Kohan Danielle S, Lanno Roman P, Weavers Linda K
Environmental Science Graduate Program, The Ohio State University, Columbus, OH 43210, United States.
Environmental Science Graduate Program, The Ohio State University, Columbus, OH 43210, United States; Department of Evolutionary Ecology and Organismal Biology, The Ohio State University, Columbus, OH 43210, United States.
Ultrason Sonochem. 2022 Apr;85:105981. doi: 10.1016/j.ultsonch.2022.105981. Epub 2022 Mar 12.
Ultrasound (US) releases polycyclic aromatic hydrocarbons (PAHs) from contaminated creosote sediments and degrades PAHs in aqueous solution. However, it is unclear how much PAHs release occurs during active US compared to after US is stopped. In this study, solid-phase microextraction (SPME) was used to determine aqueous PAH concentrations desorbed from Little Scioto River creosote contaminated sediment during exposure to 20 kHz ultrasound (US) at a power of 430 W L. First, SPME fiber-water partition coefficients,K, were experimentally determined and shown to be comparable with previous studies. Next, PAH concentrations released into aqueous solution were determined by sequentially exposing fresh, conditioned SPME fibers in a reactor containing the contaminated sediment and DI for 10 min periods. Three consecutive 10 min periods each were measured during US and after US. Compared to mixing only, PAHs desorbed during ultrasound was significantly higher. In addition, for phenanthrene, anthracene, and fluoranthene, US showed significantly higher aqueous concentrations during US compared with after US. For these less soluble PAHs, desorption into the aqueous phase reaches and surpasses expected equilibrium aqueous concentrations. However, when US is ceased, PAHs appear to resorb onto sediment resulting in the lower concentrations measured in these PAH compounds after US that are similar to expected equilibrium aqueous concentrations. Typical analytical extraction methods for determining the effects of US require stopping treatment and may underestimate the potential US has for release of contaminants from sediment during US. Using SPME during US treatment reveals that the concentration of PAHs during US may surpass the expected equilibrium aqueous concentration of some PAHs congeners. To our knowledge, this higher concentration observed during US compared to after US has not been shown previously.
超声波(US)可使多环芳烃(PAHs)从受污染的杂酚油沉积物中释放出来,并能降解水溶液中的多环芳烃。然而,与超声停止后相比,在超声作用期间有多少多环芳烃会释放尚不清楚。在本研究中,采用固相微萃取(SPME)来测定在430 W L功率的20 kHz超声波(US)作用下,从小Scioto河杂酚油污染沉积物中解吸出来的水相中多环芳烃的浓度。首先,通过实验测定了SPME纤维-水分配系数K,并表明其与先前的研究结果相当。接下来,通过在含有污染沉积物和去离子水(DI)的反应器中依次将新鲜的、经过预处理的SPME纤维暴露10分钟,来测定释放到水溶液中的多环芳烃浓度。在超声作用期间和超声作用后,分别测量了连续三个10分钟时间段。与仅进行混合相比,超声作用期间解吸的多环芳烃显著更高。此外,对于菲、蒽和荧蒽,超声作用期间的水相浓度显著高于超声作用后。对于这些溶解度较低的多环芳烃,解吸到水相中的量达到并超过了预期的平衡水相浓度。然而,当超声停止时,多环芳烃似乎会重新吸附到沉积物上,导致超声作用后这些多环芳烃化合物的测量浓度降低,与预期的平衡水相浓度相似。用于确定超声作用效果的典型分析萃取方法需要停止处理,可能会低估超声在作用期间从沉积物中释放污染物的潜力。在超声处理期间使用SPME表明,超声作用期间多环芳烃的浓度可能超过某些多环芳烃同系物的预期平衡水相浓度。据我们所知,超声作用期间观察到的这种较高浓度与超声作用后相比,此前尚未有过报道。