CN112592720A - Method for preparing composite curing agent by taking fly ash as raw material and application of composite curing agent in repairing mining area soil - Google Patents
Method for preparing composite curing agent by taking fly ash as raw material and application of composite curing agent in repairing mining area soil Download PDFInfo
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- 239000002689 soil Substances 0.000 title claims abstract description 85
- 238000005065 mining Methods 0.000 title claims abstract description 55
- 239000003795 chemical substances by application Substances 0.000 title claims abstract description 48
- 238000000034 method Methods 0.000 title claims abstract description 35
- 239000002131 composite material Substances 0.000 title claims abstract description 33
- 239000010881 fly ash Substances 0.000 title claims abstract description 27
- 239000002994 raw material Substances 0.000 title claims abstract description 20
- 229910021536 Zeolite Inorganic materials 0.000 claims abstract description 80
- 239000010457 zeolite Substances 0.000 claims abstract description 80
- 239000002808 molecular sieve Substances 0.000 claims abstract description 79
- URGAHOPLAPQHLN-UHFFFAOYSA-N sodium aluminosilicate Chemical compound [Na+].[Al+3].[O-][Si]([O-])=O.[O-][Si]([O-])=O URGAHOPLAPQHLN-UHFFFAOYSA-N 0.000 claims abstract description 79
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 claims abstract description 76
- 229910001385 heavy metal Inorganic materials 0.000 claims abstract description 61
- 230000000694 effects Effects 0.000 claims abstract description 20
- 150000001875 compounds Chemical class 0.000 claims abstract description 14
- 238000013329 compounding Methods 0.000 claims abstract description 8
- 238000001179 sorption measurement Methods 0.000 claims description 10
- 238000001027 hydrothermal synthesis Methods 0.000 claims description 9
- 239000002253 acid Substances 0.000 claims description 5
- 229910052793 cadmium Inorganic materials 0.000 claims description 4
- 229910052804 chromium Inorganic materials 0.000 claims description 4
- 229910052745 lead Inorganic materials 0.000 claims description 4
- 229910052759 nickel Inorganic materials 0.000 claims description 4
- 239000003513 alkali Substances 0.000 claims description 3
- 230000004927 fusion Effects 0.000 claims description 3
- 238000002156 mixing Methods 0.000 claims description 3
- 238000002715 modification method Methods 0.000 claims description 3
- 230000008569 process Effects 0.000 claims description 3
- 230000032683 aging Effects 0.000 claims description 2
- 238000005067 remediation Methods 0.000 description 9
- 239000000463 material Substances 0.000 description 6
- 239000003463 adsorbent Substances 0.000 description 3
- 238000005516 engineering process Methods 0.000 description 3
- 238000009825 accumulation Methods 0.000 description 2
- 230000009471 action Effects 0.000 description 2
- 230000008901 benefit Effects 0.000 description 2
- 230000007774 longterm Effects 0.000 description 2
- 239000000203 mixture Substances 0.000 description 2
- 230000004048 modification Effects 0.000 description 2
- 238000012986 modification Methods 0.000 description 2
- 230000008439 repair process Effects 0.000 description 2
- 238000007711 solidification Methods 0.000 description 2
- 230000008023 solidification Effects 0.000 description 2
- 241001465754 Metazoa Species 0.000 description 1
- 229910052782 aluminium Inorganic materials 0.000 description 1
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 231100000693 bioaccumulation Toxicity 0.000 description 1
- 230000004071 biological effect Effects 0.000 description 1
- 239000006227 byproduct Substances 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 230000018109 developmental process Effects 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 229910052500 inorganic mineral Inorganic materials 0.000 description 1
- 239000011707 mineral Substances 0.000 description 1
- 238000002161 passivation Methods 0.000 description 1
- 230000002085 persistent effect Effects 0.000 description 1
- 238000010248 power generation Methods 0.000 description 1
- 230000009467 reduction Effects 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 229910052710 silicon Inorganic materials 0.000 description 1
- 239000010703 silicon Substances 0.000 description 1
- 239000002893 slag Substances 0.000 description 1
- 230000006641 stabilisation Effects 0.000 description 1
- 238000011105 stabilization Methods 0.000 description 1
- 231100001234 toxic pollutant Toxicity 0.000 description 1
- 238000012546 transfer Methods 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
- 230000003313 weakening effect Effects 0.000 description 1
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- C09K17/08—Aluminium compounds, e.g. aluminium hydroxide
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09C—RECLAMATION OF CONTAMINATED SOIL
- B09C1/00—Reclamation of contaminated soil
- B09C1/08—Reclamation of contaminated soil chemically
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09C—RECLAMATION OF CONTAMINATED SOIL
- B09C2101/00—In situ
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Abstract
Description
技术领域technical field
本发明涉及土壤重金属污染修复技术领域,具体涉及一种以粉煤灰为原料制备复合型固化剂的方法,以及该复合型固化剂在修复矿区土壤中的应用。The invention relates to the technical field of soil heavy metal pollution remediation, in particular to a method for preparing a composite curing agent using fly ash as a raw material, and the application of the composite curing agent in soil restoration in mining areas.
