CN104909507A - Contaminated acid concentrating and recycling method - Google Patents

Contaminated acid concentrating and recycling method Download PDF

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CN104909507A
CN104909507A CN201510294711.9A CN201510294711A CN104909507A CN 104909507 A CN104909507 A CN 104909507A CN 201510294711 A CN201510294711 A CN 201510294711A CN 104909507 A CN104909507 A CN 104909507A
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acid
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filtrate
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王胜利
王东亮
侯明旺
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Henan Feiditai Environmental Science And Technology Co ltd
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He'nan Shuangyu New Material Technology Co Ltd
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Abstract

本发明公开了一种污酸浓缩回收利用的方法,其步骤为:将用量比为1L:(10~30)g的污酸溶液与硫化剂溶液加入负压反应釜中,60~70℃条件下反应25~40min,反应后的物料由压滤机压滤,滤液进入下一步处理;将用量比为1L:(20~48)g的滤液与硫化剂溶液加入下一个负压反应釜中,室温下反应80~100min,再由浓密机沉淀,压滤机压滤,得到的污酸滤液通过动力波洗涤塔处理去除大量的F-、Cl-离子,得到浓度为50~60%的工业品硫酸。本发明将两级硫化与蒸发浓缩相结合对污酸进行处理,两级硫化通过时间与温度的控制有效去除了重金属及砷,实现了硫、金属元素的综合回收利用,成本低,经济效益高。The invention discloses a method for concentrating and recycling polluted acid. The steps are as follows: adding polluted acid solution and vulcanizing agent solution with a dosage ratio of 1L: (10-30) g into a negative pressure reaction kettle, and the condition is 60-70°C. The reaction was carried out for 25~40min, and the reacted material was filtered by the filter press, and the filtrate was processed in the next step; the filtrate and vulcanizing agent solution with a dosage ratio of 1L: (20~48)g were added to the next negative pressure reaction kettle, React at room temperature for 80-100 minutes, then precipitate with a thickener and filter with a filter press. The obtained dirty acid filtrate is treated with a power wave scrubber to remove a large amount of F - and Cl - ions, and an industrial product with a concentration of 50-60% is obtained. sulfuric acid. The present invention combines two-stage vulcanization with evaporation and concentration to treat polluted acid. The two-stage vulcanization effectively removes heavy metals and arsenic through the control of time and temperature, and realizes the comprehensive recovery and utilization of sulfur and metal elements, with low cost and high economic benefits. .

Description

一种污酸浓缩回收利用的方法A method for concentrating and reusing polluted acid

技术领域 technical field

本发明属于金属冶炼制酸污酸处理领域,具体涉及一种污酸浓缩回收利用的方法。 The invention belongs to the field of metal smelting acid waste acid treatment, and in particular relates to a method for concentrating and recycling waste acid.

背景技术 Background technique

在有色金属冶炼过程中,制酸工序产生的大量污酸废水中通常含有As3+、As5+、Cu2+、Pb2+、Zn2+等重金属离子及F、Cl,由于污酸的浓度高、重金属浓度较高,在处理过程中有价金属都转移到废渣中难以回收利用,同时产生大量的危险废物,易造成严重的二次污染。 In the non-ferrous metal smelting process, a large amount of dirty acid wastewater produced by the acid production process usually contains heavy metal ions such as As 3+ , As 5+ , Cu 2+ , Pb 2+ , Zn 2+ and F , Cl . The acid concentration is high and the heavy metal concentration is high. During the treatment process, the valuable metals are transferred to the waste residue, which is difficult to recycle. At the same time, a large amount of hazardous waste is generated, which is easy to cause serious secondary pollution.

目前大部分冶炼企业采用硫化—石灰铁盐法、石灰—铁盐法处理污酸、硫化除杂石灰乳中和法,这些工艺会消耗大量的石灰资源并产生大量的石膏渣,对环境造成严重的污染,资源浪费,生产成本高;现在已有硫化除杂的污酸处理工艺,但是对污酸中的有毒金属砷的去除效率低,达不到环保要求;且很少将硫化除杂与酸的回收综合处理,经济效益较低。 At present, most smelting enterprises adopt sulfide-lime iron salt method, lime-iron salt method to treat dirty acid, sulfide to remove impurities, and lime milk neutralization method. These processes will consume a large amount of lime resources and produce a large amount of gypsum slag, causing serious damage to the environment. pollution, waste of resources, and high production costs; now there is a dirty acid treatment process for sulfuration and impurity removal, but the removal efficiency of the toxic metal arsenic in the dirty acid is low, and the environmental protection requirements are not met; and sulfuration and impurities are rarely combined with The comprehensive treatment of acid recovery has low economic benefits.

发明内容 Contents of the invention

本发明的目的在于提供一种污酸浓缩回用的生产方法,该方法实现了污酸资源的综合回收利用,污酸中重金属及砷的有效分离,达到了节能减排、零排放的目的,降低了生产成本。 The purpose of the present invention is to provide a production method for concentrated reuse of polluted acid, which realizes the comprehensive recycling of polluted acid resources, the effective separation of heavy metals and arsenic in polluted acid, and achieves the goals of energy saving, emission reduction and zero discharge. Reduced production costs.

本发明是通过以下技术方案实现的The present invention is achieved through the following technical solutions

一种污酸浓缩回收利用的方法,包括以下步骤: A method for concentrating and recycling polluted acid, comprising the following steps:

步骤(1):第一次硫化:将用量比为1L:(10~30)g的污酸溶液与硫化剂溶液,加入到压力为-250~-350Pa的负压反应釜中混合均匀,在60~70℃条件下,反应25~40min;在温度低于70℃条件下,密闭容器中,产生少量的H2S气体,少量的硫化氢气体通过引风机由负压为-900~-1000Pa的压力抽吸进入配套的碱液洗涤塔中,通过PH值的控制,洗涤之后得到的硫化钠溶液可以用于硫化剂的配制;负压反应釜内反应完毕的物料通过压滤泵输送至压滤机过滤,过滤之后的滤渣硫化物返回配料系统回收利用;滤液进入到下一个负压反应釜进行第二次硫化; Step (1): The first vulcanization: Add the dirty acid solution and vulcanizing agent solution with a dosage ratio of 1L: (10~30) g to a negative pressure reactor with a pressure of -250~-350Pa and mix evenly. Under the condition of 60~70℃, react for 25~40min; when the temperature is lower than 70℃, a small amount of H 2 S gas is generated in the airtight container, and a small amount of hydrogen sulfide gas passes through the induced draft fan and the negative pressure is -900~-1000Pa The pressure is sucked into the matching lye washing tower, and the sodium sulfide solution obtained after washing can be used to prepare the vulcanizing agent through the control of the pH value; the reacted materials in the negative pressure reactor are transported to the pressure filter pump Filtration by the filter, the filtered residue sulfide is returned to the batching system for recycling; the filtrate enters the next negative pressure reactor for the second vulcanization;

第一次硫化过程中,温度为60~70℃,该温度下不会使过多H2S逸出,保证了硫化物沉淀的有效进行;同时该温度下有利于重金属离子硫化物沉淀的形成,也有利于重金属离子与溶液中As2S3反应的进行,因此不利于砷硫化物沉淀的形成;反应时间较短,也不利于砷硫化物沉淀的形成;该过程中重金属离子的沉淀率达到99.2%,而砷的沉淀率只有3~4.5%;主要反应如下: During the first vulcanization process, the temperature is 60~70°C, at this temperature, too much H 2 S will not escape, ensuring the effective progress of sulfide precipitation; at the same time, this temperature is conducive to the formation of heavy metal ion sulfide precipitation , is also conducive to the reaction of heavy metal ions and As 2 S 3 in the solution, so it is not conducive to the formation of arsenic sulfide precipitation; the reaction time is shorter, and it is also not conducive to the formation of arsenic sulfide precipitation; the precipitation rate of heavy metal ions in this process It reaches 99.2%, while the precipitation rate of arsenic is only 3~4.5%. The main reactions are as follows:

