炼油行业废催化剂中重金属源释放特征及其影响因素
Leaching of heavy metals and their impacting factors from a spent catalyst in the refinery industry
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摘要: 采用连续分批浸出和柱淋溶方法研究废催化剂中重金属在环境暴露下的源释放特征,其中连续分批浸出实验设置液固比为5:1、10:1和20:1,浸提液pH值为4.5,柱淋溶实验浸提液为pH 4.5、pH 7.0及pH 7.0的浓度20 mg·L-1的DOM溶液.结果表明,连续分批浸出中,酸性条件下废催化剂中重金属浸出率随液固比增大先上升后降低,液固比小时,浸出体系处于饱和状态,随着液固比增大,浸出体系逐渐变为非饱和状态,浸出率逐渐增加,但当液固比对废催化剂中重金属元素的浸出不起控制作用时,浸出率不受液固比影响.浸出机理受浸出体系饱和状态、重金属元素赋存状态和液固比多重控制作用影响;柱淋溶中,酸性条件促进了废催化剂中重金属元素的浸出,累积释放率增加,相较于中性条件,酸性条件下的平均浸出率增加了13.4%,酸性条件未改变废催化剂中重金属元素的释放机理;溶解性有机质条件促进了废催化剂中重金属元素的浸出,累积释放率显著增加,相较于中性条件,溶解性有机质条件下的平均浸出率增加了19.6%,溶解性有机质条件未改变废催化剂中重金属元素的释放机理;连续分批浸出中最大重金属释放率均高于柱淋溶中的最大重金属释放率,且连续分批浸出中重金属浸出机理更易受外界条件影响,环境风险更大.因此在废催化剂的堆存、运输和处置过程中应注意避雨、防渗、隔离等措施,避免废催化剂中的重金属向地表水、地下水和土壤等环境介质中转移,造成更大的环境损害.Abstract: Serial batch leaching and column leaching were used to study the release characteristics of heavy metals in spent catalysts exposed to the environment. The extraction solutions used in the column leaching was pH 4.5, pH 7.0, and a concentration of 20 mg·L-1 of the DOM solution at pH 7.0, the liquid-solid ratio of the serial batch leaching was 5:1, 10:1, and 20:1, and the pH value of the extraction solutions was 4.5. The results show that, in serial batch leaching, under acidic conditions, the leaching rate of heavy metals in the spent catalyst first increases then decreases as the liquid-solid ratio increases. The leaching system is a saturated state when the liquid-solid ratio is small, the leaching system gradually becomes unsaturated and the leaching rate gradually increases as the liquid-solid ratio increases. The leaching rate is not affected by the liquid-solid ratio when the liquid-solid ratio's controlling effect on the leaching of heavy metal elements in the spent catalyst exceeds the threshold. The leaching mechanism is affected by the multiple control effects of the saturation state of the leaching system, the occurrence state of heavy metal elements, and the liquid-solid ratio. In column leaching, acidic solution promoted the leaching of heavy metal in spent catalysts, and the cumulative release rate increased. Compared with neutral conditions, the average leaching rate under acidic conditions increased by 13.4%, acidic conditions did not change the leaching mechanism of heavy metal in spent catalysts. Dissolved organic matter solution promote the leaching, and the cumulative release rate is significantly increased. Compared with neutral conditions, the average leaching rate under dissolved organic matter conditions has increased by 19.6%, and the dissolved organic matter conditions have not Change the leaching mechanism of heavy metal in spent catalysts. The maximum release rate of heavy metals in serial batch leaching is greater than column leaching, and the leaching mechanism of heavy metals in serial batch leaching is more susceptible to external conditions and their has greater environmental risks. Therefore, measures should be taken to rain protection and leakage prevention during the storage, transportation and disposal of spent catalysts to avoid the transfer of heavy metals in the spent catalysts to environmental media such as surface water, groundwater and soil,and prevent greater environmental damage.
