16. 481 Solidification-stabilization

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环境工程专业英语汇总

环境工程专业英语汇总

专业英语环境:environment 环境工程:environmental engineering环境保护:environmental protection 环境意识:environmental consciousness/awareness 环境问题:environmental issue/problem 环境效应:environmental effect环境污染:environmental pollution 环境要素:environmental elements环境因子:environmental factors 环境化学:environmental chemistry环境生态学:environmental ecology 环境质量:environmental quality环境自净作用:environmental self-purification/self-cleansing水环境:watershed 水体:water body流域:watershed 水质:water quality水资源:water resources 供水:water supply废水:waste water 水处理:water treatment物理性水质指标:physical indicate of water quality 水污染物:water pollutant生物性水质指标:biological water-quality index 水质标准:water quality standard化学性水质指标:chemical water-quality indexDS:dissolved solids BOD:biochemical oxygen demand TDS:total dissolved solids COD:chemical oxygen demand TSS:total suspended solids DO:dissolved oxygenTOC:total organic carbon PH值:TN:总氮total nitrogen TP:总磷phosphorusZn:zinc Cu:CopperAs:arsenic Cd:CadmiumCr:chromium Ni:NickelHg:mercury Pb:plumbum物理处理:physical treatment 过滤:screening生物处理:biological treatment 沉淀:sedimentation化学处理:chemical treatment 气浮:flotation物理化学处理:physical-chemical treatment蒸发:evaporation 稀释:dilution扩散:dispersion 吹脱:stripping好氧处理:aerobic treatment 生物膜法:bio-membrane process 厌氧处理:anaerobic treatment 生物滤池:trickling filters活性污泥法:activated sludge process 生物接触氧化:biological contact SBR:苯乙烯-丁二烯Styrene Butadiene RubberUASB(流式厌氧污泥床):Upflow anaerobic sludge blanket 活性污泥:activated sludge 改进型:modification 一级处理:primary treatment二级处理:secondary treatment 三级处理:tertiary treatment高级氧化处理:advanced treatment 生活污水:domestic wastewater生产废水:industrial wastewater 城市生活污水:municipal wastewater电镀废水:metalplating plants印染废水:pulp and paper industries wastewater 浊度:turbidity硬度:hardness 水质净化:water quality purifies混凝沉淀:coagulate flocculating agent 活性炭吸附:activated carbon adsorption隔油池:oil separation tank 中和池:neutralization tank调节池:adjusting tank 生物反应池:biological reactor加药设备:physical equipment 沉淀池:sedimentation tank初沉池:primary sedimentation tank 二沉池:secondary sedimentation tank絮凝剂:flocculant 混凝剂:coagulate flocculant生物降解:biodegradation 生物累积:bioaccumulation飘尘:floating dust 可吸入颗粒物:inhalable particles能见度:visibility 酸雨:acid rain一次污染物:primary pollutant二次污染物:secondary pollutant 氮氧化物:nitrogen oxides硫氧化物:sulfur oxides硫化氢:hydrogen sulfide 碳氧化物:carbon oxides硝酸:nitric acid 盐酸:hydrochloric acid硫酸:sulfuric acid 二氧化硫:sulfur dioxide除尘工艺:Dust removal吸收:absorption 吸附:adsorption静电除尘:electric dust precipitation 重力除尘:gravitational settling臭氧:ozone光化学烟雾:photochemical smoke 喷淋(洗涤):scavenging土壤:soil 热污染:temperature change/thermal pollution 噪声:noise 放射性:radioactivityEIA:environmental impact assessment CAD(计算机辅助设计):computer aided design大气污染控制工程:air pollution control水污染控制工程:water pollution control固体废物污染控制工程:solid waste management污染源:pollution source同化作用:assimilation 固体废物:solid wastes危险废物:hazardous wastes化学污泥chemical sludge:生物污泥:biological sludge工业固废:industrialwastes 分选处理:separation treatment 矿业固废:mine solid wastes 破碎处理:processing农业固废:agriculture solid wastes 压实处理:reduction in volume污泥脱水:disposal of the sludge ?污泥浓缩:sludge thickening带式压滤:Belt filter press离心脱水:centrifugal dewatering筛分:screening堆肥和堆肥化:compost and composting沼气和沼气化:biogas热解与焚烧:pyrolysis and incineration生物转化作用:biotransformation热化学转化作用:thermo-chemical固化和稳定化作用:solidification and stabilization资源化:resource减量化:pollution control无害化:harmlessness固体废物全过程控制:solid waste integrated control固体废物污染控制:solid waster pollution control固体废物处理:processing and recovery处置:disposal物质回收:materials recovery 物质转化:material conversion能量回收:energy recovery 能量转化:energy conversion1.Environmental engineering has been defined as the branch of engineering that is concernedwith protecting the environment from the potential, deleterious effects of human activity, protecting human populations from the effects of adverse environmental factors, and improving environmental quality for human health and well-being.(2页)环境工程学是环境工程的分支学科,其研究内容包括①保护环境免受人类活动改造形成的潜在和不利影响②保护人类免受不利环境因素的影响③持续改善环境质量,以造福于人类健康与福祉。