Na2S + H2SO= Na2SO+ H2S Na 2 S + H 2 SO 4 = Na 2 SO 4 + H 2 S

H2S = 2H+ S2- H 2 S = 2H ++ S 2-

Na2S = Na+ S2- Na 2 S = Na ++ S 2-

Cu2+ + S2- = CuS Cu 2+ + S 2- = CuS

Pb2+ + S2- = PbS Pb 2+ + S 2- = PbS

Zn2+ + S2- = ZnS Zn 2+ + S 2- = ZnS

步骤(2):第二次硫化:将用量比为1L:(20~48)g的步骤(1)中得到的滤液与硫化剂溶液,加入到负压为-450~-600Pa的反应釜中混合均匀,室温下反应80~100min停止,该过程中产生很少量的H2S气体,产生的硫化氢气体通过引风机由负压为-900~-1000Pa压力抽吸进入配套的碱液洗涤塔中,负压反应釜内反应完毕的物料经浓密机充分沉淀后,底部的矿浆由浓密机底流口卸出,通过压滤泵输送至压滤机过滤,得到滤渣硫化砷,硫化砷进行专业提砷处理;过滤之后得到的污酸滤液用管道送往污酸浓缩系统。 Step (2): Second vulcanization: add the filtrate and vulcanizing agent solution obtained in step (1) with a dosage ratio of 1L: (20~48) g to a reaction kettle with a negative pressure of -450~-600Pa Mix evenly, and stop the reaction at room temperature for 80~100min. During this process, a small amount of H 2 S gas is produced, and the hydrogen sulfide gas is sucked into the supporting lye washing by the induced draft fan at a negative pressure of -900~-1000Pa. In the tower, after the reacted materials in the negative pressure reactor are fully precipitated by the thickener, the ore slurry at the bottom is discharged from the bottom flow port of the thickener, and is transported to the filter press for filtration through a filter press pump to obtain arsenic sulfide residue, which is processed professionally. Arsenic extraction treatment; the dirty acid filtrate obtained after filtration is sent to the dirty acid concentration system through pipelines.

该反应过程在室温下进行,反应时间较长,有利于砷硫化物沉淀的形成;且能去除第一次硫化过程中剩余的少量其他重金属离子;经过第二次硫化处理之后,污酸中砷的去除率达到99.5%以上;该过程中主要反应如下: The reaction process is carried out at room temperature, and the reaction time is longer, which is conducive to the formation of arsenic sulfide precipitation; and can remove a small amount of other heavy metal ions remaining in the first sulfidation process; after the second sulfidation treatment, the arsenic in the polluted acid The removal rate reaches more than 99.5%; the main reactions in this process are as follows:

Na2S + H2SO4 = Na2SO4 + H2S Na 2 S + H 2 SO 4 = Na 2 SO 4 + H 2 S

H2S = 2H+ + S2- H 2 S = 2H ++ S 2-

Na2S = Na+ + S2- Na 2 S = Na ++ S 2-

As3+ + S2- = As2S3 As 3+ + S 2- = As 2 S 3

步骤(3):经过步骤(2)得到的污酸滤液通过输送泵输送至动力波洗涤塔塔顶,自塔顶向下喷淋;生产系统中产生的余热将空气转化为热空气,进入动力波洗涤塔底部,与自上而下的污酸滤液逆向接触,对污酸滤液进行高温绝热蒸发浓缩,提高酸浓度的同时,由蒸汽带走了大量的F、Cl离子,带走F、Cl离子的尾气从动力波洗涤塔顶部的出气管排出通入配套的碱液洗涤塔形成盐,回收处理。得到浓度为50%~60%的工业硫酸进入储酸槽。经过污酸浓缩处理,F、Cl离子的去除率达到80%以上。 Step (3): The dirty acid filtrate obtained in step (2) is transported to the top of the power wave scrubber through the transfer pump, and sprayed downward from the top of the tower; the waste heat generated in the production system converts the air into hot air and enters the power The bottom of the wave scrubber is in reverse contact with the dirty acid filtrate from top to bottom, and the dirty acid filtrate is concentrated by high-temperature adiabatic evaporation to increase the acid concentration. At the same time, a large amount of F and Cl ions are taken away by the steam, and F and Cl The tail gas of the ions is discharged from the outlet pipe at the top of the power wave scrubber and passed into the matching lye scrubber to form salt for recycling. The obtained industrial sulfuric acid with a concentration of 50%~60% enters the acid storage tank. After concentrated treatment of dirty acid, the removal rate of F and Cl ions can reach more than 80%.

所述的污酸浓缩回收利用的方法,金属冶炼工艺、原料的不同,其制酸系统产生的污酸成分也有所不同,本发明中污酸成分主要为:H2SO4:20000~30000mg/L,As:800~1500mg/L,Cu:600~800mg/L,Zn:300~600mg/L,Pb:100~400mg/L,F:500~1500mg/L,Cl:500~1500mg/L。 The method for concentrating and recycling dirty acid described above depends on the metal smelting process and raw materials, and the dirty acid components produced by the acid making system are also different. The dirty acid components in the present invention are mainly: H 2 SO 4 : 20000~30000mg/ L, As: 800~1500mg/L, Cu: 600~800mg/L, Zn: 300~600mg/L, Pb: 100~400mg/L, F: 500~1500mg/L, Cl: 500~1500mg/L.

所述的污酸浓缩回收利用的方法,步骤(1)、步骤(2)中所述的硫化剂为硫化钠,硫化钠溶液的质量百分含量为10~15%; In the method for concentrating and recycling polluted acid, the vulcanizing agent described in step (1) and step (2) is sodium sulfide, and the mass percentage of sodium sulfide solution is 10-15%;

所述的污酸浓缩回收利用的方法,步骤(1)中所述的滤渣主要为:硫化铜、硫化铅、硫化锌。 In the method for concentrating and recycling dirty acid, the filter residue in step (1) mainly includes: copper sulfide, lead sulfide, and zinc sulfide.

所述的污酸浓缩回收利用的方法,步骤(2)中所述的滤渣主要为:硫化砷。 In the method for concentrating and recycling dirty acid, the filter residue in step (2) is mainly arsenic sulfide.

所述的污酸浓缩回收利用的方法,步骤(3)所述热空气的温度为200~280℃;热空气的通入速率为0.5~1.2m/s。 In the method for concentrating and recycling dirty acid, the temperature of the hot air in step (3) is 200-280° C.; the rate of introduction of the hot air is 0.5-1.2 m/s.

与现有技术相比,本发明具有以下积极效果Compared with the prior art, the present invention has the following positive effects

(1)本发明利用两级硫化与污酸浓缩相结合的方式处理污酸废水,实现了硫资源的综合回收利用,具有提高硫资源利用率、环保节能的特点;实现了有价金属元素的综合回收、资源化利用,减少了污染物排放及原材料的消耗,降低了生产成本。 (1) The present invention uses the combination of two-stage vulcanization and sewage acid concentration to treat polluted acid wastewater, realizes the comprehensive recycling of sulfur resources, has the characteristics of improving the utilization rate of sulfur resources, environmental protection and energy saving; realizes the recovery of valuable metal elements Comprehensive recycling and resource utilization reduce pollutant discharge and raw material consumption, and reduce production costs.

(2)本发明工艺应用范围广,对所有F、Cl、As3+离子浓度小于10g/L的废水均可作为该工艺的原料,如各种硫化矿料冶炼烟气在湿法净化过程中产生的污酸,以及电解车间阳极泥处理过程中产生的酸性污水等。 (2) The process of the present invention has a wide range of applications. It can be used as raw materials for all waste water with F , Cl and As 3+ ion concentrations less than 10g/L, such as the wet purification of various sulfide ore smelting flue gases The dirty acid produced in the process, and the acid sewage produced in the process of anode slime treatment in the electrolysis workshop, etc.

