不同解吸剂对土壤介质中萘解吸和氧化降解的影响

张汝壮

华东理工大学学报(自然科学版) ›› 2026, Vol. 52 ›› Issue (4) : 520 -532.

PDF (4761KB)
华东理工大学学报(自然科学版) ›› 2026, Vol. 52 ›› Issue (4) : 520 -532. DOI: 10.14135/j.cnki.1006-3080.20260112001
研究论文

不同解吸剂对土壤介质中萘解吸和氧化降解的影响

作者信息 +

Effects of Different Desorbing Agents on Desorption and Oxidative Degradation of Naphthalene in Soil Media

Author information +
文章历史 +
PDF (4875K)

摘要

为研究萘 (NAP) 污染土壤的高效修复技术,系统探究了 NAP 在不同土壤介质中的解吸行为,分析 NAP 对土壤老化的影响,并对比无机盐 (CaCl2)、低分子量有机酸 (柠檬酸 (CA),草酸 (OA),天冬氨酸 (ASP)) 和表面活性剂 (吐温-80 (Tween-80),十二烷基硫酸钠 (SDS),烷基糖苷 (APG)) 这 3 类解吸剂对 NAP 的解吸作用,以及 3 类解吸剂对亚铁离子 (Fe(II)) 活化过二硫酸盐 (PDS) 氧化体系降解 NAP 的影响。结果表明:土壤黏粒含量越高,老化时间越长,NAP 解吸越困难;弱碱性 (pH=9.0) 有利于 NAP 解吸,且解吸过程符合拟二级动力学模型。3 类解吸剂对 NAP 的解吸效果存在显著差异:低分子量有机酸解吸效果最优,其中 1 mmol/L 的 CA 解吸 48 h 时,NAP 去除率可达到 36.1%,显著优于 OA 和 ASP;表面活性剂均能显著提升解吸效果,Tween-80 因临界胶束浓度 (CMC) 低、疏水性适宜,因而表现最佳,且 Tween-80 浓度越高,解吸效果提升越明显;低浓度(<10 mmol/L) CaCl2 可通过竞争吸附位点促进解吸,高浓度 (100 mmol/L) CaCl2 则因为会导致土壤有机质絮凝沉淀而抑制解吸。在后续氧化降解过程中,表面活性剂与 CaCl2 因竞争活性氧物种 (ROS) 而抑制 NAP 降解,但 3 种低分子量有机酸对 NAP 降解均起到正向作用;当 PDS/Fe(II)/CA/NAP 物质的量之比为 15∶5∶1∶1 时,120 min 内 NAP 去除率达到 97.5%。研究证实,CA兼具高效解吸土壤 NAP 和强化后续氧化降解的双重功能。本文为 CA 应用于有机污染场地的绿色高效修复提供了理论依据。

Abstract

To develop efficient remediation technologies for naphthalene (NAP)-contaminated soil, this study systematically investigates the desorption behavior of NAP in various soil media, analyzes the effects of soil aging on NAP retention, and compares the desorption performance of three categories of desorbents toward NAP, including inorganic salt (CaCl2), low-molecular-weight organic acids (Citric acid (CA), Oxalic acid (OA), Aspartic acid (ASP)), and surfactants (Tween-80, sodium dodecyl sulfate (SDS), alkyl polyglycoside (APG)). The influences of the three desorbent categories on NAP degradation in the ferrous ion (Fe(II))-activated persulfate (PDS) oxidation system are also evaluated. The results reveal that NAP desorption becomes more difficult with increasing soil clay content and longer aging duration. Weakly alkaline conditions (pH = 9.0) facilitate NAP desorption, and the desorption process conforms to the pseudo-second-order kinetic model. Significant differences are observed in the NAP desorption efficiency of the three desorbent groups. Low-molecular-weight organic acids exhibit the optimal desorption capacity; specifically, 1 mmol/L CA achieves a NAP removal rate of 36.1% after 48 h of desorption, which is markedly superior to OA and ASP. All tested surfactants substantially improve NAP desorption, among which Tween-80 delivers the best performance owing to its low critical micelle concentration (CMC) and suitable hydrophobicity, with desorption efficiency rising evidently as Tween-80 concentration increases. Low-concentration CaCl2 (<10 mmol/L) promotes NAP desorption by competing for soil adsorption sites, while high-concentration CaCl2 (100 mmol/L) inhibits desorption by inducing flocculation and precipitation of soil organic matter. In the subsequent oxidative degradation stage, surfactants and CaCl2 suppress NAP degradation via competing for reactive oxygen species (ROS), whereas all three low-molecular-weight organic acids exert positive promotional effects on NAP removal. When the molar ratio of PDS/Fe(II)/CA/NAP is set to 15∶5∶1∶1, the NAP removal rate reaches 97.5% within 120 min. This study verifies that CA possesses dual functions: Efficiently desorbing soil-sorbed NAP and enhancing subsequent oxidative degradation. The present work provides theoretical support for the green and efficient remediation of organic-contaminated sites using CA.

