CN106119545B - A kind of cleaning detoxification treatment of chromium slag and the extracting method of chromium - Google Patents
A kind of cleaning detoxification treatment of chromium slag and the extracting method of chromium Download PDFInfo
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- 239000011651 chromium Substances 0.000 title claims abstract description 103
- VYZAMTAEIAYCRO-UHFFFAOYSA-N Chromium Chemical compound [Cr] VYZAMTAEIAYCRO-UHFFFAOYSA-N 0.000 title claims abstract description 99
- 229910052804 chromium Inorganic materials 0.000 title claims abstract description 93
- 239000002893 slag Substances 0.000 title claims abstract description 44
- 238000000034 method Methods 0.000 title claims abstract description 37
- 238000004140 cleaning Methods 0.000 title claims abstract description 17
- 238000001784 detoxification Methods 0.000 title claims abstract description 9
- MHAJPDPJQMAIIY-UHFFFAOYSA-N Hydrogen peroxide Chemical compound OO MHAJPDPJQMAIIY-UHFFFAOYSA-N 0.000 claims abstract description 38
- JOPOVCBBYLSVDA-UHFFFAOYSA-N chromium(6+) Chemical compound [Cr+6] JOPOVCBBYLSVDA-UHFFFAOYSA-N 0.000 claims abstract description 34
- 239000000243 solution Substances 0.000 claims abstract description 20
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 17
- 238000010438 heat treatment Methods 0.000 claims abstract description 13
- 239000007788 liquid Substances 0.000 claims abstract description 13
- 238000003756 stirring Methods 0.000 claims abstract description 9
- 239000000203 mixture Substances 0.000 claims abstract description 8
- 239000006228 supernatant Substances 0.000 claims abstract description 8
- 239000011259 mixed solution Substances 0.000 claims abstract description 7
- 239000007787 solid Substances 0.000 claims abstract description 7
- 238000001027 hydrothermal synthesis Methods 0.000 claims abstract description 5
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims description 9
- 238000011084 recovery Methods 0.000 claims description 8
- 239000003638 chemical reducing agent Substances 0.000 claims description 5
- 238000005406 washing Methods 0.000 claims description 5
- 238000001035 drying Methods 0.000 claims description 3
- 238000001556 precipitation Methods 0.000 claims description 3
- DWAQJAXMDSEUJJ-UHFFFAOYSA-M Sodium bisulfite Chemical compound [Na+].OS([O-])=O DWAQJAXMDSEUJJ-UHFFFAOYSA-M 0.000 claims description 2
- 239000003795 chemical substances by application Substances 0.000 claims description 2
- SOCTUWSJJQCPFX-UHFFFAOYSA-N dichromate(2-) Chemical compound [O-][Cr](=O)(=O)O[Cr]([O-])(=O)=O SOCTUWSJJQCPFX-UHFFFAOYSA-N 0.000 claims description 2
- 230000001376 precipitating effect Effects 0.000 claims description 2
- 235000010267 sodium hydrogen sulphite Nutrition 0.000 claims description 2
- 229910052979 sodium sulfide Inorganic materials 0.000 claims description 2
- GRVFOGOEDUUMBP-UHFFFAOYSA-N sodium sulfide (anhydrous) Chemical group [Na+].[Na+].[S-2] GRVFOGOEDUUMBP-UHFFFAOYSA-N 0.000 claims description 2
- 239000002699 waste material Substances 0.000 abstract description 12
- 238000004519 manufacturing process Methods 0.000 abstract description 7
- 150000001844 chromium Chemical class 0.000 abstract description 6
- 230000000694 effects Effects 0.000 abstract description 4
- 238000004064 recycling Methods 0.000 abstract description 3
- 238000010335 hydrothermal treatment Methods 0.000 description 3
- 239000003973 paint Substances 0.000 description 3
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 2
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 2
- 239000002253 acid Substances 0.000 description 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 2
- OSGAYBCDTDRGGQ-UHFFFAOYSA-L calcium sulfate Chemical compound [Ca+2].[O-]S([O-])(=O)=O OSGAYBCDTDRGGQ-UHFFFAOYSA-L 0.000 description 2
- 239000013078 crystal Substances 0.000 description 2
- 238000000605 extraction Methods 0.000 description 2
- 239000003337 fertilizer Substances 0.000 description 2
- 150000002500 ions Chemical class 0.000 description 2
- 239000001301 oxygen Substances 0.000 description 2
- 229910052760 oxygen Inorganic materials 0.000 description 2