(3)“硫化除杂石灰乳中和法”中和法处理工艺会产生大量的石膏渣,堆放既占用空间又对土壤与水体造成二次污染,这些石膏渣填埋的难度大、费用高;本发明处理方法中以工业硫酸形式回收污酸中的硫资源,提高了硫的利用率,避免产生大量的石膏渣,消除了企业生产运行的环保压力。 (3) The neutralization process of "sulfurized lime milk neutralization method" will produce a large amount of gypsum slag, which not only takes up space but also causes secondary pollution to soil and water. It is difficult and expensive to landfill these gypsum slags ; In the treatment method of the present invention, the sulfur resources in the polluted acid are recovered in the form of industrial sulfuric acid, which improves the utilization rate of sulfur, avoids producing a large amount of gypsum slag, and eliminates the environmental protection pressure of the production and operation of enterprises.

(4)本发明利用生产系统余热产生的热风将污酸浓缩,通过“以废制废”,以工业硫酸形式回收污酸中的硫资源,提高了硫的利用率。 (4) The invention uses the hot air generated by the waste heat of the production system to concentrate the polluted acid, and recovers the sulfur resources in the polluted acid in the form of industrial sulfuric acid by "making waste into waste", thereby improving the utilization rate of sulfur.

(5)本申请采用两次硫化的方法,通过时间与温度的控制,第一次硫化有效的除去了污酸溶液中的重金属离子,得到的金属硫化物返回原料系统作为冶炼的原料;第二次硫化有效的除去了污酸溶液中的砷,并将硫化砷进行专业的炼砷处理。因此在对污酸进行除杂处理时,有效去除并分离了毒性较大的砷,污酸中的金属得到了较好的回收利用,提高了经济效益。本发明经过两次硫化之后的污酸溶液,高温浓缩过程中不仅有效的去除了溶液中F、Cl离子,而且F、Cl经过相应的碱液吸收塔吸收形成盐,回收利用,去除效果好,经济效益高。 (5) This application adopts two vulcanization methods, through the control of time and temperature, the first vulcanization effectively removes the heavy metal ions in the polluted acid solution, and the obtained metal sulfides are returned to the raw material system as raw materials for smelting; the second Subsulfurization effectively removes the arsenic in the polluted acid solution, and the arsenic sulfide is subjected to professional arsenic refining treatment. Therefore, when the impurity removal treatment is carried out on the polluted acid, the highly toxic arsenic is effectively removed and separated, and the metals in the polluted acid are better recovered and utilized, which improves the economic benefits. The present invention not only effectively removes the F and Cl ions in the solution after two vulcanizations in the high-temperature concentration process, but also absorbs the F and Cl to form salts through the corresponding lye absorption tower, which is recycled and utilized, and the removal effect is good. High economic benefit.

(6)本发明提供的处理方法成本低,经济效益显著:以铜冶炼行业为例,据统计每吨铜约产生0.3~0.7m3左右的污酸,采用传统的中和法处理1m3污酸平均成本约150元(不含石灰渣填埋费用),采用本发明处理方法处理1m3污酸的成本比原有工艺可降低50元左右。 (6) The treatment method provided by the present invention has low cost and significant economic benefits: Taking the copper smelting industry as an example, according to statistics, about 0.3-0.7m3 of polluted acid is produced per ton of copper, and the traditional neutralization method is used to treat 1m3 of polluted acid. The average cost of acid is about 150 yuan (excluding the cost of lime slag landfill), and the cost of treating 1m3 of dirty acid with the treatment method of the present invention can be reduced by about 50 yuan compared with the original process.

具体实施例 specific embodiment

为了加深对本发明的理解,下面结合实施例对本发明作进一步的详述,该实施例仅用于解释本发明,并不构成对本发明保护范围的限定。 In order to deepen the understanding of the present invention, the present invention will be further described below in conjunction with examples, which are only used to explain the present invention, and do not constitute a limitation to the protection scope of the present invention.

实施例1Example 1

一种污酸浓缩回收利用的方法,包括以下步骤: A method for concentrating and recycling polluted acid, comprising the following steps:

步骤(1):第一次硫化:将用量比为1L:25g的污酸溶液与硫化钠溶液,加入到压力为-350Pa的负压反应釜中混合均匀,在60℃下反应40min,反应停止后负压反应釜的物料通过压滤泵输送至压滤机过滤,过滤之后的滤渣输送至配料系统回收利用,滤液输送至下一个反应釜进行第二次硫化处理。该过程中产生的少量H2S气体,通过引风机由负压为-950~-1000Pa的压力抽吸进入配套的碱液洗涤塔中。 Step (1): The first vulcanization: Add the dirty acid solution and sodium sulfide solution with a dosage ratio of 1L:25g into a negative pressure reactor with a pressure of -350Pa and mix evenly, react at 60°C for 40min, and the reaction stops The material in the final negative pressure reactor is transported to the filter press for filtration through the filter press pump, and the filtered filter residue is transported to the batching system for recycling, and the filtrate is transported to the next reactor for the second vulcanization treatment. A small amount of H 2 S gas generated in this process is sucked into the matching lye washing tower by the induced draft fan at a negative pressure of -950~-1000Pa.

步骤(2):第二次硫化:将用量比为1L:44g的步骤(1)得到的滤液与硫化钠溶液,加入到负压为-600Pa的负压反应釜中,室温下反应80min,反应停止后负压反应釜内的物料经浓密机充分沉淀后,底部的矿浆由浓密机底流口卸出,通过压滤泵输送至压滤机,过滤之后的滤渣中主要为硫化砷,送往专业厂家进行提砷处理;污酸滤液以及由浓密机顶部环形槽排出的上清液通过管道输送至污酸浓缩系统。该过程中产生少量的H2S气体,通过引风机由负压为-900~-950Pa的压力抽吸进入配套的碱液洗涤塔中。 Step (2): The second vulcanization: Add the filtrate and sodium sulfide solution obtained in the step (1) with a dosage ratio of 1L:44g to a negative pressure reactor with a negative pressure of -600Pa, and react at room temperature for 80min. After stopping, the material in the negative pressure reactor is fully precipitated by the thickener, and the slurry at the bottom is discharged from the bottom flow port of the thickener, and transported to the filter press through the filter pump. After filtering, the filter residue is mainly arsenic sulfide, which is sent to a professional The manufacturer conducts arsenic extraction treatment; the dirty acid filtrate and the supernatant discharged from the ring groove at the top of the thickener are transported to the dirty acid concentration system through pipelines. A small amount of H 2 S gas is generated during this process, which is sucked into the supporting lye washing tower by the induced draft fan at a negative pressure of -900~-950Pa.

步骤(3):经过步骤(2)得到的污酸滤液通过污酸输送泵输送至动力波洗涤塔塔顶,自塔顶向下喷淋;生产系统中产生的余热将空气转化为热空气,热空气的温度为200℃,进入动力波洗涤塔底部,热空气的通入速率为1.2m/s。热空气自塔底向上与污酸滤液逆向充分接触,对污酸滤液进行高温绝热蒸发浓缩,在提高酸浓度的同时,由蒸汽带走了大量的F、Cl离子,带走F、Cl离子从动力波洗涤塔顶部的出气管排出通入配套的碱液洗涤塔形成盐,回收处理。得到浓度为50~60%的工业硫酸进入储酸槽。 Step (3): The dirty acid filtrate obtained in step (2) is transported to the top of the power wave scrubber through the dirty acid delivery pump, and sprayed downward from the top of the tower; the waste heat generated in the production system converts the air into hot air, The temperature of the hot air is 200°C, and it enters the bottom of the dynamic wave scrubber, and the velocity of the hot air is 1.2m/s. The hot air is fully in reverse contact with the dirty acid filtrate from the bottom of the tower to perform high-temperature adiabatic evaporation and concentration on the dirty acid filtrate. While increasing the acid concentration, a large amount of F and Cl ions are taken away by the steam, and F and Cl ions are taken away from the The outlet pipe at the top of the power wave scrubber is discharged into the matching lye scrubber to form salt for recycling. The obtained industrial sulfuric acid with a concentration of 50-60% enters the acid storage tank.