浸出毒性实验

浸出毒性实验

浸出毒性实验一实验目的1.了解市政污泥脱水泥饼处理工艺及浸出毒性的实验方法。

2.掌握泥饼中重金属的固化机理。

二实验原理污泥中含有大量的重金属,包括生物毒性显著的Cr、Cd、Pb、Hg以及类金属As,以及具有毒性的重金属Zn、Cu、Co、Ni、Sn、V等。

其中Cr、Cd、Pb、Cu、Hg、As、Be、Ni、Tl被列入“中国环境优先污染物黑名单”。

它们会对人体和环境造成严重危害。

表1-1列出了污泥中重金属的来源及危害。

表1 污泥中重金属的来源及对人体的危害种类来源对人体的危害Cr含铬矿石加工、重金属表面处理、皮革、印刷、耐火材料等六价铬有强氧化作用,会引发慢性中毒三价铬毒性小,但更易被吸收和蓄积Cd 电镀、颜料、塑料、合金、电池业等刺激呼吸道,损伤肾脏,能长期潜伏Pb 蓄电池、冶金、机械、涂料、电镀等“三致”,积累性伤害,有机铅毒性更大Zn 有色金属冶炼等急性中毒为主,血压升高、气促、休克等Cu 有色金属冶炼、能源、化工等急性胃肠炎,发热、高烧,特别是硫酸铜Ni 镍矿开采冶炼等致癌,致敏,羧基镍毒性特别大Hg 工业汞原料、含汞农药等急性为肾脏损伤,慢性为肺炎、呼吸衰竭As 印刷合金、电镀废水等心血管、神经、呼吸等多种急慢性损伤城市污泥产量巨大,同时重金属在不同性质污泥中的成分、含量、形态分布不同,因此采用固化/稳定化方法处理污泥中的重金属是一种更为经济有效的方法[26]。

