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生态学杂志 ›› 2021, Vol. 40 ›› Issue (12): 4034-4043.doi: 10.13292/j.1000-4890.202112.008

• 研究报告 • 上一篇    下一篇

生物炭与表面活性剂联合强化淋洗去除污染土壤中PAHs的效果及其机制

于金龙1,2,孙梨宗2,薛晨阳2,贾春云2,台培东2,李英华1*   

  1. 1东北大学资源与土木工程学院, 沈阳 110819; 2中国科学院污染生态与环境工程重点实验室, 中国科学院沈阳应用生态研究所, 沈阳 110016)
  • 出版日期:2021-12-10 发布日期:2022-05-10

Mechanism underlying the effects of biochar combined with surfactant enhanced washing on removal of PAHs from contaminated soil.

YU Jin-long1,2, SUN Li-zong2, XUE Chen-yang2, JIA Chun-yun2, TAI Pei-dong2, LI Ying-hua1*   

  1. (1School of Resources and Civil Engineering, Northeastern University, Shenyang 110819, China; 2Key Laboratory of Pollution Ecology and Environmental Engineering, Institute of Applied Ecology, Chinese Academy of Sciences, Shenyang 110016, China).
  • Online:2021-12-10 Published:2022-05-10

摘要: 采用生物炭吸附与表面活性剂淋洗联合修复PAHs污染场地土壤,通过外源添加700 ℃制备的稻壳生物炭,研究了添加生物炭对非离子型表面活性剂TX-100淋洗PAHs效果的影响;通过老化后的含芘高岭土模拟污染土壤,研究了生物炭吸附与TX-100淋洗联合修复的驱动机制。强化淋洗修复结果显示:TX-100浓度为10 g·L-1,淋洗时间为16 h,固液比为1∶10,转速为150 r·min-1,对本研究选取的PAHs浓度为94.97 mg·kg-1的污染土壤的淋洗效果最好,解吸率达66.2%;添加1%土壤质量的稻壳生物炭,稳定14 d后,TX-100对PAHs解吸率从对照的66.2%提高到了80.6%(P<0.05),其中四环PAHs的解吸量占比最高(42.1%)。高岭土模拟结果显示:添加1%土壤质量的生物炭14 d后,高岭土中芘含量从50 mg·kg-1降低至27.77 mg·kg-1,同时TX-100可以有效洗脱生物炭上吸附的芘,解吸率达80.2%。扫描电镜和光谱学分析显示:生物炭可以吸附TX-100,而被吸附的TX-100又会占据部分生物炭孔道,后者在1600 cm-1处的C=O和C=C吸收振动峰和1103~1025 cm-1处的C-O-C吸收振动峰明显减弱,进一步导致PAHs从固相向液相的迁移。因此,在表面活性剂淋洗修复前,添加生物炭可以显著提高土壤PAHs的解吸率。

关键词: 生物炭, 表面活性剂, PAHs, 界面迁移

Abstract: Biochar adsorption and surfactant washing were used to remediate PAHs contaminated soil. Rice husk biochar prepared at 700 ℃ was added to examine the effect of biochar addition on the washing of PAHs by nonionic surfactant TX-100. The underlying mechanism of biochar adsorption combined with TX-100 washing was examined by simulating contaminated soil with pyrene-containing kaolin after aging. The results of enhanced washing remediation showed that when the concentration of TX-100 was 10 g·L-1, washing time was 16 h, the ratio of solid to liquid was 1∶10, and the rotating speed was 150 r·min-1, a desorption rate of 66.2% was obtained for the contaminated soil with PAHs concentration of 94.97 mg·kg-1. After the rice husk biochar with 1% soil mass was added and stabilized for 14 days, the desorption rate of PAHs by TX-100 increased from 66.2% to 80.6% (P<0.05), and the desorption rate of tetracyclic PAHs was the highest (42.1%). Kaolin simulation results showed that after adding biochar 1% of soil mass for 14 days, the content of pyrene in kaolin decreased from 50 mg·kg-1 to 27.77 mg·kg-1. TX-100 could effectively wash out pyrene adsorbed on biochar, with desorption rate reaching 82.4%. Scanning electron microscope and spectroscopic analysis showed that biochar could adsorb TX-100, while the adsorbed TX-100 occupied part of the pores of biochar, and the absorption vibration peaks of C=O and C=C at 1600 cm-1 and C-O-C at 1103-1025 cm-1 were obviously weakened, which further led to the migration of PAHs from solid phase to liquid phase. Therefore, before using surfactants for washing and remediation, biochar addition can significantly improve the desorption rate of soil PAHs.

Key words: biochar, surfactant, PAHs, interface migration.