所述的污酸浓缩回收利用的方法,步骤(1)所述的污酸成分主要为:H2SO4:30000mg/L,As:1500mg/L,Cu:800mg/L,Zn:600mg/L,Pb:400mg/L,F: 1500mg/L,Cl:1500mg/L。 In the method for concentrating and recycling dirty acid, the dirty acid components in step (1) are mainly: H 2 SO 4 : 30000mg/L, As: 1500mg/L, Cu: 800mg/L, Zn: 600mg/L , Pb: 400mg/L, F: 1500mg/L, Cl: 1500mg/L.

所述的污酸浓缩回收利用的方法,硫化钠的质量百分含量为:10%。 In the method for concentrating and recycling dirty acid, the mass percentage of sodium sulfide is 10%.

所述的污酸浓缩回收利用的方法,步骤(1)中的滤渣成分主要为:硫化铜、硫化铅、硫化锌。 In the method for concentrating and recycling dirty acid, the filter residue in step (1) mainly includes: copper sulfide, lead sulfide, and zinc sulfide.

所述的污酸浓缩回收利用的方法,步骤(2)中的滤渣成分主要为:硫化砷。 In the method for concentrating and recycling dirty acid, the filter residue in step (2) is mainly composed of arsenic sulfide.

实施例2Example 2

一种污酸浓缩回收利用的方法,包括以下步骤: A method for concentrating and recycling polluted acid, comprising the following steps:

步骤(1):第一次硫化:将用量比为1L:10.5g的污酸溶液与硫化钠溶液,加入到压力为-250Pa的负压反应釜中混合均匀,在70℃下反应25min,反应停止后负压反应釜的物料通过压滤泵输送至压滤机过滤,过滤之后的滤渣输送至配料系统回收利用,滤液输送至下一个反应釜进行第二次硫化处理。该过程中产生的少量H2S气体通过引风机由负压为-950~-1000Pa的压力抽吸进入配套的碱液洗涤塔中。 Step (1): The first vulcanization: Add the dirty acid solution and sodium sulfide solution with a dosage ratio of 1L:10.5g into a negative pressure reactor with a pressure of -250Pa and mix evenly, react at 70°C for 25min, and react After the stop, the material in the negative pressure reactor is transported to the filter press for filtration through the filter press pump, and the filtered filter residue is transported to the batching system for recycling, and the filtrate is transported to the next reactor for the second vulcanization treatment. A small amount of H 2 S gas produced in this process is sucked into the supporting lye washing tower by the induced draft fan at a pressure of -950~-1000Pa.

步骤(2):第二次硫化:将用量比为1L:29g的步骤(1)得到的滤液与硫化钠溶液,加入到负压为-450Pa的负压反应釜中,室温下反应100min,反应停止后负压反应釜内的物料经浓密机充分沉淀后,底部的矿浆由浓密机底流口卸出,通过压滤泵输送至压滤机,过滤之后的滤渣中主要为硫化砷,送往专业厂家进行提砷处理;污酸滤液以及由浓密机顶部环形槽排出的上清液通过管道输送至污酸浓缩系统。该过程中产生少量的H2S气体,通过引风机由负压为-900~-950Pa的压力抽吸进入配套的碱液洗涤塔中。 Step (2): Second vulcanization: Add the filtrate and sodium sulfide solution obtained in step (1) with a dosage ratio of 1L:29g into a negative pressure reactor with a negative pressure of -450Pa, and react at room temperature for 100min. After stopping, the material in the negative pressure reactor is fully precipitated by the thickener, and the slurry at the bottom is discharged from the bottom flow port of the thickener, and transported to the filter press through the filter pump. After filtering, the filter residue is mainly arsenic sulfide, which is sent to a professional The manufacturer conducts arsenic extraction treatment; the dirty acid filtrate and the supernatant discharged from the ring groove at the top of the thickener are transported to the dirty acid concentration system through pipelines. A small amount of H 2 S gas is generated during this process, which is sucked into the supporting lye washing tower by the induced draft fan at a negative pressure of -900~-950Pa.

步骤(3):经过步骤(2)得到的污酸滤液通过污酸输送泵输送至动力波洗涤塔塔顶,自塔顶向下喷淋;生产系统中产生的余热将空气转化为热空气,热空气的温度为280℃,进入动力波洗涤塔底部,热空气的通入速率为0.5m/s。热空气自塔底向上与污酸滤液逆向充分接触,对污酸滤液进行高温绝热蒸发浓缩,在提高酸浓度的同时,由蒸汽带走了大量的F、Cl离子,带走F、Cl离子的尾气从动力波洗涤塔顶部的出气管排出通入配套的碱液洗涤塔形成盐,回收处理。得到浓度为50~60%的工业硫酸进入储酸槽。 Step (3): The dirty acid filtrate obtained in step (2) is transported to the top of the power wave scrubber through the dirty acid delivery pump, and sprayed downward from the top of the tower; the waste heat generated in the production system converts the air into hot air, The temperature of the hot air is 280°C, and it enters the bottom of the dynamic wave scrubber, and the velocity of the hot air is 0.5m/s. The hot air is fully in reverse contact with the dirty acid filtrate from the bottom of the tower to perform high-temperature adiabatic evaporation and concentration on the dirty acid filtrate. While increasing the acid concentration, a large amount of F and Cl ions are taken away by the steam, and the amount of F and Cl ions is taken away. The tail gas is discharged from the outlet pipe at the top of the power wave scrubber and passed into the matching lye scrubber to form salt for recycling. The obtained industrial sulfuric acid with a concentration of 50-60% enters the acid storage tank.

所述的污酸浓缩回收利用的方法,步骤(1)所述的污酸成分主要为:H2SO4:20000mg/L,As:800mg/L,Cu:600mg/L,Zn:300mg/L,Pb:100mg/L,F:500mg/L,Cl:500mg/L。 In the method for concentrating and recycling dirty acid, the dirty acid components in step (1) are mainly: H 2 SO 4 : 20000mg/L, As: 800mg/L, Cu: 600mg/L, Zn: 300mg/L , Pb: 100mg/L, F: 500mg/L, Cl: 500mg/L.

所述的污酸浓缩回收利用的方法,硫化钠的质量百分含量为:15%。 In the method for concentrating and recycling dirty acid, the mass percentage of sodium sulfide is 15%.

所述的污酸浓缩回收利用的方法,步骤(1)中的滤渣成分主要为:硫化铜、硫化铅、硫化锌。 In the method for concentrating and recycling dirty acid, the filter residue in step (1) mainly includes: copper sulfide, lead sulfide, and zinc sulfide.

所述的污酸浓缩回收利用的方法,步骤(2)中的滤渣成分主要为:硫化砷。 In the method for concentrating and recycling dirty acid, the filter residue in step (2) is mainly composed of arsenic sulfide.