固化(Solidfication)是指添加固化剂于废弃物中,使其变为不可流动性或形成固体的过程,而不管废弃物与固化剂间是否产生化学结合[19]。

稳定化(Stabilization)是指将有害污染物转变成低溶解性、低毒性及低移动性的物质,以减少有害物潜力的技术。

实际工程中经常将重金属的固化/稳定化(Solidification/Stabilization,简称为S/S)结合起来使用。

目前常见的污泥固化技术主要包括:水泥固化、石灰固化、塑性材料固化、熔融固化、自胶结固化和大型包胶固化等。

污染土壤的固化稳定化处理技术---以水泥固化技术为例

污染土壤的固化稳定化处理技术---以水泥固化技术为例
技术应用范围
固化/稳定(solidification/stabilization, S/S)是比较成熟的废物处置技术,经过几 十年的研究,已成功应用于放射性废物、 底泥和工业污泥的无害化和资源化。与其 他技术相比,该技术具有处理时间短、适 用范围较广等优势,因此美国环保局曾将 固化/稳定化技术称为处理有毒有害废物的 最佳技术。
污染土壤的固化/稳定化处理技术 (solidification/stablization,S/S) ---以水泥固化技术为例
曹琳 2014-12-11
背景
由于重金属污染具有污染范围广、 持续时间长、污染隐蔽性、无法被生 物降解,并可能通过食物链不断在生 物体内富集,最后总在人体内蓄积而 危害健康的特点,因此土壤重金属污 染日益引起人们的关注。
水泥固化技术原理
水泥是一种无机胶结材料,经过水化 反应后可以生成坚硬的水泥固化体,水泥 固化的机理主要是在水泥水化过程中,重 金属可以通过吸附、化学吸收、沉降、离 子交换、钝化等多种方式与水泥发生反应 最终以氢氧化物或络合物的形式停留在水 泥水化形成的水化硅酸盐胶体表面,同时 水泥的加入也为重金属提供了碱性环境, 抑制重金属的渗滤。
News:湖南桃源铝项目致污染:农 作物变异 十余村民患癌
固化土壤修复技术(又叫稳定化土壤修复 技术),固化技术包含两个概念。 其一,固化是指利用水泥一类的物质与土 壤相混合将污染物包被起来,使之呈颗粒状或 块状存在,进而使污染物处于相对稳定的状态。 其二,利用封装对污染土壤进行压缩隔离。 固化不涉及固化物或固化的污染物之间的 化学反应,其主要是利用磷酸盐、硫化物和碳 酸盐等作为污染物稳定化处理的反应剂,将有 害化学物质转化成毒性较低或迁移性较低的物 质。
水泥固化技术的缺点

水泥固化锌污染黏土的压缩特性试验研究_魏明俐

水泥固化锌污染黏土的压缩特性试验研究_魏明俐

第44卷增刊2011年土木工程学报CHINA CIVIL ENGINEERING JOURNALVol.442011基金项目:国家自然科学基金(50878052,40972173),江苏省科技支撑计划(BK2010060)和教育部新世界优秀人才计划(NCET-09-0286)作者简介:魏明俐,博士研究生收稿日期:2011-07-05水泥固化锌污染黏土的压缩特性试验研究魏明俐杜延军张帆(东南大学岩土工程研究所,江苏南京210096)摘要:通过压缩试验对不同水泥掺量、不同锌离子浓度的水泥固化污染土的压缩特性进行研究,分析水泥固化锌污染土的固结屈服应力p y '、压缩指数C c 与水泥掺量和锌离子浓度的关系;引入评价天然重塑黏土固有压缩特性的孔隙指数I v ,对压缩试验结果进行正规化处理,进一步探讨不同水泥掺量下不同锌离子浓度污染土的压缩特性。

结果表明,锌离子浓度对于水泥固化污染土的压缩特性和结构性具有显著影响。

锌离子浓度越高,水泥固化锌污染土的结构性越差,固结屈服应力p y '和压缩指数C c 越低。

关键词:固化稳定;压缩;固结屈服应力中图分类号:TU442文献标识码:A文章编号:1000-131X (2011)S2-0165-04Compressibility of cement solidified /stabilized zinc contaminated claysWei MingliDu YanjunZhang Fan(Institute of Geotechnical Engineering ,Southeast University ,Nanjing 210096,China )Abstract :To investigate the compressibility of cement solidified /stabilized zinc contaminated clays ,a series of oedometer tests were performed.The effects of zinc concentration and cement content on yield stress and compression index were investigated.The results were analyzed using the generalized state parameter void index I v ,which was used to characterize the intrinsic properties of remolded sedimentary natural clays.It is found that zinc concentration has considerable influence on the structure of cement solidified zinc contaminated clays.The structure of the clays degraded with increasing zinc concentration.Keywords :solidification /stabilization ;compression ;yield stress E-mail :duyanjun@seu.edu.cn引言压缩变形特性是土体力学性质的重要方面,经过固化/稳定法(solidification /stabilization )处理后的水泥固化重金属污染土作为地基使用时需考虑其压缩特性。

