[go: up one dir, main page]

CN103060570B - A method for extracting valuable components from sludge - Google Patents

A method for extracting valuable components from sludge Download PDF

Info

Publication number
CN103060570B
CN103060570B CN201310014133.XA CN201310014133A CN103060570B CN 103060570 B CN103060570 B CN 103060570B CN 201310014133 A CN201310014133 A CN 201310014133A CN 103060570 B CN103060570 B CN 103060570B
Authority
CN
China
Prior art keywords
arsenic
antimony
sludge
copper
treatment
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Active
Application number
CN201310014133.XA
Other languages
Chinese (zh)
Other versions
CN103060570A (en
Inventor
祁先进
廖天鹏
王�华
祝星
胡建杭
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Middle Regions Of Yunnan Province Chuxiong Non-Ferrous Metal Co Ltd
YUNNAN COPPER INDUSTRY Co Ltd
Kunming University of Science and Technology
Original Assignee
Kunming University of Science and Technology
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Kunming University of Science and Technology filed Critical Kunming University of Science and Technology
Priority to CN201310014133.XA priority Critical patent/CN103060570B/en
Publication of CN103060570A publication Critical patent/CN103060570A/en
Application granted granted Critical
Publication of CN103060570B publication Critical patent/CN103060570B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P10/00Technologies related to metal processing
    • Y02P10/20Recycling

Landscapes

  • Manufacture And Refinement Of Metals (AREA)

Abstract

本发明公开了一种铜污泥有价成分的提取方法,该方法利用真空蒸馏技术、真空二次蒸馏、高温氧化焙烧、砷的提取和粗锑精炼,实现砷及砷氧化物及其它易挥发性金属的分离与提取,实现有价金属的回收以及降低污泥中有害成分含量的目的,该工艺简单、设备投入少,砷和锑不经氧化还原直接提取回收,达到了降低了污泥中的有害元素含量的目的,进而降低污泥的浸出毒性或固化成本。

Figure 201310014133

The invention discloses a method for extracting valuable components from copper sludge. The method utilizes vacuum distillation technology, vacuum secondary distillation, high-temperature oxidation roasting, arsenic extraction and crude antimony refining to realize arsenic, arsenic oxides and other volatile components. Separation and extraction of non-toxic metals to achieve the recovery of valuable metals and the purpose of reducing the content of harmful components in the sludge. The process is simple and the investment in equipment is small. The purpose of reducing the content of harmful elements, thereby reducing the leaching toxicity or solidification cost of sludge.

Figure 201310014133

Description

一种污泥有价成分的提取方法A method for extracting valuable components from sludge

技术领域 technical field

  本发明涉及一种冶金危险固体废弃物综合利用技术,是一种铜污泥有价成分提取技术,属于资源综合利用与危险废弃物无害化处置领域。 The invention relates to a comprehensive utilization technology of metallurgical hazardous solid waste, which is a technology for extracting valuable components from copper sludge, and belongs to the field of comprehensive utilization of resources and harmless disposal of hazardous waste.

技术背景 technical background

铜火法冶炼过程中产生大量酸性废水,这类废水的处理目前通常采用石灰中和沉淀处理,使重金属以氢氧化物的形式沉淀析出,产生大量含Cu、Sn、Zn、As的混合污泥。这些污泥其主要成分为石膏,但富含砷及其他重金属,若任其随意堆放,会对环境造成严重的危害。由于污泥成分复杂且含有多种有毒有害物质,长期堆放不仅侵占土地,而且会严重地污染地下水、土壤和农田,影响人体健康和生态环境。该污泥含有多种有毒有害物质,必须经无害化处置,以达到防治污染目的。 A large amount of acidic wastewater is produced in the process of copper pyrometallurgy. The treatment of this type of wastewater is usually carried out by lime neutralization and precipitation, so that heavy metals are precipitated in the form of hydroxides, and a large amount of mixed sludge containing Cu, Sn, Zn, and As is produced. . The main component of these sludges is gypsum, but it is rich in arsenic and other heavy metals. If it is allowed to pile up randomly, it will cause serious harm to the environment. Due to the complex composition of sludge and various toxic and harmful substances, long-term stacking will not only encroach on land, but also seriously pollute groundwater, soil and farmland, affecting human health and the ecological environment. The sludge contains a variety of toxic and harmful substances, which must be disposed of harmlessly to achieve the purpose of pollution prevention and control.