关键词

萘 / 解吸剂 / 解吸动力学 / 高级氧化 / 污染场地修复

Key words

naphthalene / desorbing agent / desorption kinetics / advanced oxidation / contaminated site remediation

引用本文

引用格式 ▾
张汝壮. 不同解吸剂对土壤介质中萘解吸和氧化降解的影响[J]. 华东理工大学学报(自然科学版), 2026, 52(4): 520-532 DOI:10.14135/j.cnki.1006-3080.20260112001

登录浏览全文

4963

注册一个新账户 忘记密码

参考文献

[1]

GUO Y, DAI Y, ZHAO W, et al. Highly efficient photocatalytic degradation of naphthalene by Co3O4/Bi2O2CO3 under visible light: A novel p-n heterojunction nanocomposite with nanocrystals/lotus-leaf-like nanosheets structure[J].Applied Catalysis B: Environmental, 2018, 237:273-287.

[2]

YAN D Y S, LO I M C. Removal effectiveness and mechanisms of naphthalene and heavy metals from artificially contaminated soil by iron chelate-activated persulfate[J].Environmental Pollution, 2013, 178:15-22.

[3]

HAN J, LIANG Y, ZHAO B, et al. Polycyclic aromatic hydrocarbon (PAHs) geographical distribution in China and their source, risk assessment analysis[J].Environmental Pollution, 2019, 251:312-327.

[4]

ZAGYRY G J, MARIN V C A, GUNEY M. Public health risk assessment following exposure to PAH-contaminated soils-specific considerations for bioaccessibility and other exposure parameters[J].Science of The Total Environment, 2019, 656:1043-1045.

[5]

EL-SHEIKH A H, ALSHAMALY H S. Cadmium removal from organic acid-bearing soil-washing water by magnetic biosorption: Effect of various factors and adsorption isothermal study[J].Journal of Environmental Chemical Engineering, 2020, 8(5):104188.

[6]

TRELLU C, MOUSSET E, PECHAUD Y, et al. Removal of hydrophobic organic pollutants from soil washing/flushing solutions: A critical review[J].Journal of Hazardous Materials, 2016, 306:149-174.

[7]

BARBATI B, MOSCATELLI G, BELLAGAMBA M, et al. Surfactant-enhanced mobilization of polycyclic aromatic hydrocarbons from an historically contaminated marine sediment: Study of surfactants’ concentration effect and continuous test for sediment flushing simulation[J].Journal of Environmental Chemical Engineering, 2024, 12(5):113820.

[8]

CHEN H, DOU J, XU H. The effect of low-molecular-weight organic-acids (LMWOAs) on treatment of chromium-contaminated soils by compost-phytoremediation: Kinetics of the chromium release and fractionation[J].Journal of Environmental Sciences, 2018, 70:45-53.

[9]

KIM K, YOON S, KWON H, et al. Effects of treatment agents during acid washing and pH neutralization on the fertility of heavy metal-impacted dredged marine sediment as plant-growing soil[J].Environmental Pollution, 2020, 267:115466.