浸出毒性实验

浸出毒性实验

浸出毒性实验一实验目的1.了解市政污泥脱水泥饼处理工艺及浸出毒性的实验方法。

2.掌握泥饼中重金属的固化机理。

二实验原理污泥中含有大量的重金属,包括生物毒性显著的Cr、Cd、Pb、Hg以及类金属As,以及具有毒性的重金属Zn、Cu、Co、Ni、Sn、V等。

其中Cr、Cd、Pb、Cu、Hg、As、Be、Ni、Tl被列入“中国环境优先污染物黑名单”。

它们会对人体和环境造成严重危害。

表1-1列出了污泥中重金属的来源及危害。

表1 污泥中重金属的来源及对人体的危害种类来源对人体的危害Cr含铬矿石加工、重金属表面处理、皮革、印刷、耐火材料等六价铬有强氧化作用,会引发慢性中毒三价铬毒性小,但更易被吸收和蓄积Cd 电镀、颜料、塑料、合金、电池业等刺激呼吸道,损伤肾脏,能长期潜伏Pb 蓄电池、冶金、机械、涂料、电镀等“三致”,积累性伤害,有机铅毒性更大Zn 有色金属冶炼等急性中毒为主,血压升高、气促、休克等Cu 有色金属冶炼、能源、化工等急性胃肠炎,发热、高烧,特别是硫酸铜Ni 镍矿开采冶炼等致癌,致敏,羧基镍毒性特别大Hg 工业汞原料、含汞农药等急性为肾脏损伤,慢性为肺炎、呼吸衰竭As 印刷合金、电镀废水等心血管、神经、呼吸等多种急慢性损伤城市污泥产量巨大,同时重金属在不同性质污泥中的成分、含量、形态分布不同,因此采用固化/稳定化方法处理污泥中的重金属是一种更为经济有效的方法[26]。

固化(Solidfication)是指添加固化剂于废弃物中,使其变为不可流动性或形成固体的过程,而不管废弃物与固化剂间是否产生化学结合[19]。

稳定化(Stabilization)是指将有害污染物转变成低溶解性、低毒性及低移动性的物质,以减少有害物潜力的技术。

实际工程中经常将重金属的固化/稳定化(Solidification/Stabilization,简称为S/S)结合起来使用。

目前常见的污泥固化技术主要包括:水泥固化、石灰固化、塑性材料固化、熔融固化、自胶结固化和大型包胶固化等。

The Application and Prospect of Stabilization Solidification Technology for Hazardous

The Application and Prospect of Stabilization Solidification Technology for Hazardous