背景技术Background technique
随着国家经济的发展,工业的高度发达,对矿产资源需求的增加,导致矿区周边土壤重金属污染严重。重金属是一种持久性潜在有毒污染物,人类活动对矿山的不断开采以及矿渣的随意堆放,使矿区周围土壤造成重金属污染。重金属进入土壤后难以被生物降解,长期累积会引起土壤生物活性降低,造成土壤生态系统功能减弱甚至丧失,使得土地承载力下降,影响地表动植物活性。而且土壤中重金属具有随食物链传递、生物富集和生物放大的特点,这是一个长期而缓慢的累积过程。因此,针对矿区土壤中重金属的修复这一问题,许多学者也做了大量的研究工作。由于固化/稳定化技术具有费用低、修复时间短、可处理多种复合重金属污染、易操作等优点,所以它成为一种较成熟且经济有效的重金属污染土壤的修复治理技术。With the development of the national economy and the highly developed industry, the demand for mineral resources has increased, resulting in serious heavy metal pollution in the soil around the mining area. Heavy metal is a persistent and potentially toxic pollutant. The continuous mining of mines by human activities and the random stacking of slag have caused heavy metal pollution to the soil around the mining area. Heavy metals are difficult to be biodegraded after entering the soil. Long-term accumulation will cause the reduction of soil biological activity, resulting in the weakening or even loss of soil ecosystem functions, which will reduce the carrying capacity of the land and affect the activities of surface animals and plants. Moreover, heavy metals in soil have the characteristics of transfer, bioaccumulation and biomagnification along the food chain, which is a long-term and slow accumulation process. Therefore, many scholars have also done a lot of research work on the restoration of heavy metals in mining soil. Due to the advantages of low cost, short remediation time, multi-composite heavy metal pollution, and easy operation, solidification/stabilization technology has become a relatively mature and cost-effective remediation technology for heavy metal-contaminated soils.
粉煤灰出现在火力发电厂排出的废弃物中,是燃煤发电的副产品之一,随着粉煤灰数量的日益增加,并且其堆置的场地会对人类生存的空间造成巨大威胁,将其合理的资源化应用是解决其污染的有效方法。粉煤灰含有大量的硅和铝物质,与沸石组成相似,利用粉煤灰为原料制备不同类型的沸石分子筛做固化剂,用来修复矿区污染土壤是一种兼具经济和环境双重效益的技术。然而目前研究得到的固化剂,普遍存在钝化稳定性不高,且作用效果单一,不能对不同区域待修复的土壤都达到较好的固化效果,使其利用率较低。Fly ash appears in the waste discharged from thermal power plants and is one of the by-products of coal-fired power generation. Its reasonable resource application is an effective way to solve its pollution. Fly ash contains a large amount of silicon and aluminum, which is similar in composition to zeolite. Using fly ash as raw material to prepare different types of zeolite molecular sieves as curing agents to remediate polluted soil in mining areas is a technology that has both economic and environmental benefits. . However, the currently studied curing agents generally have low passivation stability and single effect, which cannot achieve a good curing effect on the soil to be repaired in different areas, resulting in a low utilization rate.
发明内容SUMMARY OF THE INVENTION
本发明的目的是提供一种以粉煤灰为原料制备复合型固化剂的方法及其在修复矿区土壤中的应用,以解决矿区土壤中重金属所导致的生态问题,并同时实现粉煤灰无害化、资源化利用。The object of the present invention is to provide a method for preparing a composite curing agent with fly ash as a raw material and its application in repairing the soil in the mining area, so as to solve the ecological problem caused by heavy metals in the soil in the mining area, and at the same time realize that the fly ash is free of Harmful and resource utilization.
