Optimization ratio of industrial waste and sodium persulfate for synergy in solidification/stabilization of petroleum-contaminated soil
SHI Qing-hong1, YANG Xiu-juan1,2, ZHAO Zhi1, FAN Heng-hui1,2, MENG Min-qiang1,2, MA Xing-ye1
1. College of Water Resources and Architectural Engineering, Northwest A&F University, Yangling 712100, China; 2. Institute of Geotechnical Engineering/Museum of Problematic Rock and Soil, Northwest A&F University, Yangling 712100, China
Abstract:Sodium persulfate, lime, fly ash, and carbide slag were used as solidification/stabilization agent materials to investigate the influence of different materials content ratios on the unconfined compression strength, toxic leaching concentration, and acid neutralization capacity of petroleum-contaminated soil, which based on the orthogonal test included four influenced factors and four levels. The optimization ratio of solidified/stabilized materials was selected under fuzzy optimization theory frame. The changeable rules of pH value, temperature, S2O82– content and total petroleum hydrocarbon content were analyzed to explain the solidified/stabilized mechanism of petroleum-contaminated soil. The X-ray diffraction test (XRD) and scanning electron microscope (SEM) test were also conducted to illustrate the microscopic mechanism in solidification/stabilization of petroleum-contaminated soil further. The experimental results showed that the sodium persulfate content had the greatest influence on the unconfined compression strength and toxic leaching concentration of petroleum-contaminated soil based on the extremum difference analysis. And the lime content had the greatest influence on acid neutralization capacity of petroleum-contaminated soil. It also showed that the content of sodium persulfate, lime, fly ash, and carbide slag were 0.6%、8.0%、10.0%、6.0%, respectively, can be selected as the optimal ratio to solidify/stabilize the petroleum-contaminated soil according to the fuzzy optimization indexes of unconfined compression strength, toxic leaching concentration, acid neutralization capacity and handing cost. The unconfined compression strength was 630.40kPa. The toxic leaching concentration was 4.44mg/L. The acid neutralization capacity was 385.71cmol/kg. And the handing cost was 136.46yuan/t. The solidified/stabilized petroleum-contaminated soil achieved the requirement of the strength of refuse reclamation and environmental safety. The toxic leaching concentration reduction, and the strength and acid neutralization capacity improved of the solidified/stabilizes petroleum-contaminated soil. The reasons can be explained by the fact that some petroleum can be removed from the contaminated soil because of oxidated reaction between sodium persulfate and petroleum. And the cemented substance was generated to cement the soil particles due to the hydration reaction of lime, fly ash and calcium carbide slag.
石庆红, 杨秀娟, 赵之, 樊恒辉, 孟敏强, 马兴业. 工业废渣-过硫酸钠协同固化/稳定化石油污染土配比优选研究[J]. 中国环境科学, 2023, 43(4): 1791-1801.
SHI Qing-hong, YANG Xiu-juan, ZHAO Zhi, FAN Heng-hui, MENG Min-qiang, MA Xing-ye. Optimization ratio of industrial waste and sodium persulfate for synergy in solidification/stabilization of petroleum-contaminated soil. CHINA ENVIRONMENTAL SCIENCECE, 2023, 43(4): 1791-1801.
刘五星,骆永明,滕 应,等.我国部分油田土壤及油泥的石油污染初步研究[J]. 土壤, 2007,39(2):247-251. Liu W X, Luo Y M, Teng Y, et al. A survey of petroleum contamination in several Chinese oilfield soils[J]. Soils, 2007,39(2):247-251.
[2]
Du W D, Wan Y Y, Zhong N N, et al. Status quo of soil petroleum contamination and evolution of bioremediation[J]. Petroleum Science, 2011,8(4):502-514.
[3]
贾建丽,刘 莹,李广贺,等.油田区土壤石油污染特性及理化性质关系[J]. 化工学报, 2009,60(3):726-732. Jia J L, Liu Y, Li G H, et al. Contamination characteristics and its relationship with physicochemical properties of oil polluted soils in oilfields of China[J]. CIESC Journal, 2009,60(3):726-732.
[4]
许殷瑞,吴蔓莉,王 丽,等.陕北石油污染土壤微生物种群变化及影响因素[J]. 中国环境科学, 2021,41(9):4349-4359. Xu Y R, Wu M L, Wang L, et al. The influences of petroleum pollution on the microbial population distribution in Northern Shaanxi Province of China[J]. China Environmental Science, 2021,41(9):4349-4359.
[5]
Devatha C P, Vishal A V, Rao J P C. Investigation of physical and chemical characteristics on soil due to crude oil contamination and its remediation[J]. Applied Water Science, 2019,9(4):89.
[6]
Ilangovan K, Vivekanandan M. Effect of oil pollution on soil respiration and growth of vigna-mungo (L) Hepper[J]. Science of the Total Environment, 1992,116(1/2):187-194.