- 239000002245 particle Substances 0.000 description 2
- 239000004033 plastic Substances 0.000 description 2
- 239000002244 precipitate Substances 0.000 description 2
- 239000005060 rubber Substances 0.000 description 2
- 239000010802 sludge Substances 0.000 description 2
- 239000004753 textile Substances 0.000 description 2
- 231100000331 toxic Toxicity 0.000 description 2
- 230000002588 toxic effect Effects 0.000 description 2
- 238000004065 wastewater treatment Methods 0.000 description 2
- 206010028980 Neoplasm Diseases 0.000 description 1
- 201000011510 cancer Diseases 0.000 description 1
- 239000003153 chemical reaction reagent Substances 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 230000018044 dehydration Effects 0.000 description 1
- 238000006297 dehydration reaction Methods 0.000 description 1
- 239000003673 groundwater Substances 0.000 description 1
- 230000007774 longterm Effects 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 239000000123 paper Substances 0.000 description 1
- 239000000575 pesticide Substances 0.000 description 1
- 239000000049 pigment Substances 0.000 description 1
- 238000004321 preservation Methods 0.000 description 1
- 239000000047 product Substances 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 238000006722 reduction reaction Methods 0.000 description 1
- 239000002689 soil Substances 0.000 description 1
- 239000002910 solid waste Substances 0.000 description 1
- 238000001179 sorption measurement Methods 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
Classifications
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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
- C22B34/00—Obtaining refractory metals
- C22B34/30—Obtaining chromium, molybdenum or tungsten
- C22B34/32—Obtaining chromium
-
- 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
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- Chemical & Material Sciences (AREA)
- Manufacturing & Machinery (AREA)
- Materials Engineering (AREA)
- Mechanical Engineering (AREA)
- Metallurgy (AREA)
- Organic Chemistry (AREA)
- Life Sciences & Earth Sciences (AREA)
- Environmental & Geological Engineering (AREA)
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Abstract
本发明公开了一种铬渣的清洁脱毒处理及铬的提取方法,属于铬渣的清洁处理及资源的循环再利用领域。该方法的具体步骤为:1)向含六价铬的废渣中加入水,混合均匀;2)向步骤1)所得溶液中加入双氧水,充分搅拌,得混合液;3)采用水热法或直接加热处理混合液;4)加热处理后,使固液混合物自然冷却至室温,静置;5)将固体渣与含铬上清液分离,并将滤渣用水洗涤再干燥;6)将含铬溶液回收并返回工段中,或者进行回收铬处理。本发明所采用的矿化剂绿色无污染,处理后的上层清液可以直接在铬盐生产或铬盐使用的工艺中回用,滤渣可进行综合利用。本方法工艺清洁简单、投资小、见效快、可回收六价铬,有效治理铬污染又不造成二次污染。The invention discloses a cleaning and detoxification treatment of chromium slag and a method for extracting chromium, belonging to the fields of cleaning treatment of chromium slag and recycling of resources. The specific steps of the method are: 1) add water to the waste residue containing hexavalent chromium, and mix evenly; 2) add hydrogen peroxide into the solution obtained in step 1), and stir thoroughly to obtain a mixed solution; 3) adopt the hydrothermal method or directly Heat the mixed solution; 4) After the heat treatment, let the solid-liquid mixture cool to room temperature naturally, and let it stand still; 5) Separate the solid residue from the chromium-containing supernatant, wash the filter residue with water and then dry it; 6) Dilute the chromium-containing solution Recycled and returned to the plant, or processed for recycled chrome. The mineralizer adopted in the invention is green and pollution-free, the treated supernatant can be directly reused in the process of chromium salt production or chromium salt use, and the filter residue can be comprehensively utilized. The method has the advantages of clean and simple process, small investment, quick effect, recyclable hexavalent chromium, and effectively controls chromium pollution without causing secondary pollution.
Description
技术领域technical field
本发明属于铬渣的清洁处理及资源的循环再利用领域,具体涉及了一种铬渣的清洁脱毒处理及铬提取的方法。The invention belongs to the field of cleaning treatment of chromium slag and recycling of resources, and in particular relates to a method for cleaning and detoxification treatment of chromium slag and chromium extraction.