为实现上述目的,本发明采用的技术方案为:To achieve the above object, the technical scheme adopted in the present invention is:
一种以粉煤灰为原料制备用于修复矿区土壤中重金属的复合型固化剂的方法,包括以下步骤:A method for preparing a composite solidifying agent for repairing heavy metals in soil in a mining area by using fly ash as a raw material, comprising the following steps:
步骤1,以粉煤灰为原料制备不同类型的沸石分子筛;Step 1, using fly ash as raw material to prepare different types of zeolite molecular sieves;
步骤2,测定待修复矿区土壤中重金属的赋存状态;Step 2, determine the occurrence state of heavy metals in the soil of the mining area to be repaired;
步骤3,测定步骤1所制备的不同类型的沸石分子筛对待修复矿区土壤中重金属的修复效果;Step 3, measuring the remediation effect of the different types of zeolite molecular sieves prepared in step 1 to remediate heavy metals in the soil of the mining area;
步骤4,由步骤3所得修复效果,将不同类型的沸石分子筛复配,得到复合型固化剂。Step 4, according to the repairing effect obtained in step 3, compound different types of zeolite molecular sieves to obtain a composite curing agent.
所述步骤1中,制备沸石分子筛的方法为水热合成法、两步水热合成法、碱熔融水热法或酸改性法。In the step 1, the method for preparing the zeolite molecular sieve is a hydrothermal synthesis method, a two-step hydrothermal synthesis method, an alkali fusion hydrothermal method or an acid modification method.
所述步骤1中,不同类型的沸石分子筛包括:4A沸石分子筛、A1型沸石分子筛、A2型沸石分子筛、X1型沸石分子筛、X2型沸石分子筛、P型沸石分子筛。In the step 1 , different types of zeolite molecular sieves include: 4A zeolite molecular sieve, A1 type zeolite molecular sieve, A2 type zeolite molecular sieve, X1 type zeolite molecular sieve, X2 type zeolite molecular sieve, and P type zeolite molecular sieve.
所述步骤2中,测定待修复的矿区土壤中重金属含量以及所含重金属在土壤中存在的形态。In the step 2, the content of heavy metals in the soil of the mining area to be repaired and the forms of the contained heavy metals in the soil are determined.
所述步骤3中,将步骤1制备的不同类型的沸石分子筛分别单独作用于待修复矿区土壤,得到不同类型的沸石分子筛对土壤中的一种或几种重金属的修复效果。In the step 3, the different types of zeolite molecular sieves prepared in the step 1 are separately applied to the soil in the mining area to be repaired to obtain the repairing effect of the different types of zeolite molecular sieves on one or several heavy metals in the soil.
所述步骤4中,根据步骤3所测定到的数据,通过以下复配方法计算出修复矿区土壤所需的每种沸石分子筛的比例,按比例混合得到复合型固化剂;In the step 4, according to the data measured in the step 3, the proportion of each zeolite molecular sieve required for repairing the soil in the mining area is calculated by the following compounding method, and the composite curing agent is obtained by mixing in proportion;
所述复配方法为:The compounding method is:
待修复土壤中超标重金属:n1、n2、n3…ni,其对应有最佳吸附效果的沸石分子筛分别:N1、N2、N3…Ni,则 Excessive heavy metals in the soil to be repaired : n 1 , n 2 , n 3 .
其中,为吸附土壤中n1所需N1的最小投加量,g/kg;in, The minimum dosage of N 1 required to adsorb n 1 in the soil, g/kg;
为n1在土壤中的含量,mg/kg; is the content of n 1 in the soil, mg/kg;
为N1对n1的最大吸附量,mg/g; is the maximum adsorption amount of N 1 to n 1 , mg/g;
同理,得到 Similarly, get
若加入的复合固化剂的量为fN总和,固化剂的吸附容量会出现过剩,因此引入一个过量系数由过量系数计算出复合固化剂的配比:If the amount of the composite curing agent added is the sum of f N , the adsorption capacity of the curing agent will be excessive, so an excess coefficient is introduced. Calculate the ratio of the composite curing agent from the excess coefficient:
其中,为过量系数,量纲为1;同理,得 in, is the excess coefficient, and the dimension is 1; in the same way, we get
找到最小过量系数 Find the minimum excess factor
则不同沸石分子筛的投加量为:Then the dosage of different zeolite molecular sieves is:
本发明的复合型固化剂在修复矿区土壤中重金属的应用,具体为:将所述复合型固化剂均匀布施在待修复矿区土壤上,再进行翻耕,使其均匀混合,堆放陈化15-25d,完成修复过程。其中,所述复合型固化剂的用量为80-200kg/亩。所述重金属为Cd、Pb、Hg、Cu、Cr、Ni的一种或多种。The application of the composite curing agent of the present invention in repairing heavy metals in the soil of a mining area is specifically as follows: uniformly distributing the composite curing agent on the soil of the mining area to be repaired, and then ploughing to make it evenly mixed, stacking and aging for 15- 25d, the repair process is completed. Wherein, the dosage of the composite curing agent is 80-200kg/mu. The heavy metal is one or more of Cd, Pb, Hg, Cu, Cr, and Ni.
