WO2019148901A1 - Method for treating chromium slag by chlorinating calcination in combination with hydrothermal mineralization - Google Patents
Method for treating chromium slag by chlorinating calcination in combination with hydrothermal mineralization Download PDFInfo
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- WO2019148901A1 WO2019148901A1 PCT/CN2018/111616 CN2018111616W WO2019148901A1 WO 2019148901 A1 WO2019148901 A1 WO 2019148901A1 CN 2018111616 W CN2018111616 W CN 2018111616W WO 2019148901 A1 WO2019148901 A1 WO 2019148901A1
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- C—CHEMISTRY; METALLURGY
- C22—METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
- C22B—PRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
- C22B1/00—Preliminary treatment of ores or scrap
- C22B1/02—Roasting processes
- C22B1/08—Chloridising roasting
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- C—CHEMISTRY; METALLURGY
- C22—METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
- C22B—PRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
- C22B3/00—Extraction of metal compounds from ores or concentrates by wet processes
- C22B3/20—Treatment or purification of solutions, e.g. obtained by leaching
- C22B3/22—Treatment or purification of solutions, e.g. obtained by leaching by physical processes, e.g. by filtration, by magnetic means, or by thermal decomposition
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- C—CHEMISTRY; METALLURGY
- C22—METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
- C22B—PRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
- C22B3/00—Extraction of metal compounds from ores or concentrates by wet processes
- C22B3/20—Treatment or purification of solutions, e.g. obtained by leaching
- C22B3/44—Treatment or purification of solutions, e.g. obtained by leaching by chemical processes
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- C—CHEMISTRY; METALLURGY
- C22—METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
- C22B—PRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
- C22B34/00—Obtaining refractory metals
- C22B34/30—Obtaining chromium, molybdenum or tungsten
- C22B34/32—Obtaining chromium
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- C—CHEMISTRY; METALLURGY
- C22—METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
- C22B—PRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
- C22B7/00—Working up raw materials other than ores, e.g. scrap, to produce non-ferrous metals and compounds thereof; Methods of a general interest or applied to the winning of more than two metals
- C22B7/006—Wet processes
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- C—CHEMISTRY; METALLURGY
- C22—METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
- C22B—PRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
- C22B7/00—Working up raw materials other than ores, e.g. scrap, to produce non-ferrous metals and compounds thereof; Methods of a general interest or applied to the winning of more than two metals
- C22B7/006—Wet processes
- C22B7/008—Wet processes by an alkaline or ammoniacal leaching
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- C—CHEMISTRY; METALLURGY
- C22—METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
- C22B—PRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
- C22B7/00—Working up raw materials other than ores, e.g. scrap, to produce non-ferrous metals and compounds thereof; Methods of a general interest or applied to the winning of more than two metals
- C22B7/04—Working-up slag
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- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P10/00—Technologies related to metal processing
- Y02P10/20—Recycling
Definitions
- the invention belongs to the technical field of chromium slag treatment, and particularly relates to a method for treating chromium residue by chlorination roasting combined with hydrothermal mineralization.
- the chromium pollution is mainly derived from the chromium salt production and use industry, and is mainly based on the pollution of chromium-containing waste residue.
- Calcium roasting and calcium-free roasting processes used in the production of chromium salts produce chromium-containing waste residues. Among them, the calcium roasting process will produce 2-3 tons of chromium slag per ton of product produced. Although calcium-free roasting significantly reduces the chromium slag emissions and the hexavalent chromium content, the risk remains. In view of this, in order to get rid of the pollution caused by chromium slag, some developed countries continue to compress chromium salt production capacity and import chromium salt products from developing countries.
- the harmlessness of chromium slag is mainly the in-situ reduction/fixation of chromium slag to reduce its toxicity, and chromium is still in the slag.
- chromium is still in the slag.
- the trivalent chromium in the chromium residue after detoxification may still be reoxidized to hexavalent chromium under the action of long-term oxidation conditions in the environment or by the action of manganese oxidizing bacteria, and has secondary toxicity.
- chromium slag or industrial chrome-containing solid waste
- chromium slag or industrial chrome-containing solid waste
- the chlorination roasting method is mainly used in the metallurgical industry.
- the chlorine element is chemically active and has a wide range of applications. Under certain conditions, it is easier to react with most metals or compounds such as metal oxides to form metal chlorides.
- Other metal compounds such as oxides, sulfides, etc.
- metal chlorides are easily soluble in water, ethanol and other solvents, relatively low melting point, easy to volatilize, etc., and for different metals, the degree of oxidation is different and There are significant differences in the physicochemical properties of the resulting metal-vaporized.