实施例3Example 3

一种污酸浓缩回收利用的方法,包括以下步骤: A method for concentrating and recycling polluted acid, comprising the following steps:

步骤(1):第一次硫化:将用量比为1L:17g的污酸溶液与硫化钠溶液,加入到压力为-300Pa的负压反应釜中混合均匀,在65℃下反应32min,反应停止后负压反应釜的物料通过压滤泵输送至压滤机过滤,过滤之后的滤渣输送至配料系统回收利用,滤液输送至下一个反应釜进行第二次硫化处理。该过程中产生的少量H2S气体通过引风机由负压为-950~-1000Pa的压力抽吸进入配套的碱液洗涤塔中。 Step (1): The first vulcanization: add the dirty acid solution and sodium sulfide solution with a dosage ratio of 1L:17g into a negative pressure reactor with a pressure of -300Pa and mix evenly, react at 65°C for 32min, and the reaction stops The material in the final negative pressure reactor is transported to the filter press for filtration through the filter press pump, and the filtered filter residue is transported to the batching system for recycling, and the filtrate is transported to the next reactor for the second vulcanization treatment. A small amount of H 2 S gas produced in this process is sucked into the supporting lye washing tower by the induced draft fan at a pressure of -950~-1000Pa.

步骤(2):第二次硫化:将用量比为1L:29g的步骤(1)得到的滤液与硫化钠溶液,加入到负压为-520Pa的负压反应釜中,室温下反应90min,反应停止后负压反应釜内的物料经浓密机充分沉淀后,底部的矿浆由浓密机底流口卸出,通过压滤泵输送至压滤机,过滤之后的滤渣中主要为硫化砷,送往专业厂家进行提砷处理;污酸滤液以及由浓密机顶部环形槽排出的上清液通过管道输送至污酸浓缩系统。该过程中产生少量的H2S气体,通过引风机由负压为-900~-950Pa的压力抽吸进入配套的碱液洗涤塔中。 Step (2): Second vulcanization: Add the filtrate and sodium sulfide solution obtained in step (1) with a dosage ratio of 1L:29g into a negative pressure reactor with a negative pressure of -520Pa, and react at room temperature for 90min. After stopping, the material in the negative pressure reactor is fully precipitated by the thickener, and the slurry at the bottom is discharged from the bottom flow port of the thickener, and transported to the filter press through the filter pump. After filtering, the filter residue is mainly arsenic sulfide, which is sent to a professional The manufacturer conducts arsenic extraction treatment; the dirty acid filtrate and the supernatant discharged from the ring groove at the top of the thickener are transported to the dirty acid concentration system through pipelines. A small amount of H 2 S gas is generated during this process, which is sucked into the supporting lye washing tower by the induced draft fan at a negative pressure of -900~-950Pa.

步骤(3):经过步骤(2)得到的污酸滤液通过污酸输送泵输送至动力波洗涤塔塔顶,自塔顶向下喷淋;生产系统中产生的余热将空气转化为热空气,热空气的温度为240℃,进入动力波洗涤塔底部,热空气的通入速率为0.8m/s。热空气自塔底向上与污酸滤液逆向充分接触,对污酸滤液进行高温绝热蒸发浓缩,在提高酸浓度的同时,由蒸汽带走了大量的F、Cl离子,带走F、Cl离子的尾气从动力波洗涤塔顶部的出气管排出通入配套的碱液洗涤塔形成盐,回收处理。得到浓度为50~60%的工业硫酸进入储酸槽。  Step (3): The dirty acid filtrate obtained in step (2) is transported to the top of the power wave scrubber through the dirty acid delivery pump, and sprayed downward from the top of the tower; the waste heat generated in the production system converts the air into hot air, The temperature of the hot air is 240°C, and it enters the bottom of the dynamic wave scrubber with a velocity of 0.8m/s. The hot air is fully in reverse contact with the dirty acid filtrate from the bottom of the tower to perform high-temperature adiabatic evaporation and concentration on the dirty acid filtrate. While increasing the acid concentration, a large amount of F and Cl ions are taken away by the steam, and the amount of F and Cl ions is taken away. The tail gas is discharged from the outlet pipe at the top of the power wave scrubber and passed into the matching lye scrubber to form salt for recycling. The obtained industrial sulfuric acid with a concentration of 50-60% enters the acid storage tank. the

所述的污酸浓缩回收利用的方法,步骤(1)所述的污酸成分主要为:H2SO4:25000mg/L,As:1150mg/L,Cu:700mg/L,Zn:450mg/L,Pb:250mg/L,F: 1000mg/L,Cl:1000mg/L。 In the method for concentrating and recycling dirty acid, the dirty acid components in step (1) are mainly: H 2 SO 4 : 25000mg/L, As: 1150mg/L, Cu: 700mg/L, Zn: 450mg/L , Pb: 250mg/L, F: 1000mg/L, Cl: 1000mg/L.

所述的污酸浓缩回收利用的方法,硫化钠的质量百分含量为:12%。 In the method for concentrating and recycling dirty acid, the mass percentage of sodium sulfide is 12%.

所述的污酸浓缩回收利用的方法,步骤(1)中的滤渣成分主要为:硫化铜、硫化铅、硫化锌。 In the method for concentrating and recycling dirty acid, the filter residue in step (1) mainly includes: copper sulfide, lead sulfide, and zinc sulfide.

所述的污酸浓缩回收利用的方法,步骤(2)中的滤渣成分主要为:硫化砷。 In the method for concentrating and recycling dirty acid, the filter residue in step (2) is mainly composed of arsenic sulfide.

实施例4Example 4

一种污酸浓缩回收利用的方法,包括以下步骤: A method for concentrating and recycling polluted acid, comprising the following steps:

步骤(1):第一次硫化:将用量比为1L:16.5g的污酸溶液与硫化钠溶液,加入到压力为-320Pa的负压反应釜中混合均匀,在62℃下反应36min,反应停止后负压反应釜的物料通过压滤泵输送至压滤机过滤,过滤之后的滤渣输送至配料系统回收利用,滤液输送至下一个反应釜进行第二次硫化处理。该过程中产生的少量H2S气体通过引风机由负压为-950~-1000Pa的压力抽吸进入配套的碱液洗涤塔中。 Step (1): The first vulcanization: add the dirty acid solution and sodium sulfide solution with a dosage ratio of 1L:16.5g into a negative pressure reactor with a pressure of -320Pa and mix evenly, react at 62°C for 36min, and react After the stop, the material in the negative pressure reactor is transported to the filter press for filtration through the filter press pump, and the filtered filter residue is transported to the batching system for recycling, and the filtrate is transported to the next reactor for the second vulcanization treatment. A small amount of H 2 S gas produced in this process is sucked into the supporting lye washing tower by the induced draft fan at a pressure of -950~-1000Pa.

步骤(2):第二次硫化:将用量比为1L:31.5g的步骤(1)得到的滤液与硫化钠溶液,加入到负压为-560Pa的负压反应釜中,室温下反应85min,反应停止后负压反应釜内的物料经浓密机充分沉淀后,底部的矿浆由浓密机底流口卸出,通过压滤泵输送至压滤机,过滤之后的滤渣中主要为硫化砷,送往专业厂家进行提砷处理;污酸滤液以及由浓密机顶部环形槽排出的上清液通过管道输送至污酸浓缩系统。该过程中产生少量的H2S气体,通过引风机由负压为-900~-950Pa的压力抽吸进入配套的碱液洗涤塔中。 Step (2): Second vulcanization: Add the filtrate and sodium sulfide solution obtained in step (1) with a dosage ratio of 1L:31.5g into a negative pressure reactor with a negative pressure of -560Pa, and react at room temperature for 85min. After the reaction is stopped, the material in the negative pressure reactor is fully precipitated by the thickener, and the slurry at the bottom is discharged from the bottom flow port of the thickener, and is transported to the filter press through the filter press pump. After filtering, the filter residue is mainly arsenic sulfide, which is sent to Professional manufacturers carry out arsenic extraction treatment; the dirty acid filtrate and the supernatant discharged from the ring groove at the top of the thickener are transported to the dirty acid concentration system through pipelines. A small amount of H 2 S gas is generated during this process, which is sucked into the supporting lye washing tower by the induced draft fan at a negative pressure of -900~-950Pa.