由于此类铜污泥中含有大量的有价成分,如As、Zn、Cu、Ag、Sb、Se等,如果能有效的回收其中有价成分,不仅避免了资源浪费,更重要的是可以降低污泥中有害成分的含量,减少对环境的污染。 Since this type of copper sludge contains a large amount of valuable components, such as As, Zn, Cu, Ag, Sb, Se, etc., if the valuable components can be effectively recovered, not only the waste of resources can be avoided, but more importantly, the waste of resources can be reduced. The content of harmful components in the sludge can reduce the pollution to the environment.

与传统的湿法浸出相比,不需要进行多次的固液分离,减少了污泥的处理过程。与传统的直接高温焙烧相比,提高了砷及其它易挥发元素的收得率,节约成本。与传统的污泥直接固化技术相比,提高了污泥利用率回收了有价金属,节约成本,降低了污泥固化成本和减少污泥对环境的危害。 Compared with traditional wet leaching, it does not need multiple solid-liquid separations, which reduces the sludge treatment process. Compared with the traditional direct high-temperature roasting, the yield of arsenic and other volatile elements is improved, and the cost is saved. Compared with the traditional sludge solidification technology, it improves the utilization rate of sludge, recovers valuable metals, saves costs, reduces the cost of sludge solidification and reduces the harm of sludge to the environment.

鉴于以上原因,本发明提出一种回收铜污泥中砷及易挥发的有价金属,实现污泥综合利用新方法。 In view of the above reasons, the present invention proposes a new method for recovering arsenic and volatile valuable metals in copper sludge to realize comprehensive utilization of sludge.

发明内容 Contents of the invention

本方法提出一种铜污泥有价成分的提取方法,以铜火法冶炼产生的污泥为主要原料,利用真空技术实现砷及砷氧化物及其他易挥发性金属的分离与提取,达到降低铜污泥中有害成分含量的目的,进而降低铜污泥的浸出毒性或固化成本。 This method proposes a method for extracting valuable components of copper sludge, using sludge produced by copper pyrometallurgy as the main raw material, and using vacuum technology to achieve the separation and extraction of arsenic, arsenic oxides and other volatile metals to reduce The purpose of reducing the content of harmful components in copper sludge, thereby reducing the leaching toxicity or solidification cost of copper sludge.

该发明包括以下几个步骤: The invention comprises the following steps:

(1)对污泥进行脱水预处理,在100℃~150℃下烘干处理12小时,脱除其中水分,预处理后将样品进行研磨处理,控制物料粒度为0.45~1.0mm左右; (1) Dehydration pretreatment is carried out on the sludge, which is dried at 100°C~150°C for 12 hours to remove the water in it. After pretreatment, the sample is ground to control the particle size of the material to be about 0.45~1.0mm;

(2)将预处理过样品与一定量的还原剂(煤粉、焦炭等)进行充分混合,其中还原剂的添加量控制在5~10%的范围内;充分混合后的物料放入真空炉内,同时将炉子抽真空;控制真空炉残压6.67~26.7Pa范围内,温度控制在(800~1200℃)范围内,进行真空高温处理20 ~60min时间; (2) Fully mix the pretreated sample with a certain amount of reducing agent (coal powder, coke, etc.), and the amount of reducing agent added is controlled within the range of 5-10%; the fully mixed material is placed in a vacuum furnace evacuate the furnace at the same time; control the residual pressure of the vacuum furnace within the range of 6.67~26.7Pa, control the temperature within the range of (800~1200°C), and perform vacuum high temperature treatment for 20~60min;

