Sun Zhaoyue, Wang Xinghao, Liu Cun, Fang Guodong, Chu Longgang, Gu Cheng, Gao Juan
Key Laboratory of Soil Environment and Pollution Remediation, Institute of Soil Science, Chinese Academy of Sciences, No. 71 East Beijing Road, Nanjing 210008, China.
University of Chinese Academy of Sciences, Beijing 100049, China.
Environ Sci Technol. 2021 Mar 16;55(6):3716-3726. doi: 10.1021/acs.est.0c07472. Epub 2021 Feb 26.
Polycyclic aromatic hydrocarbon (PAH) contamination has raised great environmental concerns, while the effects of low-molecular-weight organic compounds (LMWOCs) on PAH photodegradation at amorphous silica (AS)/air interfaces have been largely ignored. In this study, the phototransformation of anthracene (ANT) at amorphous silica (AS)/air interfaces was investigated with the addition of LMWOCs. ANT removal was attributed to OH attacking and the energy transfer process via ANT*. Light irradiation induced the fractured ≡SiO or ≡Si generation on AS surfaces, which could react with absorbed HO and O to generate OH and further yield a series of hydroxylated products of ANT. The presence of citric acid and oxalic acid improved OH generation and enhanced ANT removal by 1.0- and 2.2-fold, respectively. For comparison, the presence of catechol and hydroquinone significantly decreased ANT removal and produced coupling products. The results of density functional theory calculations suggest that persistent free radicals (PFRs) on AS surfaces from catechol or hydroquinone after OH attacking prefer to cross-couple with ANT via C-C bonding rather than self-couple. Dianthrone and cross-coupling products might possess higher ecotoxicity, while hydroxylated products were less ecotoxic than their parent compounds based on Ecological Structure Activity Relationships (ECOSAR) estimation. The results of this study revealed the potential ecotoxicity of PAH-adsorbed particulates coexisting with LMWOCs and also provided a new insight into PAH transformation through PFR pathways.
多环芳烃(PAH)污染引发了极大的环境担忧,而低分子量有机化合物(LMWOCs)对非晶硅(AS)/空气界面处PAH光降解的影响在很大程度上被忽视了。在本研究中,通过添加LMWOCs研究了蒽(ANT)在非晶硅(AS)/空气界面处的光转化。ANT的去除归因于OH攻击以及通过ANT*的能量转移过程。光照诱导AS表面产生断裂的≡SiO或≡Si,其可与吸附的HO和O反应生成OH,并进一步生成一系列ANT的羟基化产物。柠檬酸和草酸的存在分别使OH生成量增加,并使ANT去除率提高了1.0倍和2.2倍。相比之下,邻苯二酚和对苯二酚的存在显著降低了ANT的去除率,并产生了偶联产物。密度泛函理论计算结果表明,邻苯二酚或对苯二酚在OH攻击后在AS表面产生的持久性自由基(PFRs)更倾向于通过C-C键与ANT发生交叉偶联而不是自偶联。基于生态结构活性关系(ECOSAR)估计,二蒽酮和交叉偶联产物可能具有更高的生态毒性,而羟基化产物的生态毒性低于其母体化合物。本研究结果揭示了与LMWOCs共存的PAH吸附颗粒的潜在生态毒性,并为通过PFR途径的PAH转化提供了新的见解。