[7]
李 佳,曹兴涛,隋 红,等.石油污染土壤修复技术研究现状与展望[J]. 石油学报(石油加工), 2017,33(5):811-833. Li J, Cao X T, Sui H, et al. Overview of remediation technologies for petroleum-contaminated soils[J]. Acta Petrolei Sinica(Petroleum Processing Section), 2017,33(5):811-833.
[8]
Wang F, Wang H, Jin F, et al. The performance of blended conventional and novel binders in the in-situ stabilisation/solidification of a contaminated site soil[J]. Journal of Hazardous Materials, 2015,285:46-52.
[9]
Ma F J, Wu B, Zhang Q, et al. An innovative method for the solidification/stabilization of PAHs-contaminated soil using sulfonated oil[J]. Journal of Hazardous Materials, 2018,344:742-748.
[10]
刘 建,何 亮,骆成杰,等.生活垃圾焚烧飞灰固化体重金属动态浸出规律[J]. 中国环境科学, 2019,39(3):1087-1093. Liu J, He L, Luo C J, et al. Dynamic leaching rule of heavy metals in solidified body of fly ash from MSW incineration[J]. China Environmental Science, 2019,39(3):1087-1093.
[11]
Li M, Yu H M, Zheng D, et al. Effects of salt and solidification treatment on the oil-contaminated soil:A case study in the coastal region of Tianjin, China[J]. Journal of Cleaner Production, 2021,312.
[12]
Xiao W, Yao X, Zhang F Y. Recycling of oily sludge as a roadbed material utilizing phosphogypsum-based cementitious materials[J]. Advances in Civil Engineering, 2019,6280715,1-10.
[13]
Stampino P G, Zampori L, Dotelli G, et al. Use of admixtures in organic-contaminated cement-clay pastes[J]. Journal of Hazardous Materials, 2009,161(2/3):862-870.
[14]
Yen C H, Chen K F, Kao C M, et al. Application of persulfate to remediate petroleum hydrocarbon-contaminated soil:Feasibility and comparison with common oxidants[J]. Journal of Hazardous Materials, 2011,186(2/3):2097-2102.
[15]
吴 昊,孙丽娜,王 辉,等.活化过硫酸钠原位修复石油类污染土壤研究进展[J]. 环境化学, 2015,34(11):2085-2095. Wu H, Sun L N, Wang H, et al. Persulfate in-situ remediation of petroleum hydrocarbon contaminated soil[J]. Environmental Chemistry, 2015,34(11):2085-2095.
[16]
Xue Y J, Liu J, Zhou Y, et al. Treatment of petroleum hydrocarbon contaminated soil by basic oxygen furnace slag activated persulfate oxidation in presence of electromagnetic induction heating[J]. Journal of Environmental Chemical Engineering, 2022,10(2):107267.
[17]
徐源洲,张力浩,方 成,等.优化SO4-·高级氧化修复PAHs复合污染土壤[J]. 中国环境科学, 2020,40(3):1183-1190. Xu Y Z, Zhang L H, Fang C, et al. Optimization of sulfate radical advanced oxidation technology on PAHs remediation in contaminated sites.[J]. China Environmental Science, 2020,40(3):1183-1190.
[18]
Cassidy D P, Srivastava V, Dombrowski F J, et al. Combining in situ chemical oxidation, stabilization, and anaerobic bioremediation in a single application to reduce contaminant mass and leachability in soil[J]. Journal of Hazardous Materials, 2015,297:347-355.
[19]
Srivastava V J, Hudson J M, Cassidy D P. Achieving synergy between chemical oxidation and stabilization in a contaminated soil[J]. Chemosphere, 2016,154:590-598.
[20]
Ma Y, Liu Z, Xu Y, et al. Remediating potentially toxic metal and organic Co-contamination of soil by combining in situ solidification/stabilization and chemical oxidation:efficacy, mechanism, and evaluation[J]. International Journal of Environmental Research & Public Health, 2018,15(11):1-19.
[21]
GB/T 50123-2019 土工试验方法标准[S]. GB/T 50123-2019 Standard for geotechnical testing method[S].
HJ 970-2018 水质 石油类的测定 紫外分光光度法(试行)[S]. HJ 970-2018 Water quality-determination of petroleum-Ultraviolet spectrophotometric method[S].
[25]
夏威夷.新型羟基磷灰石基固化剂修复铅锌镉复合污染土的机理与应用研究[D].南京:东南大学, 2018. Xia W Y. Immobilization mechanisms and field evaluation of a new hydroxyapatite based binder for solidification and stabilization of heavy metal contaminated site soil[D]. Nanjing:Southeast University, 2018.
[26]
Kujlu R, Moslemzadeh M, Rahimi S, et al. Selecting the best stabilization/solidification method for the treatment of oil-contaminated soils using simple and applied best-worst multi-criteria decision-making method[J]. Environmental Pollution, 2020,263:114447.