The Application and Prospect of Stabilization/SolidificationTechnology for Hazardous【Abstract】The number of hazardous waste in our country increased dramatically in recent years, stabilization/solidification technology begins to attract a wide spread attention by domestic scholars. Based on the domestic related literature, this paper discussed the present situation about the treatment of the solid waste using stabilization/solidification technology; meanwhile we have a variety of outlooks on the future of the stabilization/solidification technology.【Key words】Stabilization/solidification technology;Hazardous waste;Cement;MSW fly ash;Sludge0SummaryStabilization/solidification technology is a method of disposal of hazardous waste. It is widely used at home and abroad with good treatment effect.Stabilization/solidification technology is a kind of Physical-Chemical methods, which will be inclusive of harmful substances in certain fixed inert substrate that makes it difficult to eliminate pollution of the leaching process.Compared with developed countries, the amount of solidification technology in China is still relatively small.Based on the domestic related literature, this paper summarizes the solid waste stabilization/solidification technology in China to provide useful reference for future waste treatment.1Stabilization/solidification technology for MSW fly ashWith the the development of economy and the enlargement of city size, the total quantity of the MSW fly ash is increasing by 8%~10% per year. Because of advantage in processing speed, volume reduction ratio and weight reduction, the incinerating municipal solid waste (MSW) method has been widely adopted [1].The cement solidification technology is main methods of solving the MSW fly ash. Song Zhenxia, Wang Li-ao[2] study on cement solidification of MSW fly ash, they pickling fly ash at first and improve the solidification effect. Wang Zhengyu[3] in Tung Chi University take a similar research too, he used the copperas as stabilization agents, made the Pb, Cd and Cr concentration decreased significantly in the solidifiedbody. Meanwhile, the strength of the solidified body is improving more than 20%. Xu lili[4] in Southwest JiaoTong University researched the effect on cement solidification which added the NaOH, Na2S etc. and the results showed that Na2S played best auxiliary function on the cement solidification method.Some scholars were dedicated to find a kind of curing agent with the lower compatibilization ratio to replace cement. For example, Zhang Yan, Jiang Jianguo [5] used the apatite as the stabilization agents for fly ash, and found that products had a good stability within a certain range of pH (3~11). In further research, they found that if the soluble phosphate addition amount reached 3 %( mass ratios), the removal rate of the Pb, Cd, Zn in the fly ash would be 97.5 %,91.6 %,95.5 %[6]. Zhang Haijun, Yu Yang [7] studied on treatment effect of three kinds of sulphydryl collectors for fly ash. The experimental results indicated that the products have a good stability under the neutral and alkaline