (K (DOC)). The objective of this study was to apply passive samplers to measure freely dissolved PAHs allowing depletion from the aqueous phase. The method was applied to determine K (DOC) at different temperatures for a selection of PAHs with natural DOM of very different origin.
Freely dissolved concentrations of (spiked) phenanthrene, anthracene, fluoranthene, pyrene, and benzo[e]pyrene were determined by exposing polydimethylsiloxane (PDMS) fibers to aqueous solutions containing DOM extracted from freshwater sediments from Finland and the Netherlands. The K (DOC) values were subsequently calculated at different temperatures (3.2, 20, and 36 degrees C) by including temperature-dependent PDMS to water partition coefficients (K (PDMS)) in a mass balance. Furthermore, the effect of temperature on partitioning of PAHs to PDMS fibers or DOM was assessed by comparing the enthalpy of sorption to the excess enthalpy of dissolution of liquid PAHs.
Partitioning to DOM resulted in a decrease of freely dissolved concentrations with increasing DOM concentrations and a large range in log K (DOC) values at 20 degrees C for benzo[e]pyrene was observed (log K (DOC) = 4.93-6.60 L kg(-1) organic carbon). An increase of 10 degrees C in temperature resulted in a decrease of K (PDMS) by 0.09 to 0.13 log units for phenanthrene to pyrene and a decrease of K (DOC) by 0.13 log units for pyrene. The calculated enthalpies of sorption were less exothermic than the (negative) excess enthalpies of dissolution as expected for non-specific interactions between PAHs and PDMS or DOM.
The bioavailability of PAHs in sedimentary pore waters can be accurately determined by application of PDMS fibers (without requiring negligible depletion) in the presence of natural DOM with different sorption affinity for PAHs. The observed natural variability in log K (DOC) values for different sediments shows that large differences can occur in freely dissolved PAH concentrations in pore water and properties of DOM should be taken into account in predicting the bioavailability of PAHs. Furthermore, the effect of temperature on the partitioning behavior of PAHs shows that interactions between PAHs and environmental sorbents are comparable to interactions between PAHs in their pure condensed liquid phase and calculated excess enthalpies can be safely used to directly correct partition coefficients for temperature.
The application of PDMS fibers in measuring freely dissolved PAH concentrations can be used to study structural and thermodynamic aspects of PAH sorption to natural DOM as well as other environmental processes such as enhanced diffusion phenomena in pore water that are dependent on the amount (or concentration) of DOM, sorption affinity of DOM, and hydrophobicity of PAHs. These environmental factors will therefore give further insight into the site-specific exposure to freely dissolved PAH concentrations in soil and sedimentary pore water.
背景、目的和范围:多环芳烃(PAHs)的行为受土壤和沉积物孔隙水中存在的溶解有机物质(DOM)的影响。由于分配到 DOM 会降低孔隙水中生物可利用或自由溶解的 PAH 浓度,因此评估环境变量对分配系数(K(DOC))的影响非常重要。本研究的目的是应用被动采样器测量自由溶解的 PAHs,使其从水相中耗尽。该方法用于在不同温度下确定具有天然 DOM 的不同来源的 PAHs 的 K(DOC)值。
通过将聚二甲基硅氧烷(PDMS)纤维暴露于含有源自芬兰和荷兰淡水沉积物的 DOM 的水溶液中,来确定(添加)菲、蒽、荧蒽、芘和苯并[e]芘的自由溶解浓度。随后,通过在质量平衡中包含温度依赖性 PDMS 与水的分配系数(K(PDMS)),在不同温度(3.2、20 和 36°C)下计算 K(DOC)值。此外,通过比较 PAHs 吸附的焓与液体 PAHs 溶解的过剩焓,评估了温度对 PAHs 分配到 PDMS 纤维或 DOM 的影响。
与 DOM 分配会导致自由溶解浓度随 DOM 浓度的增加而降低,并且在 20°C 下观察到苯并[e]芘的 log K(DOC)值范围很大(log K(DOC)= 4.93-6.60 L kg(-1)有机碳)。温度升高 10°C,会导致菲到芘的 K(PDMS)降低 0.09 到 0.13 个对数单位,而对于芘,K(DOC)降低 0.13 个对数单位。计算出的吸附焓比预期的非特异性相互作用(PAHs 和 PDMS 或 DOM 之间)的(负)过剩溶解焓更不放热。
在存在具有不同 PAHs 吸附亲和力的天然 DOM 的情况下,应用 PDMS 纤维(无需要求可忽略不计的耗尽)可以准确确定沉积物孔隙水中 PAHs 的生物可利用性。不同沉积物中 log K(DOC)值的观察到的自然变异性表明,孔隙水中自由溶解的 PAH 浓度和 DOM 的性质可能存在很大差异,在预测 PAHs 的生物可利用性时应考虑这些因素。此外,PAHs 分配行为的温度影响表明,PAHs 与环境吸附剂之间的相互作用与 PAHs 在其纯凝聚液相中的相互作用相当,并且可以安全地使用计算出的过剩焓直接校正温度下的分配系数。
PDMS 纤维在测量自由溶解 PAH 浓度方面的应用可用于研究 PAH 与天然 DOM 吸附的结构和热力学方面,以及其他环境过程,如孔隙水中的增强扩散现象,这些过程取决于 DOM 的数量(或浓度)、DOM 的吸附亲和力和 PAHs 的疏水性。这些环境因素将进一步深入了解土壤和沉积物孔隙水中自由溶解 PAH 浓度的特定位置暴露情况。