(3)随着真空炉温度与真空度的升高,通过还原或分解反应污泥中的As、Sb等易挥发性成分挥发出来,并且以冷凝的方式进行收集得到一次精馏产物,一次精馏产物中主要是砷、锑的混合物,含有少量的Pb、Zn等少量易挥发的杂质及焙烧产生的灰尘,将含有砷、锑的一次精馏产物重新放入真空炉中进行二次精馏可进一步提高其中有价成分含量,蒸馏温度为400-800℃,真空炉残压5.33~66.7Pa下蒸馏30-50min,冷凝收集挥发性得到含砷、锑的合金,合金的收得率在95%以上;   (3) As the temperature and vacuum degree of the vacuum furnace increase, the volatile components such as As and Sb in the reaction sludge are volatilized by reduction or decomposition, and are collected in the form of condensation to obtain a rectification product. The distillation product is mainly a mixture of arsenic and antimony, containing a small amount of volatile impurities such as Pb and Zn, and dust generated by roasting. Put the primary distillation product containing arsenic and antimony back into the vacuum furnace for secondary distillation It can further increase the content of valuable components. The distillation temperature is 400-800°C, and the residual pressure of the vacuum furnace is 5.33-66.7Pa. %above;

(4)将上述收集As、Sb合金采用常规锑精炼方法进行砷和锑的回收,在砷、锑合金精炼时砷优先蒸发,精炼是在500~700℃时,残压40Pa下处理30~60min,分别回收得到砷和锑,其中在合金精炼中加入还原剂,还原剂的添加量为物料质量的5~10%; (4) Use the conventional antimony refining method to recover arsenic and antimony from the above-mentioned collected As and Sb alloys. During the refining of arsenic and antimony alloys, arsenic is preferentially evaporated. The refining process is carried out at 500-700 °C and a residual pressure of 40 Pa for 30-60 minutes. , recover arsenic and antimony respectively, wherein a reducing agent is added in alloy refining, and the amount of reducing agent added is 5-10% of the mass of the material;

(5)将第一次蒸馏产生的残留物料与第二次蒸馏的残留物料放在一起,放入焙烧炉,通入O2进行氧化焙烧,焙烧温度在500~850℃,焙烧时间60~120min,收集As2O3气体,防止污染环境,将焙烧后的物料进行固化处理。 (5) Put the residual material from the first distillation together with the residual material from the second distillation, put it into the roaster, and pass O2 into it for oxidation roasting, the roasting temperature is 500~850°C, and the roasting time is 60~120min , collect As 2 O 3 gas to prevent environmental pollution, and solidify the roasted material.

本发明中还原剂为煤粉、焦炭。 The reducing agent in the present invention is coal powder and coke.

本发明中处理的污泥为铜火法冶炼过程中用烟气制酸后产生的废水,废水经废水处理站后产生的含高砷及其它重金属污泥,一般统称为铜污泥。 The sludge treated in the present invention is the waste water produced by using flue gas to make acid during the copper pyrometallurgy process, and the sludge containing high arsenic and other heavy metals produced after the waste water passes through the waste water treatment station is generally referred to as copper sludge.

本发明中固化处理是采用常规方法,利用物理-化学方法将焙烧后的污泥掺合并包容在密实的惰性基材中,使其稳定化的一种过程;或者是将焙烧后的污泥用惰性材料加以包容的过程。处理后的污泥中含有大量的重金属元素,为了防止重金属元素对环境产生二次污染,必须对污泥进行固化处理。 The solidification treatment in the present invention is a process of using conventional methods to blend the roasted sludge into a dense inert base material by using physical-chemical methods to stabilize it; or to use the roasted sludge The process by which an inert material is contained. The treated sludge contains a large amount of heavy metal elements. In order to prevent the heavy metal elements from causing secondary pollution to the environment, the sludge must be solidified.

本发明的优点: Advantages of the present invention:

与传统的对污泥直接固化处理相比,可以有效的回收As、Sb等有价元素,提高了资源的利用率,防止砷等有害元素进入大气环境,给周边环境带来污染。 Compared with the traditional direct solidification treatment of sludge, it can effectively recover valuable elements such as As and Sb, improve the utilization rate of resources, and prevent harmful elements such as arsenic from entering the atmosphere and polluting the surrounding environment.