conditions (pH>6). This research is very important significance for the future research of the solidification technology.Our country should develop pharmaceutical stabilization technology energetically. On one hand,we can achieve waste harmless, then make little or no capacity increase and improve the overall efficiency and economical efficiency of the hazardous waste treatment and disposal system. On the other hand, we can improve the long-term stability of the stabilization and reduce the problems of the secondary pollution brought by the stabilization.【参考文献】[1]Li Jianxin, Yan Jianhua, Ni Mingjiang etc. Stabilization Treatment for Heavy Metal in MSW Fly Ash [J]. Thermal Power Generation, 2003(12):64-68.[2]Song Zhenxia, Wang Li-ao, Lin Xiang etc. Study on Characteristics and Cement Curing Test of MSW Fly Ash [J]. Environmental Science, 2008.21 (4)163-168.[3]Wang Zhengyu. Study on the Composite Stabilization/solidification technology of MSW Fly Ash [D]. ShangHai: TongJi University. 2007[4]Xu Lili. Study on the Leaching Characteristics of Heave Metals and Cement Curing Test of MSW Fly Ash [D]. SiChuan: Southwest JiaoTong University, 2007.[5]Zhang Yan, Jiang Jianguo, Deng Zhou etc. Chemical Stabilization Technology in Treating with Fly ash Using Apatite[J].(下转第56页)(上接第58页)Environmental Science, 2006, 27(1):189-192.[6]Jiang Jianguo, Zhang Yan, Xu Xin etc. Stabilization Technology with Soluble Phosphate For MSW Fly Ash [J]. Environmental Science, 2005, 26(4):191-194.[7]Zhang Haijun, Yu Ying, Ni Yuwen etc. Stabilizing Treatment with Sulphydryl Collectors for Heave Metals in the MSW Fly Ash [J]. Environmental Science, 2007, 28(8):1899-1904.[8]Zhang Dajie, Liu Wenshi, Tian Xiaofeng etc. Solidification Treatment of MSW Fly Ash with Slag Cementitious Binder [J]. Environmental Engineering, 2008, 26(4):14-16.[9]Chen Xi. Study on the Solidification Treatment of MSW Fly Ash with Alkali-activated Slag [D]. BeiJing: BeiJing Chemical Engineering University, 2008.[10]Zhu Wei, Lin Cheng, Li Lei etc. Study on the Test of Bentonite Used As Additive to Stabilize/Solidifies the Sewage Sludge [J]. Environmental Science, 2007, 28(5):1020-1025.[11]Fang Di, Zhao Liang etc. The Preliminary Study on the Test of Alkali-activated Slag Used As Additive to Stabilize/Solidifies the Biological Virus-free Sediment [J]. Journal of Application Base and Engineering Science, 2009, 17(6):859-866.[12]Ma Jianli, Zhao Youcai, Niu Dongjie etc. Study on Stabilization for Sewage Sludge with Alkaline Mode Gelling [J]. Environmental Science, 2009, 30(3):845-850.[13]Zhou Xuefei, Zhang Yalei, Zhang Ming etc. Research of Stabilizing Treatment Effect and Mechanism of Heavy Metal in the Sediment of Jinshan Lake [J]. Environmental Science, 2008, 29(6):1705-1712.[14]Zhou Jianbo, Ning Xun-an, Liu Jingyong etc. Research of Solidification/Stabilization Treatment of Printing Sludge [J]. Journal of Environmental Engineering, 2011, 5(2):457-461.[15]Jiang Jianguo, Wang Wei etc. Current Situation and Development of Solidification/Stabilization Technology for Hazardous Waste [J]. Advance for Environmental Science, 1998,6(1):55-62.。