有益效果:本发明采用粉煤灰为主要原料,有针对性的改性处理制备具有不同性质的多种固化剂,基于土壤中重金属的赋存特征,通过多种固化剂复配用于土壤中重金属固化修复,该方法在解决矿区土壤中重金属所导致的生态问题的同时,实现了粉煤灰无害化、资源化利用,减少了粉煤灰填埋对土地的占用。Beneficial effects: The present invention uses fly ash as the main raw material, and carries out targeted modification treatment to prepare various curing agents with different properties. Based on the occurrence characteristics of heavy metals in the soil, various curing agents are compounded and used in the soil. Heavy metal solidification and restoration, the method not only solves the ecological problems caused by heavy metals in the soil of the mining area, but also realizes the harmless and resource utilization of fly ash, and reduces the land occupation of fly ash landfill.
具体实施方式Detailed ways
下面结合实施例对本发明作更进一步的说明。The present invention will be further described below in conjunction with the examples.
本发明的一种以粉煤灰为原料制备用于修复矿区土壤中重金属的复合型固化剂的方法,包括以下步骤:A method for preparing a composite solidifying agent for repairing heavy metals in soil in a mining area by using fly ash as a raw material of the present invention comprises the following steps:
步骤1,以粉煤灰为原料,以现有技术中的水热合成法、两步水热合成法、碱熔融水热法或酸改性法制备不同类型的沸石分子筛;其中,不同类型的沸石分子筛包括:4A沸石分子筛、A1型沸石分子筛、A2型沸石分子筛、X1型沸石分子筛、X2型沸石分子筛、P型沸石分子筛。Step 1, using fly ash as raw material, prepare different types of zeolite molecular sieves by hydrothermal synthesis method, two-step hydrothermal synthesis method, alkali fusion hydrothermal method or acid modification method in the prior art; Zeolite molecular sieves include : 4A zeolite molecular sieve, A1 type zeolite molecular sieve, A2 type zeolite molecular sieve, X1 type zeolite molecular sieve, X2 type zeolite molecular sieve, and P type zeolite molecular sieve.
步骤2,测定待修复矿区土壤中重金属含量以及所含重金属在土壤中存在的形态。Step 2, measuring the content of heavy metals in the soil of the mining area to be repaired and the forms of the contained heavy metals in the soil.
步骤3,将步骤1制备的不同类型的沸石分子筛分别单独作用于待修复矿区土壤,得到不同类型的沸石分子筛对土壤中的一种或几种重金属的修复效果。In step 3, the different types of zeolite molecular sieves prepared in step 1 are separately applied to the soil of the mining area to be repaired to obtain the repairing effects of different types of zeolite molecular sieves on one or several heavy metals in the soil.
步骤4,根据步骤3所测定到的数据,通过以下复配方法计算出修复矿区土壤所需的每种沸石分子筛的比例,按比例混合得到复合型固化剂;Step 4, according to the data measured in step 3, calculate the proportion of each zeolite molecular sieve required for repairing the soil in the mining area by the following compound method, and mix in proportion to obtain a composite curing agent;
其中,复配方法为:Among them, the compound method is:
待修复土壤中超标重金属:n1、n2、n3…ni,其对应有最佳吸附效果的沸石分子筛分别:N1、N2、N3…Ni,则 Excessive heavy metals in the soil to be repaired : n 1 , n 2 , n 3 .