背景技术Background technique
铬渣是指铬盐生产及应用行业中产生的含六价铬的废渣,六价铬毒性高、可致癌,被列为对人类危害最大的八大化学物质之一。我国铬盐产量及消费量高居世界第一,也是铬渣产生最多的国家,已经堆存了数百万吨的铬渣亟待处理,给土壤和地下水带来了严重污染。但是我国铬矿资源比较贫乏,目前探明的储量仅占世界总储量的0.825%,按可满足需求的程度看,属短缺资源。因此,既能将铬渣解毒,又能回收铬资源,已经成为了处理铬渣的理想思路。Chromium residue refers to the waste residue containing hexavalent chromium produced in the production and application of chromium salts. Hexavalent chromium is highly toxic and can cause cancer, and is listed as one of the eight most harmful chemicals to humans. my country's chromium salt production and consumption rank first in the world, and it is also the country that produces the most chromium slag. Millions of tons of chromium slag have been piled up to be treated urgently, which has brought serious pollution to soil and groundwater. However, my country's chromium ore resources are relatively poor, and the current proven reserves only account for 0.825% of the world's total reserves, which is a shortage of resources in terms of meeting the demand. Therefore, detoxification of chromium slag and recovery of chromium resources have become an ideal way to deal with chromium slag.
针对铬渣的处理,通常用的是解毒后再填埋的方法,其核心是将高溶解性、高毒的六价铬还原固定成低毒的三价铬。不仅铬资源得不到回收和利用,而且铬仍排放在环境中,随着自然环境长期作用下三价铬又会被氧化成六价铬,造成二次污染。较理想的方法是将铬渣中的铬从渣中提取分离,进行回收和再利用,在脱毒铬渣的同时回收铬资源。For the treatment of chromium slag, the method of detoxification and then landfill is usually used. The core is to reduce and fix the highly soluble and highly toxic hexavalent chromium into low-toxic trivalent chromium. Not only chromium resources cannot be recovered and utilized, but also chromium is still discharged in the environment. With the long-term action of the natural environment, trivalent chromium will be oxidized to hexavalent chromium, causing secondary pollution. The ideal method is to extract and separate the chromium in the chromium slag from the slag, recycle and reuse it, and recover chromium resources while detoxifying the chromium slag.
中国专利“一种从铬渣中回收六价铬资源的方法”(CN102191390A)采用常温下硫酸或盐酸浸出水溶性和酸溶性的六价铬,然后在浸出的六价铬的溶液中添加还原剂和沉淀剂回收铬,从铬渣中回收60% ~ 80%的六价铬。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。Chinese patent "A method for recovering hexavalent chromium resources from chromium slag" (CN102191390A) uses sulfuric acid or hydrochloric acid at room temperature to leach water-soluble and acid-soluble hexavalent chromium, and then adds a reducing agent to the leached hexavalent chromium solution and precipitant to recover chromium, and recover 60% to 80% of hexavalent chromium from chromium slag. The Chinese patent "Process for Recycling and Reusing Chromium Slag and Wastewater Treatment" (CN102699006A) takes into account the recovery of chromium and the reuse of slag. Under normal temperature conditions, the chromium slag is almost completely dissolved with acid, and then different precipitants are added respectively. The mixed ions in the solution are precipitated and separated, but this method needs to consume a large amount of chemical reagents such as acid and precipitant, and the process is complicated and the treatment cost is high.
因此,针对现有技术的不足,迫切需要一种实用、科学的铬渣处理方法,将六价铬充分提取并实现铬渣的解毒。Therefore, aiming at the deficiencies of the prior art, there is an urgent need for a practical and scientific chromium slag treatment method to fully extract the hexavalent chromium and realize the detoxification of the chromium slag.
发明内容Contents of the invention
本发明的目的是提供一种铬渣的清洁脱毒处理及铬的提取方法,该方法工艺清洁、简单、投资小、见效快、可以充分回收六价铬,解毒彻底,有效治理铬污染又不造成二次污染。采用该方法回收到的铬,可以重新回用到生产中或者用到其它用途之中,如涂料、颜料、造纸等,变废为宝。采用该方法得到的滤渣可用于橡胶、塑料、肥料、油漆、纺织、造纸等行业。The purpose of the present invention is to provide a cleaning and detoxification treatment of chromium slag and a method for extracting chromium. The method is clean, simple, small in investment, quick in effect, can fully recover hexavalent chromium, detoxify thoroughly, and effectively control chromium pollution without cause secondary pollution. The chromium recovered by this method can be reused in production or used in other purposes, such as paint, pigment, papermaking, etc., turning waste into treasure. The filter residue obtained by the method can be used in rubber, plastic, fertilizer, paint, textile, papermaking and other industries.