- the chlorination roasting method is to convert the target metal component in the mineral raw material into a corresponding chloride by using a chlorinating agent such as chlorine gas, hydrogen chloride or solid chloride salt in the roasting process, and to achieve the target metal according to the characteristics of the above metal chloride
- a chlorinating agent such as chlorine gas, hydrogen chloride or solid chloride salt in the roasting process
- the high-temperature chlorination roasting method can be used to directly separate the metal from the gangue in the form of a gas phase or a molten phase, and the refining mineral raw material can be purified by other extraction methods such as infiltration.
- the chlorination roasting method has lower operating temperature than other pyrometallurgical methods and saves energy; finally, the chlorination roasting method is beneficial to the comprehensive utilization of ore, and the metal separation efficiency is high; according to the difficulty of chlorination for different metals, The physicochemical properties of the produced metal chlorides are significantly different. Therefore, for the comprehensive utilization of low-grade components complex ore and waste tailings, the chlorination roasting method can be used to effectively separate the enriched metals, and the comprehensive utilization effect is obvious.
- the current chlorination roasting method is mainly used for the separation and enrichment of metals in industrial metallurgical mineral raw materials. There has not been any report on the combined treatment of chlorination roasting with hydrothermal mineralization.
- the Chinese patent "Recycling Process for Treatment of Chromium Slag and Wastewater” (CN102699006A) takes into account the recovery of chromium and the reuse of solid slag. Under normal temperature conditions, the chromium slag is almost completely dissolved with acid, and then different precipitants are added separately. The mixed ions in the solution are precipitated and separated, but this method requires a large amount of chemical reagents such as an acid and a precipitant, and the process is complicated and the treatment cost is high.
- a method for treating chrome slag by chlorination roasting combined with hydrothermal mineralization comprises the following steps:
- step (2) adding the fine powder after the step (1) is added to the hydrothermal reactor, adding a mineralizer aqueous solution, hydrothermal mineralization reaction at a temperature of 30 to 250 ° C for 2 to 24 hours;
- step (3) The mixed liquid obtained in the step (2) is cooled and allowed to stand to obtain a chromium-containing supernatant liquid and solid residue, and the solid residue is washed with water and dried to obtain detoxified chromium residue, and the chromium-containing supernatant is used for production. Or recycle chrome.
- the chloride salt in step (1) is sodium chloride or calcium chloride.
- the mass ratio of the chromium slag to the chloride salt is 1: (0.5 to 1.5).
- the mineralizer described in the step (2) is at least one of sodium carbonate and sodium hydrogencarbonate; and the concentration of the mineralizer aqueous solution is 0.5 to 1.5 mol/L.
- the solid-liquid ratio of the sieved fine powder and the mineralizer aqueous solution in the step (2) is 1: (0.5 to 10) (w/w).
- the step of recovering the chromium treatment in the step (3) is: adding a reducing agent to reduce the hexavalent chromium of the solution to trivalent chromium, and then adding a precipitating agent NaOH to produce a Cr(OH) 3 precipitate for recovery.
- the reducing agent includes sodium sulfide, sodium hydrogen sulfite, and the like.
- the leaching of hexavalent chromium includes not only the surface free state and the leaching of the adsorbed hexavalent chromium, but also the slow diffusion and dissolution of the soluble hexavalent chromium trapped inside the solid particles.
- the package leads to a large mass transfer resistance, and the hexavalent chromium in the sandwich state is difficult to leaching in a short time.
- the chlorination roasting method can be selected to react with most metals or metal compounds including chromium at high temperature to form corresponding chlorides, which have the characteristics of lower melting point and can be released inside the microscopic solid particles to reach the metal materials including chromium and
- the purpose of separation of other solid phase impurities is to improve chromium separation and refining efficiency, and ultimately increase the recovery rate of chromium.
- the subsequent mineralizer hydrothermal treatment causes a small amount of trivalent chromium in the chromium slag to be oxidized to hexavalent chromium, and it is easier to enter the solution with the presence of dichromate.
- the invention combines the chlorination roasting technology in industrial metallurgy to treat the chromium slag, solves the problem that the hexavalent chromium in the chromium slag is difficult to separate from the internal solid particles (including aluminosilicate, iron oxide, etc.), and improves the separation of chromium. Efficiency and recycling efficiency.
- the treated slag leaching hexavalent chromium content is lower than the national standard (HJ/T301-2007) general industrial solid waste residue, and the process is simple, suitable for large-scale industrial production processes, large processing capacity, high recovery rate, detoxification The effect is good, with high social and economic benefits.
- FIG. 1 is a schematic flow chart of a chlorination roasting combined with hydrothermal mineralization treatment of chromium slag according to an embodiment of the present invention.