环境工程专业英语汇总

环境工程专业英语汇总

专业英语环境:environment环境工程:environmentalengineering环境保护:environmentalprotection环境意识:environmentalconsciousness/awareness环境问题:environmentalissue/problem环境效应:environmentaleffect环境污染:environmentalpollution环境要素:environmentalelements环境因子:environmentalfactors环境化学:environmentalchemistry环境生态学:environmentalecology环境质量:environmentalquality环境自净作用:environmentalself-purification/self-cleansing 水环境:watershed水体:waterbody流域:watershed水质:waterquality水资源:waterresources供水:watersupply废水:wastewater水处理:watertreatment物理性水质指标:physicalindicateofwaterquality水污染物:waterpollutant生物性水质指标:biologicalwater-qualityindex水质标准:waterqualitystandard化学性水质指标:chemicalwater-qualityindexDS:dissolvedsolidsBOD:biochemicaloxygendemandTDS:totaldissolvedsolidsCOD:chemicaloxygendemand TSS:totalsuspendedsolidsDO:dissolvedoxygenTOC:totalorganiccarbonPH值:TN:总氮totalnitrogenTP:总磷phosphorusZn:zincCu:CopperAs:arsenicCd:CadmiumCr:chromiumNi:NickelHg:mercuryPb:plumbum物理处理:physicaltreatment过滤:screening生物处理:biologicaltreatment沉淀:sedimentation化学处理:chemicaltreatment气浮:flotation物理化学处理:physical-chemicaltreatment蒸发:evaporation稀释:dilution扩散:dispersion吹脱:stripping好氧处理:aerobictreatment生物膜法:bio-membraneprocess 厌氧处理:anaerobictreatment生物滤池:tricklingfilters 活性污泥法:activatedsludgeprocess生物接触氧化:biologicalcontactSBR:苯乙烯-丁二烯StyreneButadieneRubberUASB(流式厌氧污泥床):Upflowanaerobicsludgeblanket活性污泥:activatedsludge改进型:modification一级处理:primarytreatment二级处理:secondarytreatment三级处理:tertiarytreatment高级氧化处理:advancedtreatment生活污水:domesticwastewater 生产废水:industrialwastewater城市生活污水:municipalwastewater电镀废水:metalplatingplants印染废水:pulpandpaperindustrieswastewater浊度:turbidity 硬度:hardness水质净化:waterqualitypurifies混凝沉淀:coagulateflocculatingagent活性炭吸附:activatedcarbonadsorption隔油池:oilseparationtank中和池:neutralizationtank调节池:adjustingtank生物反应池:biologicalreactor加药设备:physicalequipment沉淀池:sedimentationtank初沉池:primarysedimentationtank二沉池:secondarysedimentationtank絮凝剂:flocculant混凝剂:coagulateflocculant生物降解:biodegradation生物累积:bioaccumulation飘尘:floatingdust可吸入颗粒物:inhalableparticles能见度:visibility酸雨:acidrain一次污染物:primarypollutant二次污染物:secondarypollutant氮氧化物:nitrogenoxides 硫氧化物:sulfuroxides硫化氢:hydrogensulfide碳氧化物:carbonoxides硝酸:nitricacid盐酸:hydrochloricacid硫酸:sulfuricacid二氧化硫:sulfurdioxide除尘工艺:Dustremoval吸收:absorption吸附:adsorption静电除尘:electricdustprecipitation重力除尘:gravitationalsettling臭氧:ozone光化学烟雾:photochemicalsmoke喷淋(洗涤):scavenging 土壤:soil热污染:temperaturechange/thermalpollution 噪声:noise放射性:radioactivityEIA:environmentalimpactassessmen tCAD(计算机辅助设计):computeraideddesign大气污染控制工程:airpollutioncontrol水污染控制工程:waterpollutioncontrol 固体废物污染控制工程:solidwastemanagement污染源:pollutionsource同化作用:assimilation固体废物:solidwastes危险废物:hazardouswastes 化学污泥chemicalsludge:生物污泥:biologicalsludge工业固废:industrialwastes分选处理:separationtreatment 矿业固废:minesolidwastes破碎处理:processing农业固废:agriculturesolidwastes压实处理:reductioninvolume污泥脱水:disposalofthesludge?污泥浓缩:sludgethickening 带式压滤:Beltfilterpress 离心脱水:centrifugaldewatering 筛分:screening堆肥和堆肥化:compostandcomposting沼气和沼气化:biogas热解与焚烧:pyrolysisandincineration 生物转化作用:biotransformation热化学转化作用:thermo-chemical固化和稳定化作用:solidificationandstabilizati on资源化:resource减量化:pollutioncontrol无害化:harmlessness固体废物全过程控制:solidwasteintegratedcontrol 固体废物污染控制:solidwasterpollutioncontrol 固体废物处理:processingandrecovery处置:disposal物质回收:materialsrecovery 物质转化:materialconversion 能量回收:energyrecovery能量转化:energyconversion1.Environmentalengineeringhasbeendefinedasthebranchofengineeringthatisconcernedwithprotectingtheenvironmentfromthepotential,deleteriouseffectsofhumanactivity,protectinghuman populationsfromtheeffectsofadverseenvironmentalfactors,andimprovingenvironmentalqualit yforhumanhealthandwell-being.(2页)环境工程学是环境工程的分支学科,其研究内容包括①保护环境免受人类活动改造形成的潜在和不利影响②保护人类免受不利环境因素的影响③持续改善环境质量,以造福于人类健康与福祉。