[27]
孟亚妮,李天鹏,施 展,等.施肥和增水对弃耕草地土壤酸中和容量的影响[J]. 应用生态学报, 2020,31(5):1579-1586. Meng Y N, Li T P, Shi Z, et al. Effects of fertilization and water addition on soil acid neutralizing capacity in an old-field grassland[J]. Chinese Journal of Applied Ecology, 2020,31(5):1579-1586.
[28]
Liang C J, Huang C F, Mohanty N, et al. A rapid spectrophotometric determination of persulfate anion in ISCO[J]. Chemosphere:Environmental Toxicology and Risk Assessment, 2008,73(9):1540-1543.
[29]
温震江,高 谦,王永定,等.基于模糊综合评判的复合胶凝材料开发及料浆配比优化[J]. 中国有色金属学报, 2020,30(3):698-707. Wen Z J, Gao Q, Wang Y D, et al. Development of composite cementitious material and optimization of slurry proportion based on fuzzy comprehensive evaluation[J]. The Chinese Journal of Nonferrous Metals, 2020,30(3):698-707.
[30]
陈守煜,赵瑛琪.模糊优选(优化)理论与模型[J]. 应用数学, 1993, 6(1):1-6. Chen S Y, Zhao Y Q. Fuzzy optimum selecting theory and model[J]. Mathematica Applicata, 1993,6(1):1-6.
[31]
李 丽,张 兴,王亚军,等.过硫酸钠对黄土高原石油类污染土壤的处理[J]. 环境科学与技术, 2020,43(12):159-165. Li L, Zhang X, Wang Y J, et al. Treatment of petroleum hydrocarbons in loess by sodium persulfate[J]. Environmental Science & Technology, 2020,43(12):159-165.
[32]
Karamalidis A K, Voudrias E A. Cement-based stabilization/solidification of oil refinery sludge:Leachingbehavior of alkanes and PAHs[J]. Journal of Hazardous Materials, 2007,148(1/2):122-135.
[33]
刘晓文,李荣飞,李 霞,等.过硫酸钠原位修复三氯乙烯污染土壤的模拟研究[J]. 环境科学学报, 2013,33(11):2935-2940. Liu X W, Li R F, Li X, et al. A model of in situ remediation of TCE-contaminated soil by sodium persulfate[J]. Acta Scientiae Circumstantiae, 2013,33(11):2935-2940.
[34]
张丽娟,何捷聪,陈 逸,等.广州某淤泥地基固化改良试验及优化配比研究[J]. 地下空间与工程学报, 2017,13(2):344-347,369. Zhang L J, He J C, Chen Y, et al. Research on mud foundation solidification improvement experiment and optimal additive portion of a project in Guangzhou[J]. Chinese Journal of Underground Space and Engineering, 2017,13(2):344-347,369.
[35]
JTG/T F20-2015 公路路面基层施工技术细则[S]. JTG/T F20-2015 Technical guidelines for construction of gighway roadbases[S].
[36]
王新民,赵 彬,张钦礼.基于层次分析和模糊数学的采矿方法选择[J]. 中南大学学报(自然科学版), 2008,39(5):875-880. Wang X M, Zhao B, Zhang Q L. Mining method choice based on AHP and fuzzy mathematics[J]. Journal of Central South University (Science and Technology), 2008,39(5):875-880.
周恒宇,王修山,胡星星,等.地聚合物固化淤泥强度增长影响因素及机制分析[J]. 岩土力学, 2021,42(8):2089-2098. Zhou H Y, Wang X S, Hu X X, et al. Influencing factors and mechanism analysis of strength development of geopolymer stabilized sludge[J]. Rock and Soil Mechanics, 2021,42(8):2089-2098.
[39]
Phummiphan I, Horpibulsuk S, Rachan R, et al. High calcium fly ash geopolymer stabilized lateritic soil and granulated blast furnace slag blends as a pavement base material[J]. Journal of Hazardous Materials, 2018,341:257-267.
[40]
吕擎峰,俞晶晶,单小康,等.石膏碱激发地聚物固化黄土强度及机理[J]. 兰州大学学报(自然科学版), 2021,57(2):221-225,232. Lv Q F, Yu J J, Shan X K, et al. A study on the mechanical property and mechanism of loess solidified by gypsum alkali-activated geopolymer[J]. Journal of Lanzhou University (Natural Sciences), 2021,57(2):221-225,232.
[41]
谢首斌,李 敏,杜红普,等.环境温度对石油污染滨海盐渍土强度及变形特性的影响[J]. 工程地质学报, 2016,24(4):616-621. Xie S B, Li M, Du H P, et al. Influence of environment temperature on strength and deformation of saline soil in inshore contaminated by petroleum[J]. Journal of Engineering Geology, 2016,24(4):616-621.
[42]
Ahmadi M, Ebadi T, Maknoon R. Effects of crude oil contamination on geotechnical properties of sand-kaolinite mixtures[J]. Engineering Geology, 2021,283:106021.