- FIG. 1 A method for chlorination roasting combined with hydrothermal mineralization to treat chromium slag according to the embodiment is shown in FIG. 1 . Specific steps are as follows:
- the mixture obtained in the step (2) is naturally cooled to room temperature and allowed to stand for 12 hours to obtain a chromium-containing supernatant liquid and solid residue, and the solid residue is separated from the chromium-containing supernatant by filtration, and the solid residue is washed with water, dried and dried.
- the chromium-containing supernatant is reused in the production, or collected in a wastewater treatment station for reduction, recovery, purification treatment (adding a reducing agent (such as sodium sulfide, sodium hydrogen sulfite), the solution
- the hexavalent chromium is reduced to trivalent chromium, and the precipitated NaOH is added to produce Cr(OH) 3 precipitate for recovery.
- the water can reach the national drainage standard). Water can be recycled in the system throughout the process.
- the original chromium residue of the present embodiment has a hexavalent chromium concentration of 740 mg/L, and the treated residue has a hexavalent chromium concentration of 0.975 mg/L.
- FIG. 1 A method for chlorination roasting combined with hydrothermal mineralization to treat chromium slag according to the embodiment is shown in FIG. 1 . Specific steps are as follows:
- the mixture obtained in the step (2) is naturally cooled to room temperature and allowed to stand for 0.5 h to obtain a chromium-containing supernatant liquid and solid residue, and the solid residue is separated from the chromium-containing supernatant by filtration, and the solid residue is washed with water and dried.
- the chromium-containing supernatant is reused in production, or collected in a wastewater treatment station for reduction, recovery, and purification treatment (adding a reducing agent (such as sodium sulfide, sodium hydrogen sulfite),
- the solution of hexavalent chromium is reduced to trivalent chromium, and the precipitated NaOH is added to produce Cr(OH) 3 precipitate for recovery.
- the water can reach the national drainage standard). Water can be recycled in the system throughout the process.
- the original chromium residue of the present embodiment has a hexavalent chromium concentration of 763 mg/L, and the treated residue has a hexavalent chromium concentration of 1.025 mg/L.
- FIG. 1 A method for chlorination roasting combined with hydrothermal mineralization to treat chromium slag according to the embodiment is shown in FIG. 1 . Specific steps are as follows:
- the mixture obtained in the step (2) is naturally cooled to room temperature and allowed to stand for 0.5 h to obtain a chromium-containing supernatant liquid and solid residue, and the solid residue is separated from the chromium-containing supernatant by filtration, and the solid residue is washed with water and dried.
- the chromium-containing supernatant is reused in production, or collected in a wastewater treatment station for reduction, recovery, and purification treatment (adding a reducing agent (such as sodium sulfide, sodium hydrogen sulfite),
- the solution of hexavalent chromium is reduced to trivalent chromium, and the precipitated NaOH is added to produce Cr(OH) 3 precipitate for recovery.
- the water can reach the national drainage standard). Water can be recycled in the system throughout the process.
- the original chromium residue of the present embodiment has a hexavalent chromium concentration of 752 mg/L, and the treated residue has a hexavalent chromium concentration of 0.850 mg/L.
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Abstract
Description
本发明属于铬渣处理技术领域,具体涉及一种氯化焙烧联合水热矿化处理铬渣的方法。The invention belongs to the technical field of chromium slag treatment, and particularly relates to a method for treating chromium residue by chlorination roasting combined with hydrothermal mineralization.
铬污染主要来源于铬盐生产和使用行业,以含铬废渣的污染为主。铬盐生产过程中所使用的有钙焙烧和无钙焙烧工艺均会产生含铬废渣。其中有钙焙烧工艺每生成1吨产品就将产生2-3吨的铬渣,无钙焙烧虽然显著降低了铬渣排放量及其中的六价铬含量,但风险依然存在。鉴于此,为了摆脱铬渣污染的困扰,一些发达国家不断压缩铬盐生产能力,改为从发展中国家进口铬盐产品。目前中国已经成为铬盐的生产和使用大国,产量及消费量居世界第一,也是铬渣产生量及堆储量最多的国家。因此,既能将铬渣解毒又能回收铬资源的处理思路,已经成为了处理铬渣的重要思路。The chromium pollution is mainly derived from the chromium salt production and use industry, and is mainly based on the pollution of chromium-containing waste residue. Calcium roasting and calcium-free roasting processes used in the production of chromium salts produce chromium-containing waste residues. Among them, the calcium roasting process will produce 2-3 tons of chromium slag per ton of product produced. Although calcium-free roasting significantly reduces the chromium slag emissions and the hexavalent chromium content, the risk remains. In view of this, in order to get rid of the pollution caused by chromium slag, some developed countries continue to compress chromium salt production capacity and import chromium salt products from developing countries. At present, China has become a large country in the production and use of chromium salts, with the world's largest output and consumption, and the country with the largest amount of chromium slag production and reserves. Therefore, the treatment idea of detoxifying and recovering chromium resources has become an important idea for treating chromium slag.