砷污染场地土壤的稳定化技术工程应用研究

砷污染场地土壤的稳定化技术工程应用研究

供试土壤
WSL WSX FZ FZS
As 总量 / ( mg/kg) 4 120. 0 1 210.0 95 334. 5

表1供试土壤的基本信息 Table 1 Basic information of tested soils
水中As浸出浓度/ pH
(mg/L)
修复目标
1.49 10.2 177.0 63.6
供试土壤
投加比/%
FБайду номын сангаасM
CF
WSL
1、2、3
2、3、3. 5
WSX
5、10、20
10、20
FZ
3、5、10
15、20、30
MPA修复材料对高浓度神污染土壤的稳定化 效果试验:针对高浓度神污染土壤样品FZ,以MPA1 /I/皿系列材料进行稳定化效果对比和投加比调 节。具体稳定化试验方案如表3所示。
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环境工程技术学报
第11卷
表3 MPA修复材料FZ 土壤稳定化试验方案设计 Table 3 Design of batch experimental scheme of FZ soil
stabilization by MPA remediation materials
供试 土壤
FZ
MPA- I 10、12、15、20
WSX及FZ)进行稳定化小试试验,比较Fen/Mg复 配型(F2M)、Ca/Fe 复配型(CF)及 MetaPro©-ani (As)系列修复材料(MPA)对土壤中神污染的稳定 化效果,进一步分析修复材料用量对稳定化效果的 影响,并选择稳定化效果较优材料进行工程化施工 验证(基于FZS 土壤样品)。
Vol. 11, No.4 July, 2021
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Ex-situ Process - Pozzolan/Portland Cement
The process consists primarily of silicates from pozzolanic-based materials like fly ash, kiln dust, pumice, or blast furnace slag and cement-based materials like Portland cement.
6
System Design
No well established design protocol Select appropriate formulation Waste removal, transportation, storage Mixing Setting and curing Waste transportation
Ex-situ Process
Factors limit process: Environmental conditions Applicability may affect the long-term The target immobilization. contaminant group is Some increase the volume. inorganics, including Certain wastes are radionuclides. incompatible with different Limited effectiveness processes. against organics and Organics are generally not pesticides, except immobilized. vitrification which Long-term effectiveness destroys most has not been organic contaminants. demonstrated for many.
5
Factors Affecting S/S Process
Particle size and shape Solid content (too watery?) Specific gravity (phase separation?) Wetting (add surfactant?) Mixing (over-mixing affects gel formation?) Temperature (release of steam, and break up the solid mass) Chemical (some can retard or accelerate setting and curing)
Pozzolanic and cement-based binding agents are typically appropriate for inorganic contaminants.
The effectiveness of this binding agent with organic contaminants varies.
These materials chemically react with water to form a solid cementious matrix. They also raise the pH of the water which may help precipitate and immobilize some heavy metal contaminants.
CE 481 - Solidification/Stabilization
Jeff Kuo, Ph.D., P.E jkuo@
1
Introduction
Solidification/stabilization (S/S) reduces the mobility of hazardous contaminants through both physical and chemical means. S/S seeks to trap or immobilize contaminants within their "host" medium. Leachability testing is typically performed to measure the immobilization of contaminants. S/S techniques can be used alone or combined with other treatment methods to yield a product or material suitable for land disposal or, in other cases, that can be applied to beneficial use.
Immobilization Mechanisms
Chemical reactions

Precipitation Redox
Organic waste encapsulated in binder matrix.

Complexation
Adsorption Encapsulation

7
Ex-situ Process
Bituminization The process combines heated bitumen and a concentrate of the waste material, usually in slurry form, in a heated extruder containing screws that mix the bitumen and waste. Water is evaporated from the mixture to about 0.5% moisture. Emulsified Asphalt Asphalt emulsions are very fine droplets of asphalt dispersed in water that are stabilized by chemical emulsifying agents. The process adds emulsified asphalts having the appropriate charge (cationic or anionic) to hydrophilic liquid or semi-liquid wastes at ambient temperature.
micro macro
Organic waste adsorbed 4 to an organophilic clay
Common S/S Systems
Organic system bitumen polymers organophilic clay Inorganic System cement-based pozzolanic lime sodium silicates
8
Ex-situ Process
Modified Sulfur Cement A thermoplastic material, easily melted (127 to 149 °C) and then mixed with the waste. The relatively low T used limit emissions of sulfur dioxide and hydrogen sulfide t. Polyethylene Extrusion The process mixes PE binders and dry waste using a heated cylinder containing a screw. The process has been tested on nitrate salt wastes at plant-scale, establishing its viability, and on various other wastes at the bench and pilot scale. 9
2
Introduction Objectives
Pocket penetrometer evaluating a stabilized waste.
Production of solid for liquid or semi-liquid Reduction of contaminant solubility (and toxicity) Decrease in the exposed area across which transfer may occur Solidification: Increase strength Decrease compressibility Decrease K Stabilization Convert the contaminants to their less toxic or least soluble form 3 Metal fixation
Cost Ex situ S/S processes are among the most mature remediation technologies.
Data from more than a dozen vendors indicate an approximate cost of under $110 per metric ton ($100 per ton), including excavation.
10
Vitrification/Molten Glass Ex-situ Process The processes employ heat up to 1,200° C to convert Soluble Phosphates waste materials into glassy The process adds products. phosphate and alkali for The high T destroys any control of pH to complex organic constituents with metal molecules of lowvery few byproducts. Heavy solubility. metals and radionuclides, It does not convert the are incorporated into the waste into a hardened, glass structure which is, monolithic mass. One generally, a relatively strong, application is in durable material that is stabilizing fly ash by resistant to leaching. immobilizing the lead and cadmium in the ash. 11
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