其中,为吸附土壤中n1所需N1的最小投加量,g/kg;in, The minimum dosage of N 1 required to adsorb n 1 in the soil, g/kg;
为n1在土壤中的含量,mg/kg; is the content of n 1 in the soil, mg/kg;
为N1对n1的最大吸附量,mg/g; is the maximum adsorption amount of N 1 to n 1 , mg/g;
同理,得到 Similarly, get
若加入的复合固化剂的量为fN总和,固化剂的吸附容量会出现过剩,因此引入一个过量系数由过量系数计算出复合固化剂的配比:If the amount of the composite curing agent added is the sum of f N , the adsorption capacity of the curing agent will be excessive, so an excess coefficient is introduced. Calculate the ratio of the composite curing agent from the excess coefficient:
其中,为过量系数,量纲为1;同理,得 in, is the excess coefficient, and the dimension is 1; in the same way, we get
找到最小过量系数 Find the minimum excess factor
则不同沸石分子筛的投加量为:Then the dosage of different zeolite molecular sieves is:
下面结合实施例对本发明做进一步说明。The present invention will be further described below in conjunction with the embodiments.
实施例1Example 1
以粉煤灰为原料制备不同类型的沸石分子筛;测定待修复矿区土壤中重金属的赋存状态;测定不同类型吸附材料对矿区土壤中重金属的修复效果;由测定的数据,复配制备出复合型的固化剂。修复地为徐州某矿区土壤。Prepare different types of zeolite molecular sieves with fly ash as raw material; determine the occurrence state of heavy metals in the soil of the mining area to be rehabilitated; determine the remediation effect of different types of adsorption materials on the heavy metals in the soil of the mining area; from the measured data, compound and prepare a composite type of curing agent. The restoration site is the soil of a mining area in Xuzhou.
不同类型的沸石分子筛包括:4A沸石分子筛、A1型沸石分子筛、A2型沸石分子筛、X型沸石分子筛、P型沸石分子筛。Different types of zeolite molecular sieves include: 4A zeolite molecular sieve, A 1 type zeolite molecular sieve, A 2 type zeolite molecular sieve, X type zeolite molecular sieve, and P type zeolite molecular sieve.
测定出待修复的矿区土壤中的重金属含量见表1;The content of heavy metals in the soil of the mining area to be restored is determined in Table 1;
表1:待修复矿区土壤重金属含量Table 1: Content of heavy metals in the soil of the mining area to be rehabilitated
重金属元素Cd、Hg、Cu以及Pb,其元素以酸可提取态、可还原态和可氧化态存在的形态占其元素含量的59.4%-78.6%;Cr和Ni元素的残渣态含量占比相对较多。Heavy metal elements Cd, Hg, Cu and Pb, whose elements exist in acid extractable state, reducible state and oxidizable state account for 59.4%-78.6% of their element content; Cr and Ni elements account for relative residual state content more.
所述的测定不同类型沸石分子筛对矿区土壤中重金属的修复效果具体为:将制备的不同类型的沸石分子筛分别作用于待修复矿区土壤,得到不同的吸附材料对土壤中的一种或几种重金属的修复效果见表2。The described determination of the remediation effect of different types of zeolite molecular sieves on heavy metals in the soil of the mining area is specifically as follows: the prepared different types of zeolite molecular sieves are respectively applied to the soil of the mining area to be repaired to obtain the effect of different adsorption materials on one or several heavy metals in the soil. The repair effect is shown in Table 2.
表2:不同吸附材料作用待修复矿区土壤结果Table 2: The results of the soil in the mining area to be rehabilitated by the action of different adsorbent materials
由上述两个步骤得到的数据,通过本发明所提供的复配方法计算出所需单一沸石分子筛的比例,其中:4A沸石分子筛8%、A1型沸石分子筛23%、A2型沸石分子筛17%、X1型沸石分子筛8%、X2型沸石分子筛26%、P型沸石分子筛18%;按比例混合得到所需要的复合型固化剂。From the data obtained from the above two steps, the required proportion of single zeolite molecular sieve is calculated by the compounding method provided by the present invention, wherein: 4A zeolite molecular sieve 8%, A 1 type zeolite molecular sieve 23%, A 2 type zeolite molecular sieve 17% %, X 1 type zeolite molecular sieve 8%, X 2 type zeolite molecular sieve 26%, P type zeolite molecular sieve 18%; mixed in proportion to obtain the required composite curing agent.
将复合型固化剂按照120kg/亩的比例,均匀布施在污染土壤上,再进行翻耕,使其均匀混合,堆放陈化20d,完成修复过程。测定修复后土壤中重金属含量见表3。The composite curing agent was evenly distributed on the polluted soil in the proportion of 120kg/mu, and then ploughed to make it evenly mixed, stacked and aged for 20 days to complete the restoration process. The content of heavy metals in soil after restoration is shown in Table 3.