铬渣无害化主要是对铬渣进行原位还原/固定以降低其毒性,铬仍然在渣中。我们知道,即使是低毒的三价铬,在环境中的大量存在,也会带来土壤中铬富集以及进入人类食物链,长期将危害人类健康。况且脱毒后的铬渣中的三价铬仍有可能在环境中长期氧化条件下或者锰氧化菌的作用下被重新氧化成六价铬,具有二次毒性。因此,更理想的解决方式是将铬渣(或工业含铬固废)中的铬提取并回用到工业中——从根本上减少有毒有害物质,同时回收再利用稀有的战略金属资源。从这个意义上来说,将铬渣的无害化与资源化相结合,是铬渣治理研究的重要发展方向。The harmlessness of chromium slag is mainly the in-situ reduction/fixation of chromium slag to reduce its toxicity, and chromium is still in the slag. We know that even the low-toxic trivalent chromium, in the presence of a large amount of the environment, will lead to the enrichment of chromium in the soil and into the human food chain, which will endanger human health for a long time. Moreover, the trivalent chromium in the chromium residue after detoxification may still be reoxidized to hexavalent chromium under the action of long-term oxidation conditions in the environment or by the action of manganese oxidizing bacteria, and has secondary toxicity. Therefore, a more ideal solution is to extract and reuse chromium from chromium slag (or industrial chrome-containing solid waste) into the industry – radically reducing toxic and hazardous substances while recycling and recycling rare strategic metal resources. In this sense, the combination of harmlessness and resource utilization of chromium slag is an important development direction of chromium slag treatment research.
氯化焙烧法主要用于金属冶金行业,氯元素化学性质活泼,具有广泛的应 用范围,在一定条件下较容易和大多数金属或该金属氧化物等化合物发生反应生成金属氯化物,相较于其他该金属化合物(如氧化物、硫化物等),金属氯化物具有易溶于水、乙醇等溶剂、相对熔点低、易于挥发等特点,且对于不同金属来说,其氧化难易程度不同且所生成的金属氛化的物化性质存在明显不同。氯化焙烧法即是在焙烧过程中通过使用氯气、氯化氢、固体氯化盐等氯化剂使矿物原料中的目的金属组分转变成相应氯化物,根据上述金属氯化物特性,达到使目的金属组分分离、精炼的过程。根据金属氯化物性质,可采用高温氯化焙烧法使金属直接以气相或熔融相形式直接与脉石分离,亦可配合浸润法等其它提取方法,提纯精炼矿物原料。其次,氯化焙烧法相较于其他火法冶金方法操作温度低,节约能源;最后,氯化焙烧法有利于矿石综合利用,且金属分离效率高;根据对于不同金属氯化难易程度不同且所生成的金属氯化的物化性质存在明显不同,依此对于低品位组分复杂矿石、废料尾渣的综合利用,均可采用氯化焙烧方法有效分离富集金属,综合利用效果明显。但目前氯化焙烧方法主要用于工业冶金矿物原料中金属的分离富集,尚未有将氯化焙烧与水热矿化联合处理铬渣的报道。The chlorination roasting method is mainly used in the metallurgical industry. The chlorine element is chemically active and has a wide range of applications. Under certain conditions, it is easier to react with most metals or compounds such as metal oxides to form metal chlorides. Other metal compounds (such as oxides, sulfides, etc.), metal chlorides are easily soluble in water, ethanol and other solvents, relatively low melting point, easy to volatilize, etc., and for different metals, the degree of oxidation is different and There are significant differences in the physicochemical properties of the resulting metal-vaporized. The chlorination roasting method is to convert the target metal component in the mineral raw material into a corresponding chloride by using a chlorinating agent such as chlorine gas, hydrogen chloride or solid chloride salt in the roasting process, and to achieve the target metal according to the characteristics of the above metal chloride The process of component separation and refining. According to the nature of the metal chloride, the high-temperature chlorination roasting method can be used to directly separate the metal from the gangue in the form of a gas phase or a molten phase, and the refining mineral raw material can be purified by other extraction methods such as infiltration. Secondly, the chlorination roasting method has lower operating temperature than other pyrometallurgical methods and saves energy; finally, the chlorination roasting method is beneficial to the comprehensive utilization of ore, and the metal separation efficiency is high; according to the difficulty of chlorination for different metals, The physicochemical properties of the produced metal chlorides are significantly different. Therefore, for the comprehensive utilization of low-grade components complex ore and waste tailings, the chlorination roasting method can be used to effectively separate the enriched metals, and the comprehensive utilization effect is obvious. However, the current chlorination roasting method is mainly used for the separation and enrichment of metals in industrial metallurgical mineral raw materials. There has not been any report on the combined treatment of chlorination roasting with hydrothermal mineralization.