步骤(3):经过步骤(2)得到的污酸滤液通过污酸输送泵输送至动力波洗涤塔塔顶,自塔顶向下喷淋;生产系统中产生的余热将空气转化为热空气,热空气的温度为220℃,进入动力波洗涤塔底部,热空气的通入速率为1.0m/s。热空气自塔底向上与污酸滤液逆向充分接触,对污酸滤液进行高温绝热蒸发浓缩,在提高酸浓度的同时,由蒸汽带走了大量的F、Cl离子,带走F、Cl离子的尾气从动力波洗涤塔顶部的出气管排出通入配套的碱液洗涤塔形成盐,回收处理。得到浓度为50~60%的工业硫酸进入储酸槽。  Step (3): The dirty acid filtrate obtained in step (2) is transported to the top of the power wave scrubber through the dirty acid delivery pump, and sprayed downward from the top of the tower; the waste heat generated in the production system converts the air into hot air, The temperature of the hot air is 220°C, and it enters the bottom of the dynamic wave scrubber, and the velocity of the hot air is 1.0m/s. The hot air is fully in reverse contact with the dirty acid filtrate from the bottom of the tower to perform high-temperature adiabatic evaporation and concentration on the dirty acid filtrate. While increasing the acid concentration, a large amount of F and Cl ions are taken away by the steam, and the amount of F and Cl ions is taken away. The tail gas is discharged from the outlet pipe at the top of the power wave scrubber and passed into the matching lye scrubber to form salt for recycling. The obtained industrial sulfuric acid with a concentration of 50-60% enters the acid storage tank. the

所述的污酸浓缩回收利用的方法,步骤(1)所述的污酸成分主要为:H2SO4:27500mg/L,As:1320mg/L,Cu:750mg/L,Zn:520mg/L,Pb:320mg/L,F: 1250mg/L,Cl:1250mg/L。 In the method for concentrating and recycling dirty acid, the dirty acid components in step (1) are mainly: H 2 SO 4 : 27500mg/L, As: 1320mg/L, Cu: 750mg/L, Zn: 520mg/L , Pb: 320mg/L, F: 1250mg/L, Cl: 1250mg/L.

所述的污酸浓缩回收利用的方法,硫化钠的质量百分含量为:13%。 In the method for concentrating and recycling dirty acid, the mass percentage of sodium sulfide is 13%.

所述的污酸浓缩回收利用的方法,步骤(1)中的滤渣成分主要为:硫化铜、硫化铅、硫化锌。 In the method for concentrating and recycling dirty acid, the filter residue in step (1) mainly includes: copper sulfide, lead sulfide, and zinc sulfide.

所述的污酸浓缩回收利用的方法,步骤(2)中的滤渣成分主要为:硫化砷。 In the method for concentrating and recycling dirty acid, the filter residue in step (2) is mainly composed of arsenic sulfide.

实施例5Example 5

一种污酸浓缩回收利用的方法,包括以下步骤: A method for concentrating and recycling polluted acid, comprising the following steps:

步骤(1):第一次硫化:将用量比为1L:12g的污酸溶液与硫化钠溶液,加入到压力为-280Pa的负压反应釜中混合均匀,在68℃下反应30min,反应停止后负压反应釜的物料通过压滤泵输送至压滤机过滤,过滤之后的滤渣输送至配料系统回收利用,滤液输送至下一个反应釜进行第二次硫化处理。该过程中产生的少量H2S气体通过引风机由负压为-950~-1000Pa的压力抽吸进入配套的碱液洗涤塔中。 Step (1): The first vulcanization: Add the dirty acid solution and sodium sulfide solution with a dosage ratio of 1L:12g into a negative pressure reactor with a pressure of -280Pa and mix evenly, react at 68°C for 30min, and the reaction stops The material in the final negative pressure reactor is transported to the filter press for filtration through the filter press pump, and the filtered filter residue is transported to the batching system for recycling, and the filtrate is transported to the next reactor for the second vulcanization treatment. A small amount of H 2 S gas produced in this process is sucked into the supporting lye washing tower by the induced draft fan at a pressure of -950~-1000Pa.

步骤(2):第二次硫化:将用量比为1L:20.5g的步骤(1)得到的滤液与硫化钠溶液,加入到负压为-480Pa的负压反应釜中,室温下反应95min,反应停止后负压反应釜内的物料经浓密机充分沉淀后,底部的矿浆由浓密机底流口卸出,通过压滤泵输送至压滤机,过滤之后的滤渣中主要为硫化砷,送往专业厂家进行提砷处理;污酸滤液以及由浓密机顶部环形槽排出的上清液通过管道输送至污酸浓缩系统。该过程中产生少量的H2S气体,通过引风机由负压为-900~-950Pa的压力抽吸进入配套的碱液洗涤塔中。 Step (2): Second vulcanization: add the filtrate and sodium sulfide solution obtained in step (1) with a dosage ratio of 1L:20.5g into a negative pressure reactor with a negative pressure of -480Pa, and react at room temperature for 95min. After the reaction is stopped, the material in the negative pressure reactor is fully precipitated by the thickener, and the slurry at the bottom is discharged from the bottom flow port of the thickener, and is transported to the filter press through the filter press pump. After filtering, the filter residue is mainly arsenic sulfide, which is sent to Professional manufacturers carry out arsenic extraction treatment; the dirty acid filtrate and the supernatant discharged from the ring groove at the top of the thickener are transported to the dirty acid concentration system through pipelines. A small amount of H 2 S gas is generated during this process, which is sucked into the supporting lye washing tower by the induced draft fan at a negative pressure of -900~-950Pa.

步骤(3):经过步骤(2)得到的污酸滤液通过污酸输送泵输送至动力波洗涤塔塔顶,自塔顶向下喷淋;生产系统中产生的余热将空气转化为热空气,热空气的温度为260℃,进入动力波洗涤塔底部,热空气的通入速率为0.7m/s。热空气自塔底向上与污酸滤液逆向充分接触,对污酸滤液进行高温绝热蒸发浓缩,在提高酸浓度的同时,由蒸汽带走了大量的F、Cl离子,带走F、Cl离子的尾气从动力波洗涤塔顶部的出气管排出通入配套的碱液洗涤塔形成盐,回收处理。得到浓度为50~60%的工业硫酸进入储酸槽。  Step (3): The dirty acid filtrate obtained in step (2) is transported to the top of the power wave scrubber through the dirty acid delivery pump, and sprayed downward from the top of the tower; the waste heat generated in the production system converts the air into hot air, The temperature of the hot air is 260°C, and it enters the bottom of the dynamic wave scrubber with a velocity of 0.7m/s. The hot air is fully in reverse contact with the dirty acid filtrate from the bottom of the tower, and the high-temperature adiabatic evaporation and concentration of the dirty acid filtrate is carried out. While increasing the acid concentration, a large amount of F and Cl ions are taken away by the steam, and the amount of F and Cl ions is taken away. The tail gas is discharged from the outlet pipe at the top of the power wave scrubber and passed into the matching lye scrubber to form salt for recycling. The obtained industrial sulfuric acid with a concentration of 50-60% enters the acid storage tank. the

所述的污酸浓缩回收利用的方法,步骤(1)所述的污酸成分主要为:H2SO4:22500mg/L,As:980mg/L,Cu:650mg/L,Zn:380mg/L,Pb:180mg/L,F: 750mg/L,Cl:750mg/L。 In the method for concentrating and recycling dirty acid, the dirty acid components in step (1) are mainly: H 2 SO 4 : 22500mg/L, As: 980mg/L, Cu: 650mg/L, Zn: 380mg/L , Pb: 180mg/L, F: 750mg/L, Cl: 750mg/L.