[10]

AN C, HUANG G, WEI J, et al. Effect of short-chain organic acids on the enhanced desorption of phenanthrene by rhamnolipid biosurfactant in soil-water environment[J].Water Research, 2011, 45(17):5501-5510.

[11]

GUO R, XI B, HU Y, et al. Enhancing persulfate activation by carbon-based Mn-Fe nanoparticles for groundwater ISCO treatment: Efficiency, stability and mechanism[J].Chemical Engineering Journal, 2023, 476:146827.

[12]

IKE I A, LINDEN K G, ORBELL J D, et al. Critical review of the science and sustainability of persulphate advanced oxidation processes[J].Chemical Engineering Journal, 2018, 338:651-669.

[13]

WACLAWEK S, LUTZE H V, GRUBEL K, et al. Chemistry of persulfates in water and wastewater treatment: A review[J].Chemical Engineering Journal, 2017, 330:44-62.

[14]

DOMINGUEZ C M, ROMERO A, SANTOS A. Selective removal of chlorinated organic compounds from lindane wastes by combination of nonionic surfactant soil flushing and Fenton oxidation[J].Chemical Engineering Journal, 2019, 376:120009.

[15]

LI Y, LIAO X, HULING S G, et al. The combined effects of surfactant solubilization and chemical oxidation on the removal of polycyclic aromatic hydrocarbon from soil[J].Science of The Total Environment, 2019, 647:1106-1112.

[16]

ZHOU Y, LIU R, TANG H. Sorption interaction of phenanthrene with soil and sediment of different particle sizes and in various CaCl2 solutions[J].Journal of Colloid and Interface Science, 2004, 270(1):37-46.

[17]

ZHANG J, HE M. Effect of structural variations on sorption and desorption of phenanthrene by sediment organic matter[J].Journal of Hazardous Materials, 2010, 184(1):432-438.

[18]

OBRIST D, ZIELINSKA B, PERLINGER J A. Accumulation of polycyclic aromatic hydrocarbons (PAHs) and oxygenated PAHs (OPAHs) in organic and mineral soil horizons from four U. S. remote forests[J].Chemosphere, 2015, 134:98-105.

[19]

ENGEL M, CHEFETZ B. Adsorption and desorption of dissolved organic matter by carbon nanotubes: Effects of solution chemistry[J].Environmental Pollution, 2016, 213:90-98.

[20]

ZHANG J, HUA P, KREBA P. The influences of dissolved organic matter and surfactant on the desorption of Cu and Zn from road-deposited sediment[J].Chemosphere, 2016, 150:63-70.

[21]

许明珠, 刘文新, 邢宝山, 等. 水-土体系中溶解有机质对菲解吸动力学的影响 [J].环境科学学报, 2008(5):976-981.

[22]

SCHLAUTMAN M A, MORGAN J J. Effects of aqueous chemistry on the binding of polycyclic aromatic hydrocarbons by dissolved humic materials[J].Environmental Science and Technology, 1993, 27(5):961-969.

[23]

陈刚, 程莉蓉, 丁爱中. 金属离子对长期污染土壤中多环芳烃解吸的影响 [J].环境科学学报, 2012, 32(7):1708-1716.

[24]

SOKOLOVA T A. Low-molecular-weight organic acids in soils: Sources, composition, concentrations, and functions: A review[J].Eurasian Soil Science, 2020, 53(5):580-594.

[25]

KE X, ZHANG F J, ZHOU Y, et al. Removal of Cd, Pb, Zn, Cu in smelter soil by citric acid leaching[J].Chemosphere, 2020, 255:126690.

[26]

GAO Y, XIONG W, LING W, et al. Impact of exotic and inherent dissolved organic matter on sorption of phenanthrene by soils[J].Journal of Hazardous Materials, 2007, 140(1):138-144.

[27]

SUN B, GAO Y. The impact of different root exudate components on phenanthrene availability in soil[J].Soil Science Society of America Journal, 2010, 74(1):51-59.

[28]

GAO Y, REN L, LING W, et al. Effects of low-molecular-weight organic acids on sorption-desorption of phenanthrene in soils[J].Soil Science Society of America Journal, 2010, 74:51-59.