中国专利“循环再利用处理铬渣及废水工艺”(CN102699006A)考虑到了铬的回收和固体渣的再利用,在常温条件下先用酸将铬渣几乎完全溶解,然后分别加入不同的沉淀剂,将溶液中的混合离子沉淀和分离,但是这种方法需要消耗大量的酸和沉淀剂等化学试剂,而且工艺流程繁杂,处理成本较高。The Chinese patent "Recycling Process for Treatment of Chromium Slag and Wastewater" (CN102699006A) takes into account the recovery of chromium and the reuse of solid slag. Under normal temperature conditions, the chromium slag is almost completely dissolved with acid, and then different precipitants are added separately. The mixed ions in the solution are precipitated and separated, but this method requires a large amount of chemical reagents such as an acid and a precipitant, and the process is complicated and the treatment cost is high.
发明内容Summary of the invention
针对以上现有技术存在的缺点和不足之处,本发明的目的在于提供一种氯化焙烧联合水热矿化处理铬渣的方法。In view of the shortcomings and deficiencies of the above prior art, it is an object of the present invention to provide a method for chlorination roasting combined with hydrothermal mineralization to treat chromium slag.
本发明目的通过以下技术方案实现:The object of the invention is achieved by the following technical solutions:
一种氯化焙烧联合水热矿化处理铬渣的方法,包括如下步骤:A method for treating chrome slag by chlorination roasting combined with hydrothermal mineralization comprises the following steps:
(1)向铬渣中加入氯化盐混合均匀,然后升温至400~1000℃,进行高温焙 烧处理0.5~12h,冷却后研磨过筛;(1) adding chlorinated salt to the chromium slag and mixing uniformly, then heating to 400-1000 ° C, performing high-temperature baking treatment for 0.5 to 12 h, cooling and sieving;
(2)将步骤(1)过筛后的细粉加入到水热反应器中,加入矿化剂水溶液,在30~250℃温度下水热矿化反应2~24h;(2) adding the fine powder after the step (1) is added to the hydrothermal reactor, adding a mineralizer aqueous solution, hydrothermal mineralization reaction at a temperature of 30 to 250 ° C for 2 to 24 hours;
(3)步骤(2)所得混合液经冷却、静置,得到含铬上清液和固体渣,固体渣经水洗、干燥后得到脱毒后的铬渣,含铬上清液回用于生产或回收铬处理。(3) The mixed liquid obtained in the step (2) is cooled and allowed to stand to obtain a chromium-containing supernatant liquid and solid residue, and the solid residue is washed with water and dried to obtain detoxified chromium residue, and the chromium-containing supernatant is used for production. Or recycle chrome.
优选地,步骤(1)中所述氯化盐为氯化钠或氯化钙。Preferably, the chloride salt in step (1) is sodium chloride or calcium chloride.
优选地,所述铬渣与氯化盐加入的质量比为1:(0.5~1.5)。Preferably, the mass ratio of the chromium slag to the chloride salt is 1: (0.5 to 1.5).
优选地,步骤(2)中所述的矿化剂为碳酸钠和碳酸氢钠中的至少一种;矿化剂水溶液的浓度为0.5~1.5mol/L。Preferably, the mineralizer described in the step (2) is at least one of sodium carbonate and sodium hydrogencarbonate; and the concentration of the mineralizer aqueous solution is 0.5 to 1.5 mol/L.
优选地,步骤(2)中所述过筛后的细粉与矿化剂水溶液的固液比为1:(0.5~10)(w/w)。Preferably, the solid-liquid ratio of the sieved fine powder and the mineralizer aqueous solution in the step (2) is 1: (0.5 to 10) (w/w).
优选地,步骤(3)中所述回收铬处理的步骤为:加入还原剂将溶液六价铬还原为三价铬,再加入沉淀剂NaOH生产Cr(OH) 3沉淀回收。所述还原剂包括硫化钠、亚硫酸氢钠等。 Preferably, the step of recovering the chromium treatment in the step (3) is: adding a reducing agent to reduce the hexavalent chromium of the solution to trivalent chromium, and then adding a precipitating agent NaOH to produce a Cr(OH) 3 precipitate for recovery. The reducing agent includes sodium sulfide, sodium hydrogen sulfite, and the like.