本发明与以往的直接焙烧污泥脱砷相比,通过一次蒸馏和二次蒸馏更好的保证了对砷、锑的回收效果,而且可以不用额外的再加入熟石灰来防止煅烧过的污泥中的砷的浸出。 Compared with the previous method of directly roasting sludge for arsenic removal, the present invention can better ensure the recovery effect of arsenic and antimony through primary distillation and secondary distillation, and can prevent additional slaked lime from being added to calcined sludge. leaching of arsenic.

本发明与湿法浸出相比,不需要进行多次的固液分离,减少操作的环节,节约成本。 Compared with wet leaching, the present invention does not need to perform multiple solid-liquid separations, reduces operation links and saves costs.

本发明由于采用上述工艺方法,工艺简单,投入设备少,成本低,提取过程不产生污染,为处理污泥的一种新工艺。 Due to the adoption of the above process method, the present invention has simple process, less equipment input, low cost, no pollution in the extraction process, and is a new process for treating sludge.

通过本发明方法可以将有价成分中砷锑的回收率提高到98%以上、锑的回收率提高到95%以上。 Through the method of the invention, the recovery rate of arsenic and antimony in the valuable components can be increased to over 98%, and the recovery rate of antimony can be increased to over 95%.

附图说明 Description of drawings

图1是本发明工艺流程示意图。 Fig. 1 is a schematic diagram of the process flow of the present invention.

具体实施方式 Detailed ways

实施例1:本污泥有价成分的提取方法,具体内容如下: Embodiment 1: the extraction method of this sludge valuable component, specific content is as follows:

本实施例使用的是炼铜厂废水处理后产生的污泥,其组分见表1: What this embodiment used was the sludge produced after the copper smelter wastewater treatment, and its components are shown in Table 1:

表1 :某炼铜厂废水处理后的污泥成分 Table 1: Sludge composition after wastewater treatment in a copper smelter

元素element AsAs SbSb Zn Zn C C O o Ca Ca PbPb 含量%content%  1616  6.56.5  44 5.55.5 24twenty four 42 42 22

1、对20g污泥进行脱水预处理,在100℃下烘干处理15小时,干燥后样品进行研磨,研磨后物料粒度为1.0mm; 1. Perform dehydration pretreatment on 20g of sludge, dry it at 100°C for 15 hours, grind the sample after drying, and the particle size of the material after grinding is 1.0mm;

2、将预处理后物料与还原剂煤粉混合,加入物料质量5%的煤粉,混匀后物料放入真空炉中,真空炉残压为6.67Pa,在800℃下进行真空高温精馏处理60min,然后将反应污泥中挥发出来的易挥发性成分以冷凝的方式进行收集,得到一次精馏产物含As、Sb的混合物6g; 2. Mix the pretreated material with the reducing agent pulverized coal, add 5% coal pulverized by the mass of the material, put the material into a vacuum furnace after mixing, the residual pressure of the vacuum furnace is 6.67Pa, and carry out vacuum high-temperature rectification at 800°C Treat for 60 minutes, then collect the volatile components volatilized in the reaction sludge in a condensed manner, and obtain 6 g of a mixture containing As and Sb in the primary distillation product;

3、将含有As、Sb的一次精馏产物再放入真空炉中进行真空重蒸馏,蒸馏温度400℃,真空炉残压40Pa下蒸馏40min,冷凝收集挥发性成分,得到含As、Sb的合金4.46g; 3. Put the primary distillation product containing As and Sb into a vacuum furnace for vacuum redistillation, the distillation temperature is 400°C, and the residual pressure of the vacuum furnace is 40Pa for 40 minutes, and the volatile components are collected by condensation to obtain an alloy containing As and Sb 4.46g;

4、将上述冷凝收集As、Sb的合金进行锑精炼回收砷、锑,在砷、锑合金蒸馏时砷优先蒸发,锑精炼是在500℃时,残压40Pa下蒸发30min,分别回收得到砷3.15g,锑1.24g;砷的回收率为98.4%,锑的回收率是95.4%; 4. Perform antimony refining on the alloys of As and Sb collected by condensation above to recover arsenic and antimony. Arsenic evaporates preferentially during the distillation of arsenic and antimony alloys. The antimony refining process evaporates at 500°C for 30 minutes under a residual pressure of 40 Pa, and respectively recovers arsenic 3.15 g, antimony 1.24g; the recovery rate of arsenic is 98.4%, and the recovery rate of antimony is 95.4%;