所述的污酸浓缩回收利用的方法,硫化钠的质量百分含量为:15%。 In the method for concentrating and recycling dirty acid, the mass percentage of sodium sulfide is 15%.

所述的污酸浓缩回收利用的方法,步骤(1)中的滤渣成分主要为:硫化铜、硫化铅、硫化锌。 In the method for concentrating and recycling dirty acid, the filter residue in step (1) mainly includes: copper sulfide, lead sulfide, and zinc sulfide.

所述的污酸浓缩回收利用的方法,步骤(2)中的滤渣成分主要为:硫化砷。 In the method for concentrating and recycling dirty acid, the filter residue in step (2) is mainly composed of arsenic sulfide.

实施例6Example 6

一种污酸浓缩回收利用的方法,包括以下步骤: A method for concentrating and recycling polluted acid, comprising the following steps:

步骤(1):第一次硫化:将用量比为1L:15g的酸溶液与硫化钠溶液,加入到压力为-290Pa的负压反应釜中混合均匀,在67℃下反应30min,反应停止后负压反应釜的物料通过压滤泵输送至压滤机过滤,过滤之后的滤渣输送至配料系统回收利用,滤液输送至下一个反应釜进行第二次硫化处理。该过程中产生的少量H2S气体通过引风机由负压为-950~-1000Pa的压力抽吸进入配套的碱液洗涤塔中。 Step (1): The first vulcanization: Add the acid solution and sodium sulfide solution with a dosage ratio of 1L:15g into a negative pressure reactor with a pressure of -290Pa and mix evenly, react at 67°C for 30min, after the reaction stops The material in the negative pressure reactor is transported to the filter press for filtration through the filter press pump, and the filtered residue is transported to the batching system for recycling, and the filtrate is transported to the next reactor for the second vulcanization treatment. A small amount of H 2 S gas produced in this process is sucked into the supporting lye washing tower by the induced draft fan at a pressure of -950~-1000Pa.

步骤(2):第二次硫化:将用量比为1L:22.5g的步骤(1)得到的滤液与硫化钠溶液,加入到负压为-500Pa的负压反应釜中,室温下反应93min,反应停止后负压反应釜内的物料经浓密机充分沉淀后,底部的矿浆由浓密机底流口卸出,通过压滤泵输送至压滤机,过滤之后的滤渣中主要为硫化砷,送往专业厂家进行提砷处理;污酸滤液以及由浓密机顶部环形槽排出的上清液通过管道输送至污酸浓缩系统。该过程中产生少量的H2S气体,通过引风机由负压为-900~-950Pa的压力抽吸进入配套的碱液洗涤塔中。 Step (2): Second vulcanization: Add the filtrate and sodium sulfide solution obtained in step (1) with a dosage ratio of 1L:22.5g into a negative pressure reactor with a negative pressure of -500Pa, and react at room temperature for 93min. After the reaction is stopped, the material in the negative pressure reactor is fully precipitated by the thickener, and the slurry at the bottom is discharged from the bottom flow port of the thickener, and is transported to the filter press through the filter press pump. After filtering, the filter residue is mainly arsenic sulfide, which is sent to Professional manufacturers carry out arsenic extraction treatment; the dirty acid filtrate and the supernatant discharged from the ring groove at the top of the thickener are transported to the dirty acid concentration system through pipelines. A small amount of H 2 S gas is generated during this process, which is sucked into the supporting lye washing tower by the induced draft fan at a negative pressure of -900~-950Pa.

步骤(3):经过步骤(2)得到的污酸滤液通过污酸输送泵输送至动力波洗涤塔塔顶,自塔顶向下喷淋;酸生产系统中产生的余热将空气转化为热空气,热空气的温度为250℃,进入动力波洗涤塔底部,热空气的通入速率为0.8m/s。热空气自塔底向上与污酸滤液逆向充分接触,对污酸滤液进行高温绝热蒸发浓缩,在提高酸浓度的同时,由蒸汽带走了大量的F、Cl离子,带走F、Cl离子的尾气从动力波洗涤塔顶部的出气管排出通入配套的碱液洗涤塔形成盐,回收处理。得到浓度为50~60%的工业硫酸进入储酸槽。  Step (3): The dirty acid filtrate obtained in step (2) is transported to the top of the power wave scrubber through the dirty acid delivery pump, and sprayed downward from the top of the tower; the waste heat generated in the acid production system converts the air into hot air , the temperature of the hot air is 250°C, it enters the bottom of the dynamic wave scrubber, and the velocity of the hot air is 0.8m/s. The hot air is fully in reverse contact with the dirty acid filtrate from the bottom of the tower to perform high-temperature adiabatic evaporation and concentration on the dirty acid filtrate. While increasing the acid concentration, a large amount of F and Cl ions are taken away by the steam, and the amount of F and Cl ions is taken away. The tail gas is discharged from the outlet pipe at the top of the power wave scrubber and passed into the matching lye scrubber to form salt for recycling. The obtained industrial sulfuric acid with a concentration of 50-60% enters the acid storage tank. the

所述的污酸浓缩回收利用的方法,步骤(1)所述的污酸成分主要为:H2SO4:24000mg/L,As:1000mg/L,Cu:690mg/L,Zn:530mg/L,Pb:240mg/L,F: 900mg/L,Cl:900mg/L。 In the method for concentrating and recycling dirty acid, the dirty acid components in step (1) are mainly: H 2 SO 4 : 24000mg/L, As: 1000mg/L, Cu: 690mg/L, Zn: 530mg/L , Pb: 240mg/L, F: 900mg/L, Cl: 900mg/L.

所述的污酸浓缩回收利用的方法,硫化钠的质量百分含量为:14%。 In the method for concentrating and recycling dirty acid, the mass percentage of sodium sulfide is 14%.

所述的污酸浓缩回收利用的方法,步骤(1)中的滤渣成分主要为:硫化铜、硫化铅、硫化锌。 In the method for concentrating and recycling dirty acid, the filter residue in step (1) mainly includes: copper sulfide, lead sulfide, and zinc sulfide.

所述的污酸浓缩回收利用的方法,步骤(2)中的滤渣成分主要为:硫化砷。 In the method for concentrating and recycling dirty acid, the filter residue in step (2) is mainly composed of arsenic sulfide.

.

Claims (8)