本发明的原理如下:The principle of the invention is as follows:
由于铬渣中成分和物相复杂,六价铬的浸出不仅包括表面游离态和吸附态六价铬的浸出,还包括固体颗粒内部包夹的可溶性六价铬的缓慢扩散和溶出。包裹导致传质阻力较大,包夹态六价铬在短时间内难以浸出。因此选择氯化焙烧法,在高温条件下可以与大部分金属或金属化合物包括铬反应生成对应氯化物,具有熔点较低的特点,能够在微观固体颗粒内部释放出来,达到金属物质包括铬元素与其他固相杂质分离的目的,提高铬分离、精炼效率,最终增加铬的再回收率。此外后续矿化剂水热处理令铬渣中少量三价铬被氧化成六价铬,以重铬酸根存在更容易进入到溶液中。Due to the complex composition and phase of the chromium slag, the leaching of hexavalent chromium includes not only the surface free state and the leaching of the adsorbed hexavalent chromium, but also the slow diffusion and dissolution of the soluble hexavalent chromium trapped inside the solid particles. The package leads to a large mass transfer resistance, and the hexavalent chromium in the sandwich state is difficult to leaching in a short time. Therefore, the chlorination roasting method can be selected to react with most metals or metal compounds including chromium at high temperature to form corresponding chlorides, which have the characteristics of lower melting point and can be released inside the microscopic solid particles to reach the metal materials including chromium and The purpose of separation of other solid phase impurities is to improve chromium separation and refining efficiency, and ultimately increase the recovery rate of chromium. In addition, the subsequent mineralizer hydrothermal treatment causes a small amount of trivalent chromium in the chromium slag to be oxidized to hexavalent chromium, and it is easier to enter the solution with the presence of dichromate.
本发明的方法具有如下优点及有益效果:The method of the invention has the following advantages and benefits:
本发明结合工业冶金中的氯化焙烧技术对铬渣进行处理,解决了铬渣中六价铬难以与内部固体颗粒(含铝硅酸盐、氧化铁等)分离的难题,提高了铬的 分离效率与回收效率。处理后的滤渣浸出六价铬的含量低于国家标准(HJ/T301-2007)一般工业固体废渣的限制,而且工艺简单,适用于大规模工业生产流程,处理量大,回收率高,脱毒效果好,具有较高的社会效益和经济效益。The invention combines the chlorination roasting technology in industrial metallurgy to treat the chromium slag, solves the problem that the hexavalent chromium in the chromium slag is difficult to separate from the internal solid particles (including aluminosilicate, iron oxide, etc.), and improves the separation of chromium. Efficiency and recycling efficiency. The treated slag leaching hexavalent chromium content is lower than the national standard (HJ/T301-2007) general industrial solid waste residue, and the process is simple, suitable for large-scale industrial production processes, large processing capacity, high recovery rate, detoxification The effect is good, with high social and economic benefits.
图1为本发明实施例中一种氯化焙烧联合水热矿化处理铬渣的流程示意图。1 is a schematic flow chart of a chlorination roasting combined with hydrothermal mineralization treatment of chromium slag according to an embodiment of the present invention.
下面结合实施例及附图对本发明作进一步详细的描述,但本发明的实施方式不限于此。The present invention will be further described in detail below with reference to the embodiments and drawings, but the embodiments of the present invention are not limited thereto.