[29]

LING W, SUN R, GAO X, et al. Low-molecular-weight organic acids enhance desorption of polycyclic aromatic hydrocarbons from soil[J].European Journal of Soil Science, 2015, 66(2):339-347.

[30]

BOUZID I, MAIRE J, BRUNOL E, et al. Compatibility of surfactants with activated-persulfate for the selective oxidation of PAH in groundwater remediation [J].Journal of Environmental Chemical Engineering, 2017, 5(6):6098-6106.

[31]

MAO X H, JIANG R, XIAO W, et al. Use of surfactants for the remediation of contaminated soils: A review[J].Journal of Hazardous Materials, 2015, 285:419-435.

[32]

WANG L, PENG L, XIE L, et al. Compatibility of surfactants and thermally activated persulfate for enhanced subsurface remediation[J].Environmental Science & Technology, 2017, 51:7055-7064.

[33]

KARTHICK A, ROY B, CHATTOPADHYAY P. A review on the application of chemical surfactant and surfactant foam for remediation of petroleum oil contaminated soil[J].Journal of Environmental Management, 2019, 243:187-205.

[34]

CHENG K Y, WONG J C W. Effect of synthetic surfactants on the solubilization and distribution of PAHs in water/soil-water systems[J].Environmental Technology, 2006, 27(8):835-844.

[35]

BEFKADU A A, CHEN Q. Surfactant-enhanced soil washing for removal of petroleum hydrocarbons from contaminated soils: A review[J].Pedosphere, 2018, 28(3):383-410.

[36]

ANIPSITAKIS G P, DIONYSIOU D D. Degradation of organic contaminants in water with sulfate radicals generated by the conjunction of peroxymonosulfate with cobalt[J].Environmental Science & Technology, 2003, 37(20):4790-4797

[37]

SUN Y, SUN X, ALI M, et al. Enhanced trichloroethene degradation performance in innovative nanoscale CaO2 coupled with bisulfite system and mechanism investigation[J].Separation and Purification Technology, 2021, 278:119539.

[38]

YANG J, ZHONG L, LIU L. Chromium(VI) reduction in the nano or micron-sized iron oxide-citric acid systems: Kinetics and mechanisms[J].Journal of Environmental Chemical Engineering, 2017, 5(3):2564-2569.

[39]

MOUSSET E, OTURAN N, VAN HULLEBUSCH E D, et al. Influence of solubilizing agents (cyclodextrin or surfactant) on phenanthrene degradation by electro-Fenton process-Study of soil washing recycling possibilities and environmental impact[J].Water Research, 2014, 48:306-316.

[40]

MOUSSET E, OTURAN N, VAN HULLEBUSCH E D, et al. Treatment of synthetic soil washing solutions containing phenanthrene and cyclodextrin by electro-oxidation. Influence of anode materials on toxicity removal and biodegradability enhancement[J].Applied Catalysis B: Environmental, 2014, 160:666-675.

[41]

TRELLU C, OTURAN N, PECHAUD Y, et al. Anodic oxidation of surfactants and organic compounds entrapped in micelles: Selective degradation mechanisms and soil washing solution reuse[J].Water Research, 2017, 118:1-11.

[42]

WANG L, WU H, DENG D. Role of surfactants in accelerating or retarding persulfate decomposition[J].Chemical Engineering Journal, 2020, 384:123303.

[43]

ZRINYI N, PHAM A L T. Oxidation of benzoic acid by heat-activated persulfate: Effect of temperature on transformation pathway and product distribution[J].Water Research, 2017, 120:43-51.

[44]

DONG H, LI Y, WANG S, et al. Both Fe(IV) and radicals are active oxidants in the Fe(II)/peroxydisulfate process[J].Environmental Science and Technology Letters, 2020, 7(3):219-224.

基金资助

上海市东方英才计划青年项目(QNKJ2024053)

上海城投 (集团) 有限公司科技创新计划项目(CTKY-PTZX-2025-008)

AI Summary AI Mindmap
PDF (4761KB)

0

访问

0

被引

详细

导航
相关文章

AI思维导图

/

〈 〉