5、将第一次精馏产生的残留物料与第二次精馏的残留物料收集在一起,放入焙烧炉,通入O2进行氧化焙烧,焙烧温度为500℃,焙烧时间120min,通过改变物料的结构,使其疏松多孔,同时使残留的砷以挥发性氧化物As2O3形式从污泥中挥发,收集As2O3气体,进而降低污泥的浸出毒性或固化成本,将焙烧后的物料采用常规方法进行固化处理(见图1)。 5. Collect the residual material produced by the first rectification and the residual material of the second rectification together, put it into the roaster, pass O2 to carry out oxidation roasting, the roasting temperature is 500 ° C, the roasting time is 120min, by changing The structure of the material makes it loose and porous, and at the same time, the residual arsenic is volatilized from the sludge in the form of volatile oxide As 2 O 3 , and As 2 O 3 gas is collected, thereby reducing the leaching toxicity or solidification cost of the sludge, and roasting The final material is cured by conventional methods (see Figure 1).

实施例2:本污泥有价成分的提取方法,具体内容如下: Embodiment 2: the extraction method of this sludge valuable component, specific content is as follows:

本实施例中使用的是某炼铜厂废水处理后的污泥,其成分如下表: What used in the present embodiment is the sludge after the wastewater treatment of a certain copper smelter, and its composition is as follows:

表2:某炼铜厂废水处理后的污泥成分 Table 2: Sludge composition after wastewater treatment in a copper smelter

元素element AsAs SbSb Zn Zn C C O o Ca Ca PbPb 含量%content%  18.518.5  7.57.5  3.53.5 66 22.522.5 40 40 22

1、对20g污泥进行脱水预处理,在120℃下烘干处理12小时,干燥后样品进行研磨,研磨后物料粒度为0.8mm; 1. Perform dehydration pretreatment on 20g of sludge, dry it at 120°C for 12 hours, grind the sample after drying, and the particle size of the material after grinding is 0.8mm;

2、将预处理后物料与还原剂煤粉混合,加入物料质量10%的煤粉,混匀后物料放入真空炉中,真空炉残压为26.7Pa,在1000℃下进行真空高温精馏处理40min,然后将反应污泥中挥发出来的易挥发性成分以冷凝的方式进行收集,得到一次精馏产物含As、Sb的混合物6.5g; 2. Mix the pretreated material with the reducing agent coal powder, add coal powder with 10% of the material mass, and put the material into a vacuum furnace after mixing. After 40 minutes of treatment, the volatile components volatilized in the reaction sludge were collected in a condensed manner to obtain 6.5 g of a mixture containing As and Sb in the primary distillation product;

3、将含有As、Sb的一次精馏产物再放入真空炉中进行真空重蒸馏,蒸馏温度800℃,真空炉残压66.7Pa下蒸馏30min,最终得到含As、Sb的冷凝物5.14g; 3. Put the primary distillation product containing As and Sb into a vacuum furnace for vacuum redistillation, the distillation temperature is 800°C, and the residual pressure of the vacuum furnace is 66.7Pa for 30 minutes to obtain 5.14g of condensate containing As and Sb;

4、将上述冷凝收集As、Sb的合金进行锑精炼回收砷、锑,在砷、锑,合金蒸馏时砷优先蒸发,锑精炼是在700℃时,残压40Pa下蒸发60min,分别回收得到砷3.66g,锑1.46g;砷的回收率为98.9%,锑的回收率是97.3%; 4. The above-mentioned condensed collected As and Sb alloys are subjected to antimony refining to recover arsenic and antimony. During the distillation of arsenic, antimony and alloys, arsenic is preferentially evaporated. Antimony refining is performed at 700°C and evaporated at a residual pressure of 40 Pa for 60 minutes, and arsenic is recovered separately. 3.66g, antimony 1.46g; the recovery rate of arsenic is 98.9%, and the recovery rate of antimony is 97.3%;

5、将第一次精馏产生的残留物料与第二次精馏的残留物料收集在一起,放入焙烧炉,通入O2进行氧化焙烧,焙烧温度为850℃,焙烧时间60min,同时收集As2O3气体,将焙烧后的物料采用常规方法进行固化处理。 5. Collect the residual material produced by the first rectification and the residual material of the second rectification together, put it into the roaster, and pass O2 to carry out oxidation roasting. The roasting temperature is 850 ° C, and the roasting time is 60 minutes. As 2 O 3 gas, the calcined material is solidified by conventional methods.