实施例1Example 1
本实施例的一种氯化焙烧联合水热矿化处理铬渣的方法,具体流程示意图如图1所示。具体步骤如下:A method for chlorination roasting combined with hydrothermal mineralization to treat chromium slag according to the embodiment is shown in FIG. 1 . Specific steps are as follows:
(1)取5kg铬渣与2.5kg氯化钠混合均匀,然后放入高温焙烧炉中以400℃高温焙烧处理3h,停止加热,自然缓慢冷却至室温后研磨过筛处理;(1) 5 kg of chromium slag and 2.5 kg of sodium chloride are mixed uniformly, and then placed in a high-temperature roasting furnace for 400 h at 400 ° C for 3 h, the heating is stopped, and naturally cooled to room temperature and then ground and sieved;
(2)将步骤(1)过筛后的细粉加入到水热釜中,并根据固液比为1:5(w/w)加入1.0mol/L的碳酸钠溶液,充分搅拌后加热至120℃温度下水热矿化反应3h;(2) adding the fine powder after the step (1) to the hydrothermal kettle, and adding 1.0 mol/L sodium carbonate solution according to a solid-liquid ratio of 1:5 (w/w), stirring well and heating to Hydrothermal mineralization reaction at 120 ° C for 3 h;
(3)步骤(2)所得混合液经自然冷却至室温、静置12h,得到含铬上清液和固体渣,将固体渣与含铬上清液过滤分离,固体渣经水洗、脱水干燥后得到脱毒后的铬渣,含铬上清液回用到生产中,或者汇集于废水处理站,进行还原、回收、净化处理(加入还原剂(如硫化钠、亚硫酸氢钠),将溶液六价铬还原为三价铬,加入沉淀剂NaOH生产Cr(OH) 3沉淀回收,经处理后水可以达到国家排水标准)。整个过程中,水在系统中可以循环利用。 (3) The mixture obtained in the step (2) is naturally cooled to room temperature and allowed to stand for 12 hours to obtain a chromium-containing supernatant liquid and solid residue, and the solid residue is separated from the chromium-containing supernatant by filtration, and the solid residue is washed with water, dried and dried. After the detoxification of the chromium residue, the chromium-containing supernatant is reused in the production, or collected in a wastewater treatment station for reduction, recovery, purification treatment (adding a reducing agent (such as sodium sulfide, sodium hydrogen sulfite), the solution The hexavalent chromium is reduced to trivalent chromium, and the precipitated NaOH is added to produce Cr(OH) 3 precipitate for recovery. After treatment, the water can reach the national drainage standard). Water can be recycled in the system throughout the process.
本实施例的原始铬渣浸出六价铬浓度为740mg/L,处理后滤渣浸出六价铬浓度为0.975mg/L。The original chromium residue of the present embodiment has a hexavalent chromium concentration of 740 mg/L, and the treated residue has a hexavalent chromium concentration of 0.975 mg/L.
实施例2Example 2
本实施例的一种氯化焙烧联合水热矿化处理铬渣的方法,具体流程示意图如图1所示。具体步骤如下:A method for chlorination roasting combined with hydrothermal mineralization to treat chromium slag according to the embodiment is shown in FIG. 1 . Specific steps are as follows:
(1)取10kg铬渣与10kg氯化钠混合均匀,然后放入高温焙烧炉中以400℃高温焙烧处理6h,停止加热,自然缓慢冷却至室温后研磨过筛处理;(1) 10 kg of chromium slag and 10 kg of sodium chloride are mixed uniformly, and then placed in a high-temperature roasting furnace and calcined at 400 ° C for 6 h, the heating is stopped, and naturally cooled to room temperature and then ground and sieved;
(2)将步骤(1)过筛后的细粉加入到水热釜中,并根据固液比为1:5(w/w)加入1.5mol/L的碳酸钠溶液,充分搅拌后加热至150℃温度下水热矿化反应2h;(2) adding the fine powder after the step (1) to the hydrothermal kettle, and adding 1.5 mol/L sodium carbonate solution according to a solid-liquid ratio of 1:5 (w/w), stirring well and heating to Hydrothermal mineralization reaction at 150 ° C for 2 h;
(3)步骤(2)所得混合液经自然冷却至室温、静置0.5h,得到含铬上清液和固体渣,将固体渣与含铬上清液过滤分离,固体渣经水洗、脱水干燥后得到脱毒后的铬渣,含铬上清液回用到生产中,或者汇集于废水处理站,进行还原、回收、净化处理(加入还原剂(如硫化钠、亚硫酸氢钠),将溶液六价铬还原为三价铬,加入沉淀剂NaOH生产Cr(OH) 3沉淀回收,经处理后水可以达到国家排水标准)。整个过程中,水在系统中可以循环利用。 (3) The mixture obtained in the step (2) is naturally cooled to room temperature and allowed to stand for 0.5 h to obtain a chromium-containing supernatant liquid and solid residue, and the solid residue is separated from the chromium-containing supernatant by filtration, and the solid residue is washed with water and dried. After detoxification of the chromium residue, the chromium-containing supernatant is reused in production, or collected in a wastewater treatment station for reduction, recovery, and purification treatment (adding a reducing agent (such as sodium sulfide, sodium hydrogen sulfite), The solution of hexavalent chromium is reduced to trivalent chromium, and the precipitated NaOH is added to produce Cr(OH) 3 precipitate for recovery. After treatment, the water can reach the national drainage standard). Water can be recycled in the system throughout the process.
本实施例的原始铬渣浸出六价铬浓度为763mg/L,处理后滤渣浸出六价铬浓度为1.025mg/L。The original chromium residue of the present embodiment has a hexavalent chromium concentration of 763 mg/L, and the treated residue has a hexavalent chromium concentration of 1.025 mg/L.