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Key words:
- spent catalyst /
- heavy metals /
- column leaching /
- serial batch leaching
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[1] MARAFI M, STANISLAUS A. Spent catalyst waste management:A review part I-Developments in hydroprocessing catalyst waste reduction and use[J]. Resources, Conservation and Recycling, 2008, 52:859-873. [2] ROJASRODRIGUEZ A D, FLORESFAJARDO O, GONZALEZ F S, et al. Chemical treatment to recover molybdenum and vanadium from spent heavy gasoil hydrodesulfurization catalyst[J]. Advances in Chemical Engineering and Science, 2012, 2(3):408-412. [3] AKCIL A, VEGLIO F, FERELLA F, et al. A review of metal recovery from spent petroleum catalysts and ash[J]. Waste Management, 2015, 45(11):420-433. [4] 刘健, 邱兆富, 杨骥, 等. 我国石油化工废催化剂的综合利用[J]. 中国资源综合利用, 2015, 33(6):38-42. LIU J, QIU Z F, YANG J, et al. The Comprehensive utilization of spent petrochemical catalysts in China[J]. China Resources Comprehensive Utilization, 2015, 33(6):38-42(in Chinese).
[5] 生态环境部.《中华人民共和国固体废物污染环境防治法》附件:国家危险废物名录[Z]. 2016. Ministry of Ecology and Environmental of the People's Republic of China. Law of the People's Republic of China on the Prevention and Control of Solid Waste Pollution:National Catalogue of Hazardous Wastes[Z]. 2016(in Chinese). [6] 周德杰. 危险废弃物中毒性组分浸出特性和浸出方法研究[D]. 济南:山东大学, 2006. ZHOU D J, Study on leaching characteristics and leaching method of toxic compounds in hazardous waste[D]. Jinan:Shandong University, 2006(in Chinese). [7] EPA Method 1320, Multiple extraction procedure[S]. U.S Environmental Protection Agency, 1986. [8] NEN 7343, Leaching characteristics of solid (earth and stony) building and waste materials. Leaching tests[S]. Determination of the leaching of inorganic constituents from granular materials with the column test, First edition, Netherlands Normalization Institute, 1995. [9] 王希尹. 固废生产建材中重金属浸出方法研究[D]. 重庆:重庆交通大学, 2018. WANG X Y. Study on leaching methods of heavy metals in solid waste production building materials[D]. Chongqing:Chongqing Jiaotong University, 2018(in Chinese). [10] HJ/T 298-2007, 危险废物鉴别技术规范[S]. 国家环境保护总局, 2007. HJ/T 298-2007, Technical specifications on identification for hazardous waste[S]. Ministry of Ecology and Environmental of the People's Republic of China, 2007(in Chinese). [11] GALVIN A P, AYUSO J, JIMENEZ J R, et al. Comparison of batch leaching tests and influence of pH on the release of metals from construction and demolition wastes[J]. Waste Management, 2012, 32(1):88-95. [12] HJ 557-2010, 固体废物浸出毒性浸出方法-水平振荡法[S]. 生态环境保护部, 2010. HJ 557-2010, Solid waste-extraction procedure for leaching toxicity-horizontal vibration method[S]. Ministry of Ecology and Environmental of the People's Republic of China, 2010(in Chinese). [13] HJ 299-2007, 固体废物浸出毒性浸出方法-硫酸硝酸法[S]. 生态环境保护部, 2007. HJ 299-2007, Solid waste-extraction procedure for leaching toxicity sulphuric acid and nitric acid method[S]. Ministry of Ecology and Environmental of the People's Republic of China, 2007(in Chinese). [14] GB 5085.3-1996, 危险废物鉴别标准-浸出毒性鉴别[S]. 生态环境保护部, 1996. GB 5085.3-1996, Identification standard of hazardous waste-identification of extraction toxicity[S]. Ministry of Ecology and Environmental of the People's Republic of China, 1996(in Chinese). [15] HJ 781-2016, 固体废物中22种金属元素的测定-电感耦合等离子体发射光谱法[S]. 