实施例3:本污泥有价成分的提取方法,具体内容如下: Embodiment 3: the extraction method of this sludge valuable component, specific content is as follows:

本实施例中使用的是某炼铜厂废水处理后的污泥,其成分如下表: What used in the present embodiment is the sludge after the wastewater treatment of a certain copper smelter, and its composition is as follows:

表3:某炼铜厂废水处理后的污泥成分 Table 3: Sludge composition after wastewater treatment in a copper smelter

元素element AsAs SbSb Zn Zn C C O o Ca Ca PbPb 含量%content%  1717  6.56.5  3.53.5 88 21 twenty one 41 41 33

1、对20g污泥进行脱水预处理,在120℃下烘干处理12小时,干燥后样品进行研磨,研磨后物料粒度为0.45mm;  1. Perform dehydration pretreatment on 20g of sludge, dry it at 120°C for 12 hours, grind the sample after drying, and the particle size of the material after grinding is 0.45mm;

2、将预处理后物料与还原剂煤粉混合,加入物料质量18%的焦炭,混匀后物料放入真空炉中,真空炉残压为7Pa,在1200℃下进行真空高温精馏处理20min,然后将反应污泥中挥发出来的易挥发性成分以冷凝的方式进行收集,得到一次精馏产物含As、Sb的混合物5.8g; 2. Mix the pretreated material with the reducing agent coal powder, add coke with a mass of 18% of the material, put the material into a vacuum furnace after mixing, the residual pressure of the vacuum furnace is 7Pa, and carry out vacuum high-temperature rectification treatment at 1200 ° C for 20 minutes , and then the volatile components volatilized in the reaction sludge are collected in a condensed manner to obtain 5.8 g of a mixture containing As and Sb in the primary distillation product;

3、将含有As、Sb的一次精馏产物再放入真空炉中进行真空重蒸馏,蒸馏温度650℃,真空炉残压6Pa下蒸馏50min,最终得到含As、Sb的冷凝物4.67g; 3. Put the primary distillation product containing As and Sb into a vacuum furnace for vacuum redistillation, the distillation temperature is 650°C, and the residual pressure of the vacuum furnace is 6Pa for 50 minutes to obtain 4.67g of condensate containing As and Sb;

4、将上述冷凝收集As、Sb合金进行锑精炼回收砷、锑,在砷、锑合金蒸馏时砷优先蒸发,锑精炼是在500℃时,残压40Pa下蒸发40min,分别回收得到砷3.38g,锑1.26g;砷的回收率为99.4%,锑的回收率是96.9%; 4. Collect As and Sb alloys from the above-mentioned condensation for antimony refining to recover arsenic and antimony. Arsenic evaporates preferentially during the distillation of arsenic and antimony alloys. The antimony refining process evaporates for 40 minutes under a residual pressure of 40 Pa at 500°C, and recovers 3.38 g of arsenic respectively. , antimony 1.26g; the recovery rate of arsenic is 99.4%, and the recovery rate of antimony is 96.9%;

5、将第一次精馏产生的残留物料与第二次精馏的残留物料收集在一起,放入焙烧炉,通入O2进行氧化焙烧,焙烧温度为600℃,焙烧时间100min,同时收集As2O3气体,将焙烧后的物料采用常规方法进行固化处理。 5. Collect the residual material produced by the first rectification and the residual material of the second rectification together, put it into the roaster, pass O2 to carry out oxidation roasting, the roasting temperature is 600°C, the roasting time is 100min, and collect at the same time As 2 O 3 gas, the calcined material is solidified by conventional methods.