实施例3Example 3
本实施例的一种氯化焙烧联合水热矿化处理铬渣的方法,具体流程示意图如图1所示。具体步骤如下:A method for chlorination roasting combined with hydrothermal mineralization to treat chromium slag according to the embodiment is shown in FIG. 1 . Specific steps are as follows:
(1)取10kg铬渣与15kg氯化钠混合均匀,然后放入高温焙烧炉中以800℃高温焙烧处理1.5h,停止加热,自然缓慢冷却至室温后研磨过筛处理;(1) 10 kg of chromium slag and 15 kg of sodium chloride are mixed uniformly, and then placed in a high-temperature roasting furnace at 800 ° C high temperature roasting for 1.5 h, the heating is stopped, naturally cooled to room temperature and then ground and sieved;
(2)将步骤(1)过筛后的细粉加入到水热釜中,并根据固液比为1:10(w/w)加入1.0mol/L的碳酸钠溶液,充分搅拌后加热至180℃温度下水热矿化反应12h;(2) adding the fine powder after the step (1) to the hydrothermal kettle, and adding 1.0 mol/L sodium carbonate solution according to a solid-liquid ratio of 1:10 (w/w), stirring well and heating to Hydrothermal mineralization reaction at 180 ° C for 12 h;
(3)步骤(2)所得混合液经自然冷却至室温、静置0.5h,得到含铬上清液和固体渣,将固体渣与含铬上清液过滤分离,固体渣经水洗、脱水干燥后得到脱毒后的铬渣,含铬上清液回用到生产中,或者汇集于废水处理站,进行还 原、回收、净化处理(加入还原剂(如硫化钠、亚硫酸氢钠),将溶液六价铬还原为三价铬,加入沉淀剂NaOH生产Cr(OH) 3沉淀回收,经处理后水可以达到国家排水标准)。整个过程中,水在系统中可以循环利用。 (3) The mixture obtained in the step (2) is naturally cooled to room temperature and allowed to stand for 0.5 h to obtain a chromium-containing supernatant liquid and solid residue, and the solid residue is separated from the chromium-containing supernatant by filtration, and the solid residue is washed with water and dried. After detoxification of the chromium residue, the chromium-containing supernatant is reused in production, or collected in a wastewater treatment station for reduction, recovery, and purification treatment (adding a reducing agent (such as sodium sulfide, sodium hydrogen sulfite), The solution of hexavalent chromium is reduced to trivalent chromium, and the precipitated NaOH is added to produce Cr(OH) 3 precipitate for recovery. After treatment, the water can reach the national drainage standard). Water can be recycled in the system throughout the process.
本实施例的原始铬渣浸出六价铬浓度为752mg/L,处理后滤渣浸出六价铬浓度为0.850mg/L。The original chromium residue of the present embodiment has a hexavalent chromium concentration of 752 mg/L, and the treated residue has a hexavalent chromium concentration of 0.850 mg/L.
上述实施例为本发明较佳的实施方式,但本发明的实施方式并不受上述实施例的限制,其它的任何未背离本发明的精神实质与原理下所作的改变、修饰、替代、组合、简化,均应为等效的置换方式,都包含在本发明的保护范围之内。The above embodiments are preferred embodiments of the present invention, but the embodiments of the present invention are not limited to the above embodiments, and any other changes, modifications, substitutions, combinations, and modifications may be made without departing from the spirit and scope of the invention. Simplifications should all be equivalent replacements and are included in the scope of the present invention.
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| CN109554536A (en) * | 2018-11-23 | 2019-04-02 | 华南理工大学 | A kind of device and method of vacuum chloridising roasting processing heavy metal dangerous waste |
| CN109280777A (en) * | 2018-11-29 | 2019-01-29 | 华南理工大学 | Method for selectively recovering heavy metals in electroplating sludge by chlorination roasting method |
| CN109593964A (en) * | 2018-11-29 | 2019-04-09 | 华南理工大学 | The device and method of variable valency metal in dangerous solid waste is recycled in low-temperature reduction chlorination |
| CN109762991B (en) * | 2019-01-22 | 2019-11-29 | 福州大学 | A kind of chromium containing electroplating Heavy Metals in Sludge Selective Separation recovery process |
| CN112853112A (en) * | 2021-01-09 | 2021-05-28 | 中新国际联合研究院 | Method for realizing full recovery of chromium in chromium slag |
| CN113620318B (en) * | 2021-07-31 | 2022-10-25 | 华南理工大学 | Method for treating chromium-containing mirabilite waste salt by chlorination process |
| CN118122758A (en) * | 2024-04-22 | 2024-06-04 | 西安建筑科技大学 | A method for enhancing the stability of chromium slag under light environment |
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