生态环境保护部, 2016. HJ 781-2016, Solid waste-determination of 22 metal elements-Inductively coupled optical emission spectrometry[S]. Ministry of Ecology and Environmental of the People's Republic of China, 2016(in Chinese). [16] GB/T19500-2004, X射线光电子能谱分析方法通则[S]. 中国国家标准化管理委员会, 2004. GB/T19500-2004, General rules for x-ray photoelectron spectroscopic analysis method[S]. Standardization administration, 2004(in Chinese). [17] COURSON C, MAKAGA E, PETIT C, et al. Development of Ni catalysts for gas production from biomass gasification. Reactivity in steam-and dry-reforming[J]. Catalysis Today, 2000, 63(2):427-437. [18] TOWNSEND T, JANG Y. C, TOLAYMAT T. A guide to the use of leaching tests in solid waste management decision making[R]. 2011. [19] TRIBOUT C, HUSSON B, NZIHOU A. Use of treated dredged sediments as road base materials:Environmental assessment[J]. Waste & Biomass Valorization, 2011, 2(3):337-346. [20] ECKE H, ABERG A. Quantification of the effects of environmental leaching factors on emissions from bottom ash in road construction[J]. Science of the Total Environment, 2006, 362(1-3):42-9. [21] LOMBARDI F, MANGIALARDI T, PIGA L, et al. Mechanical and leaching properties of cement solid wasted hospital solid waste incinerator fly ash[J]. Waste Management, 1998, 18:99-106. [22] 苏光明, 胡恭任, 毛平平, 等. 模拟酸雨对泉州市交通区表层土壤重金属淋溶的累积释放特征[J]. 地球与环境, 2013, 41(5):512-517. SU G M, HU G R, MAO P P, et al. Release characteristics of heavy metals in the traffic-area topsoil leached by simulated acid rain[J]. Earth and Environment, 2013, 41(5):512-517(in Chinese).
[23] 何品晶, 吴长淋, 章骅, 等. 生活垃圾焚烧飞灰及其稳定化产物的长期浸出行为[J]. 环境化学, 2008, 27(6):786-790. HE P J, WU C L, ZHANG Y, et al. Long-term leaching behavior of fly ash from domestic waste incineration and its stabilized products[J]. Environmental Chemistry, 2008, 27(6):786-790(in Chinese).
[24] GUO Y, HUANG P, ZHANG W, et al. Leaching of heavy metals from dexing copper mine tailings pond[J]. Transactions of Nonferrous Metals Society of China, 2013, 23(10):3068-3075. [25] 赵述华, 陈志良, 张太平, 等. 稳定化处理对矿渣中重金属迁移转化的影响研究[J]. 环境科学, 2014, 35(4):1548-1554. ZHAO S H, CHEN Z L, ZHANG T P, et al. Effects of stabilization treatment on migration and transformation of heavy metals in mineral waste residues[J]. Environmental Science, 2014, 35(4):1548-1554(in Chinese).
[26] KALBITZ K, SOLINGER S, PARK J H, et al. Controls on the dynamics of dissolved organic matter in soils:A review[J]. Soil Science, 2000, 165(4):277-304. [27] AIKEN G R, MCNIGHT D M, WERSHAW R L, et al. Humic substances in soil, sediment, and water:Geochemistry, isolation, and characterization[M]. New York:Wiley, 1985. [28] BENNETT G F, MICHAEL E. Soil and water chemistry:An integrative approach[M]. Boca Raton:CRC press, 2015. [29] STUMM W. Aquatic surface chemistry:Chemical processes at the particle-water interface[M]. New York:Wiley, 1987. [30] BI Y Q. Production of co-siderophore complexes by ligand-promoted dissolution[D]. Raleigh:North Carolina State University, 2009. [31] GU B H, SCHMITT J, CHEN Z, et al. Adsorption and desorption of natural organic matter on iron oxide:Mechanisms and models[J]. Environmental Science and Technology, 1994, 28(1):38-46. -

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