Claims (2)

1. an extracting method for copper mud valuable constituent, is characterized in that carrying out as follows:
(1) pre-treatment of mud: to the pre-treatment of dewatering of copper mud, drying and processing is 12 hours at 100 ~ 150 ℃, dry after sample grind, after grinding, raw meal particle size is 0.45 ~ 1.0mm;
(2) material after pre-treatment is mixed with reductive agent, mix rear material and put into vacuum oven, vacuum oven residual voltage is 6.67 ~ 26.7Pa, at 800 ~ 1200 ℃, carry out vacuum high-temperature rectification process 20 ~ 60min, then the easy volatile composition evaporating in reaction mud is collected in the mode of condensation, obtain rectifying product one time, to contain arsenic, a rectifying product of antimony is put into vacuum oven again and is carried out vacuum vapor enrichment, distillation temperature is 400 ~ 800 ℃, under vacuum oven residual voltage 5.33 ~ 66.7Pa, distill 30 ~ 50min, fugitive constituent is collected in condensation, obtain containing arsenic, the alloy of antimony, wherein the addition of reductive agent be after pre-treatment quality of material 5 ~ 10%,
(3) arsenic of collection, antimony alloy are adopted conventional antimony method of refining carry out the recovery of arsenic and antimony, antimony refining is to process 30 ~ 60min under 500 ~ 700 ℃, residual voltage 40Pa, obtain respectively arsenic and antimony, wherein in refining and modifying, add reductive agent, the addition of reductive agent is for containing 5 ~ 10% of arsenic, antimony alloy quality of material;
(4) residual material rectifying for the first time being produced is collected together with the residual material of rectifying for the second time, puts into stoving oven, passes into O 2carry out oxidizing roasting, maturing temperature is 500 ~ 850 ℃, and roasting time 60 ~ 120min collects As simultaneously 2o 3gas, is cured processing by the material after roasting;
Wherein said copper mud be in copper pyrometallurgy process with the waste water producing after flue gas acid preparing, waste water after waste water processing station, produce containing high arsenic and other heavy metal sewage sludge.
2. the extracting method of copper mud valuable constituent according to claim 1, is characterized in that: reductive agent is coal dust, coke.
CN201310014133.XA 2013-01-15 2013-01-15 A method for extracting valuable components from sludge Active CN103060570B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201310014133.XA CN103060570B (en) 2013-01-15 2013-01-15 A method for extracting valuable components from sludge

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201310014133.XA CN103060570B (en) 2013-01-15 2013-01-15 A method for extracting valuable components from sludge

Publications (2)

Publication Number Publication Date
CN103060570A CN103060570A (en) 2013-04-24
CN103060570B true CN103060570B (en) 2014-04-02

Family

ID=48103459

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201310014133.XA Active CN103060570B (en) 2013-01-15 2013-01-15 A method for extracting valuable components from sludge

Country Status (1)

Country Link
CN (1) CN103060570B (en)

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105060675B (en) * 2015-08-17 2017-07-25 昆明理工大学 A kind of river and lake sediment resource utilization method
CN106381396B (en) * 2016-09-13 2018-08-10 昆明理工大学 A kind of method that solid oxidizer roasting high-arsenic antimony flue dust detaches arsenic, antimony and recycling wherein antimony
CN107217145A (en) * 2016-12-09 2017-09-29 郴州万墨环保科技有限公司 A kind of method that copper anode mud vacuum reduction takes off lead antimony bismuth selen-tellurjum arsenic
CN109136576B (en) * 2018-09-19 2021-08-24 昆明理工大学 A method for removing arsenic from arsenic-containing smoke and dust

Family Cites Families (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CA867672A (en) * 1968-05-02 1971-04-06 The International Nickel Company Of Canada Fire refining of copper
SE407424B (en) * 1977-08-19 1979-03-26 Boliden Ab PROCEDURE FOR THE MANUFACTURE OF BLISTER COPPERS FROM ANTIMONOUS COPPER MATERIAL
CN100404708C (en) * 2006-12-06 2008-07-23 山东国大黄金股份有限公司 Production process of recovering Au Ag Cu As S from arsenic-containing carbon-gold concentrate by two-stage roasting method
CN101792857B (en) * 2010-04-13 2012-11-21 李柏荣 Process for refining metals from minerals
CN101935767B (en) * 2010-09-26 2012-04-11 山西龙港高纯材料有限公司 Preparation method of high-purity arsenic
CN102286665B (en) * 2011-09-05 2012-10-31 耒阳市焱鑫有色金属有限公司 Comprehensive recovery method for complicated materials containing arsenic and valuable metal slag dust