表3:复合型固化剂修复后矿区土壤重金属含量Table 3: Content of heavy metals in the soil of the mining area after the composite curing agent has been repaired
实施例2Example 2
以粉煤灰为原料制备不同类型的沸石分子筛;测定待修复矿区土壤中重金属的赋存状态;测定不同类型沸石分子筛对矿区土壤中重金属的修复效果;由测定的数据,复配制备出复合型的固化剂。修复地为徐州某矿区土壤。Prepare different types of zeolite molecular sieves with fly ash as raw material; determine the occurrence state of heavy metals in the soil of the mining area to be repaired; determine the remediation effect of different types of zeolite molecular sieves on the heavy metals in the soil of the mining area; from the measured data, compound and prepare a composite type of curing agent. The restoration site is the soil of a mining area in Xuzhou.
不同类型的沸石分子筛包括:4A沸石分子筛、A1型沸石分子筛、A2型沸石分子筛、X型沸石分子筛、P型沸石分子筛。Different types of zeolite molecular sieves include: 4A zeolite molecular sieve, A 1 type zeolite molecular sieve, A 2 type zeolite molecular sieve, X type zeolite molecular sieve, and P type zeolite molecular sieve.
测定出待修复的矿区土壤中的重金属含量见表4;The content of heavy metals in the soil of the mining area to be restored is determined in Table 4;
表4:待修复矿区土壤重金属含量Table 4: Content of heavy metals in the soil of the mining area to be rehabilitated
重金属元素Hg、Cu、Cd以及Cr,其元素以酸可提取态、可还原态和可氧化态存在的形态占其元素含量的56.3%-79.1%;Pb和Ni元素的残渣态含量占比相对较多。Heavy metal elements Hg, Cu, Cd and Cr, whose elements exist in acid extractable state, reducible state and oxidizable state account for 56.3%-79.1% of their element content; Pb and Ni elements account for relative residual state content more.
将制备的不同类型的沸石分子筛分别作用于待修复矿区土壤,得到不同的吸附材料对土壤中的一种或几种重金属的修复效果见表5。The prepared different types of zeolite molecular sieves were respectively applied to the soil of the mining area to be repaired, and the repairing effects of different adsorption materials on one or several heavy metals in the soil were obtained as shown in Table 5.
表5:不同吸附材料作用待修复矿区土壤结果Table 5: The results of the soil in the mining area to be rehabilitated by the action of different adsorbent materials
由上述两个步骤得到的数据,通过本发明所提供的复配方法计算出所需单一吸附材料的比例,其中:4A沸石分子筛18%、A1型沸石分子筛26%、A2型沸石分子筛10%、X1型沸石分子筛9%、X2型沸石分子筛24%、P型沸石分子筛13%;按比例混合得到所需要的复合型固化剂。From the data obtained from the above two steps, the ratio of the required single adsorbent material is calculated by the compounding method provided by the present invention, wherein: 18% of 4A zeolite molecular sieve, 26 % of A1 type zeolite molecular sieve, 10 % of A2 type zeolite molecular sieve %, X 1 type zeolite molecular sieve 9%, X 2 type zeolite molecular sieve 24%, P type zeolite molecular sieve 13%; mixed in proportion to obtain the required composite curing agent.
将复合型固化剂按照150kg/亩的比例,均匀布施在污染土壤上,再进行翻耕,使其均匀混合,堆放陈化18d,完成修复过程。测定修复后土壤中重金属含量见表6。The composite curing agent is evenly distributed on the polluted soil at the proportion of 150kg/mu, and then ploughed to make it evenly mixed, stacked and aged for 18 days to complete the restoration process. The content of heavy metals in soil after remediation was determined in Table 6.
表6:复合型固化剂修复后矿区土壤重金属含量Table 6: Contents of heavy metals in the soil of the mining area after remediation by the composite curing agent
以上所述的实施例,只是本发明的部分较优选方案,本领域的技术员应该了解,本发明不受上述实施例的限制,上述实施例和说明书中描述的只是说明本发明的原理,在不脱离本发明的实质和范围的前提下,本发明的技术方案可进行修改或者等同替换,这些修改和等同替换也应视为本发明的保护范围。The above-mentioned embodiments are only some preferred solutions of the present invention. Those skilled in the art should understand that the present invention is not limited by the above-mentioned embodiments. The above-mentioned embodiments and descriptions only illustrate the principles of the present invention. Without departing from the spirit and scope of the present invention, the technical solutions of the present invention may be modified or equivalently replaced, and these modifications and equivalent replacements should also be regarded as the protection scope of the present invention.
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