1.一种污酸浓缩回收利用的方法,其特征在于,包括以下步骤: 1. a method for concentrating and recycling polluted acid, is characterized in that, comprises the following steps: 步骤(1):取污酸溶液、硫化剂溶液,加入到负压反应釜中混合均匀后反应,反应停止后负压反应釜内的物料通过压滤泵输送至压滤机过滤,滤渣回收利用,滤液进入下一步处理; Step (1): Take the dirty acid solution and vulcanizing agent solution, add them to the negative pressure reactor, mix them evenly, and then react. After the reaction stops, the materials in the negative pressure reactor are sent to the filter press for filtration through the filter press pump, and the filter residue is recycled. , the filtrate enters the next step for processing; 步骤(2):取步骤(1)得到的滤液、硫化剂溶液,加入到负压反应釜中混合均匀后反应,反应停止后,反应釜中的物料输送至浓密机沉淀后,浆料由压滤泵输送至压滤机过滤,滤渣进行回收处理,污酸滤液进入下一步处理; Step (2): Take the filtrate and vulcanizing agent solution obtained in step (1), add them to the negative pressure reactor, mix them evenly, and then react. The filter pump is transported to the filter press for filtration, the filter residue is recycled, and the dirty acid filtrate enters the next step of treatment; 步骤(3):经过步骤(2)硫化处理之后得到的污酸滤液通过污酸输送泵输送至动力波洗涤塔塔顶,自塔顶向下喷淋;热空气进入动力波洗涤塔底部,与污酸滤液逆流接触,热空气对污酸滤液高温绝热蒸发浓缩,带有F-、Cl-的尾气从动力波洗涤塔顶部的出气管排出通入碱液洗涤塔,塔内得到工业品硫酸进入储酸槽。 Step (3): The dirty acid filtrate obtained after the vulcanization treatment in step (2) is transported to the top of the power wave scrubber by the dirty acid delivery pump, and sprayed downward from the top of the tower; hot air enters the bottom of the power wave scrubber, and The dirty acid filtrate is in countercurrent contact, the hot air is concentrated by high-temperature adiabatic evaporation on the dirty acid filtrate, and the tail gas with F - and Cl - is discharged from the outlet pipe at the top of the power wave washing tower and passed into the alkali washing tower, where industrial sulfuric acid enters Acid storage tank. 2.根据权利要求1所述的污酸浓缩回收利用的方法,其特征在于:步骤(1)所述的污酸成分为:H2SO4:20000~30000mg/L,As:800~1500mg/L,Cu:600~800mg/L,Zn:300~600mg/L,Pb:100~400mg/L,F:500~1500mg/L,Cl:500~1500mg/L。 2. The method for concentrating and recycling dirty acid according to claim 1, characterized in that: the dirty acid components in step (1) are: H 2 SO 4 : 20000~30000mg/L, As: 800~1500mg/L L, Cu: 600~800mg/L, Zn: 300~600mg/L, Pb: 100~400mg/L, F: 500~1500mg/L, Cl: 500~1500mg/L. 3.根据权利要求1所述的污酸浓缩回收利用的方法,其特征在于:步骤(1)、步骤(2)中所述的硫化剂为硫化钠溶液,硫化钠溶液的质量百分含量为10~15%。 3. The method for concentrating and recycling polluted acid according to claim 1, characterized in that: the vulcanizing agent described in step (1) and step (2) is a sodium sulfide solution, and the mass percentage of the sodium sulfide solution is 10~15%. 4.根据权利要求1所述的污酸浓缩回收利用的方法,其特征在于:步骤(1)所述的加入污酸与硫化剂溶液的用量比为1L:(10~30)g。 4. The method for concentrating and recycling polluted acid according to claim 1, characterized in that the ratio of the amount of polluted acid added to the vulcanizing agent solution in step (1) is 1L: (10~30) g. 5.根据权利要求1所述的污酸浓缩回收利用的方法,其特征在于:步骤(1)所述的负压反应釜内的反应压力为-250~-350Pa,反应温度为60~70℃,反应时间为25~40min。 5. The method for concentrating and recycling dirty acid according to claim 1, characterized in that: the reaction pressure in the negative pressure reactor described in step (1) is -250~-350Pa, and the reaction temperature is 60~70°C , The reaction time is 25~40min. 6.根据权利要求1所述的污酸浓缩回收利用的方法,其特征在于:步骤(2)所述的加入到负压反应釜中的滤液与硫化剂溶液的用量比为:1L:(20~48)g。 6. The method for concentrating and recycling polluted acid according to claim 1, characterized in that: the dosage ratio of the filtrate added to the negative pressure reactor described in step (2) and the vulcanizing agent solution is: 1L: (20 ~48) g. 7.根据权利要求1所述的污酸浓缩回收利用的方法,其特征在于:步骤(2)所述的反应釜内的反应压力为-450~-600Pa,室温下反应80~100min。 7. The method for concentrating and recycling polluted acid according to claim 1, characterized in that: the reaction pressure in the reactor described in step (2) is -450~-600Pa, and the reaction takes 80~100min at room temperature. 8.根据权利要求1所述的污酸浓缩回收利用的方法,其特征在于:步骤(3)所述的热空气的温度为200~280℃,热空气的通入速率为0.5~1.2m/s。 8. The method for concentrating and recycling dirty acid according to claim 1, characterized in that: the temperature of the hot air in step (3) is 200-280°C, and the rate of introduction of the hot air is 0.5-1.2m/ s.
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Cited By (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105502307A (en) * 2015-12-24 2016-04-20 南通三圣石墨设备科技股份有限公司 Method for removing fluorine and chlorine from waste acid through concentration and special device
CN105617843A (en) * 2016-02-14 2016-06-01 楚雄滇中有色金属有限责任公司 Contaminated acid treatment water recycling method
CN107162306A (en) * 2017-07-07 2017-09-15 湖南求是检测科技有限公司 A kind of recycling processing method of battery spent acid
CN107512813A (en) * 2017-08-25 2017-12-26 金川集团股份有限公司 A kind of multipath recoverying and utilizing method of metallurgical off-gas acid-making waste water
CN107935022A (en) * 2017-12-08 2018-04-20 南丹县南方有色金属有限责任公司 A kind of zinc oxide desulfurization washing system
CN108946889A (en) * 2017-06-01 2018-12-07 株洲三特环保节能股份有限公司 A kind of processing method and processing equipment of the spent acid containing heavy metal
CN108996743A (en) * 2018-07-26 2018-12-14 甘肃中顺石化工程装备有限公司 A kind of smelting waste acid deep treatment method and smelt waste acid advanced treatment system
CN109019530A (en) * 2018-10-31 2018-12-18 河南菲迪泰环境科技有限公司 A kind of waste acid processing recovery system and its processing recovery method
CN109354098A (en) * 2018-12-21 2019-02-19 萍乡市新安环保工程有限公司 A kind of desulfurization wastewater treatment system and method
CN110923440A (en) * 2019-11-22 2020-03-27 西北矿冶研究院 A kind of copper smelting wastewater removal arsenic and heavy metal recovery method
CN116062951A (en) * 2023-03-16 2023-05-05 天津高能时代水处理科技有限公司 Zero-emission process system for waste acid and wastewater and waste acid and wastewater treatment method

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP2042471A2 (en) * 2007-09-24 2009-04-01 PLINKE GmbH Method for concentrating sulphuric acid
CN101857203A (en) * 2010-05-24 2010-10-13 东营方圆有色金属有限公司 Process for comprehensively recycling heavy metal-polluted acid
CN102424368A (en) * 2011-09-27 2012-04-25 东营方圆有色金属有限公司 Process for removing F, Cl and As from waste acid by hot air concentration method

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP2042471A2 (en) * 2007-09-24 2009-04-01 PLINKE GmbH Method for concentrating sulphuric acid
CN101857203A (en) * 2010-05-24 2010-10-13 东营方圆有色金属有限公司 Process for comprehensively recycling heavy metal-polluted acid
CN102424368A (en) * 2011-09-27 2012-04-25 东营方圆有色金属有限公司 Process for removing F, Cl and As from waste acid by hot air concentration method

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* Cited by examiner, † Cited by third party
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CN105617843A (en) * 2016-02-14 2016-06-01 楚雄滇中有色金属有限责任公司 Contaminated acid treatment water recycling method
CN108946889A (en) * 2017-06-01 2018-12-07 株洲三特环保节能股份有限公司 A kind of processing method and processing equipment of the spent acid containing heavy metal
CN107162306A (en) * 2017-07-07 2017-09-15 湖南求是检测科技有限公司 A kind of recycling processing method of battery spent acid
CN107512813A (en) * 2017-08-25 2017-12-26 金川集团股份有限公司 A kind of multipath recoverying and utilizing method of metallurgical off-gas acid-making waste water
CN107935022B (en) * 2017-12-08 2024-05-10 南丹县南方有色金属有限责任公司 Zinc oxide desulfurization washing system
CN107935022A (en) * 2017-12-08 2018-04-20 南丹县南方有色金属有限责任公司 A kind of zinc oxide desulfurization washing system
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CN109019530B (en) * 2018-10-31 2023-08-08 河南菲迪泰环境科技有限公司 Sewage acid treatment and recovery system and treatment and recovery method thereof
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