Also Published As

Publication number Publication date
CN103060570A (en) 2013-04-24

Similar Documents

Publication Publication Date Title
CN103464101B (en) A kind of method of repairing the plant giantreed recycling of heavy-metal contaminated soil
CN103602834B (en) Selective oxidation-reduction method for recycling arsenic and antimony from arsenic-antimony smoke
CN103789551B (en) Prepare manganese sulfate electrolyte with electrolytic manganese anode mud and reclaim plumbous method
CN103789556A (en) Method for recovering zinc in waste residue containing zinc ferrite through ferric sulfate roasting-water leaching
CN111515224B (en) Garbage fly ash treatment method
CN111996383B (en) Method for separating arsenic from copper slag by matching high-arsenic materials
CN103060570B (en) A method for extracting valuable components from sludge
CN101942567A (en) Method for removing arsenic and antimonic from anode sludge containing polyvalence composite type arsenic-antimonic compound
CN106381396B (en) A kind of method that solid oxidizer roasting high-arsenic antimony flue dust detaches arsenic, antimony and recycling wherein antimony
CN107557570A (en) Method for comprehensively recovering valuable metals from cyanidation tailings
CN103060547B (en) Method for restoring, roasting, purifying, and extracting manganese and iron by utilizing electrolytic manganese slag rotary kiln
CN111235397A (en) Process for efficiently treating copper smelting smoke dust
CN106498190B (en) The method of neodymium iron boron greasy filth waste material in-situ carbon thermocatalytic chlorination recovering rare earth product
CN103820587B (en) A kind of method containing dearsenization of volatilizing in arsenic richness scum
CN105130156A (en) Method for controlling sludge heavy metal to be discharged
CN110075697B (en) A method for flue gas desulfurization and resource utilization based on electrolytic manganese tailings slag
CN106380048A (en) Harmless arsenic treatment technology
CN106756000B (en) A method of clean and effective extracts vanadic anhydride from bone coal navajoite
CN118531222A (en) A process for recovering gold by two-stage roasting of arsenic-containing gold concentrate
CN209968029U (en) Waste gas treatment system for recycling metal surface treatment waste
CN108588424B (en) A method for separating manganese and lead in electrolytic manganese anode slag
CN102268538A (en) Boiling furnace device used for roasting nickel-molybdenum concentrate and method for roasting nickel-molybdenum concentrate
CN107326178B (en) A method for recovery and utilization of tail gas in the reduction leaching process of zinc hydrometallurgy slag
CN113528734A (en) Method for recovering iron ore concentrate by roasting and reducing iron-containing waste
CN106219921A (en) The processing means of heavy metal arsenic in water sludge

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
C41 Transfer of patent application or patent right or utility model
CB03 Change of inventor or designer information

Inventor after: Shi Yifeng

Inventor after: Zhou Shang

Inventor after: Zhao Liming

Inventor after: Qi Xianjin

Inventor after: Dai Hongkun

Inventor after: Liao Tianpeng

Inventor after: Shu Bo

Inventor after: Wang Hua

Inventor after: Hui Xinghuan

Inventor after: Zhu Xing

Inventor after: Hu Jianhang

Inventor before: Qi Xianjin

Inventor before: Liao Tianpeng

Inventor before: Wang Hua

Inventor before: Zhu Xing

Inventor before: Hu Jianhang

COR Change of bibliographic data
TR01 Transfer of patent right

Effective date of registration: 20160204

Address after: 650102 Wang Jia Qiao, Wuhua District, Yunnan, Kunming

Patentee after: Yunnan Copper Industry Co., Ltd.

Patentee after: Kunming University of Science and Technology

Patentee after: The middle regions of the Yunnan Province, Chuxiong non-ferrous metal Co., Ltd

Address before: 650093 Kunming, Yunnan, Wuhua District Road, No. 253

Patentee before: Kunming University of Science and Technology