本发明的目的通过以下技术方案实现。The purpose of the present invention is achieved through the following technical solutions.
一种铬渣的清洁脱毒处理及铬的提取方法,步骤如下:A method for cleaning and detoxifying chromium slag and extracting chromium, the steps are as follows:
1)向含六价铬的废渣中加入水,混合均匀;1) Add water to the waste residue containing hexavalent chromium and mix well;
2)向步骤1)所得溶液中加入矿化剂,充分搅拌,得混合液;所述矿化剂为双氧水;2) Add a mineralizer to the solution obtained in step 1), and stir thoroughly to obtain a mixed solution; the mineralizer is hydrogen peroxide;
3)采用水热法或直接加热处理步骤2)所得混合液;3) The mixed solution obtained in step 2) is treated by hydrothermal method or direct heating;
4)将步骤3)所得固液混合物自然冷却至室温,静置;4) Cool the solid-liquid mixture obtained in step 3) to room temperature naturally, and let stand;
5)将固体渣与含铬上清液分离,并将滤渣用水洗涤再干燥;5) Separating the solid residue from the chromium-containing supernatant, washing the filter residue with water and drying;
6)将含铬溶液回收并返回工段中,或者进行回收铬处理。6) Recover the chromium-containing solution and return it to the workshop, or carry out chromium recovery treatment.
进一步地,步骤1)所述含六价铬的废渣中加入水后固液比(w/w)为1:0.5 ~ 1:10。Further, after adding water to the waste residue containing hexavalent chromium in step 1), the solid-to-liquid ratio (w/w) is 1:0.5-1:10.
进一步地,步骤2)所述双氧水在混合液中的浓度为0.1 mol/L ~ 5 mol/L。Further, the concentration of hydrogen peroxide in the mixed liquid in step 2) is 0.1 mol/L-5 mol/L.
进一步地,步骤3)所述水热法或直接加热的温度均控制在50℃ ~ 250℃。Further, the temperature of the hydrothermal method or direct heating in step 3) is controlled at 50°C-250°C.
进一步地,步骤3)中保温时间为2 ~ 10小时 。Further, the heat preservation time in step 3) is 2 to 10 hours.
进一步地,步骤4)所述静置的时间为0.5 ~ 48小时。Further, the standing time in step 4) is 0.5-48 hours.
进一步地,步骤6)所述回收铬处理具体步骤为:向含铬溶液中加入还原剂,将溶液中六价铬还原为三价铬,再加入沉淀剂NaOH生产Cr(OH)3沉淀,最后把Cr(OH)3沉淀煅烧成Cr2O3。Further, the specific steps of the recovery of chromium in step 6) are as follows: adding a reducing agent to the chromium-containing solution to reduce the hexavalent chromium in the solution to trivalent chromium, then adding the precipitant NaOH to produce Cr(OH) 3 precipitation, and finally The Cr(OH) 3 precipitate is calcined to Cr 2 O 3 .
一种铬渣的清洁脱毒处理及铬的提取方法,步骤如下:A method for cleaning and detoxifying chromium slag and extracting chromium, the steps are as follows:
(1)将含六价铬的废渣和水按固液比1:0.5 ~ 1:10(w/w)混合均匀后,加入双氧水使溶液中双氧水浓度为0.1 mol/L ~ 5 mol/L 。(1) After mixing the waste residue containing hexavalent chromium and water at a solid-to-liquid ratio of 1:0.5 ~ 1:10 (w/w), add hydrogen peroxide to make the concentration of hydrogen peroxide in the solution 0.1 mol/L ~ 5 mol/L.
(2)充分搅拌,使废渣和溶液充分混合。(2) Stir fully to fully mix the waste residue and the solution.
(3)设定温度为30℃~250℃,再搅拌或不搅拌下保温时间为2 ~ 10小时。(3) Set the temperature at 30°C to 250°C, and keep warm for 2 to 10 hours with or without stirring.
(4)停止加热,让其自然冷却,静置时间为0.5 ~ 48小时。(4) Stop heating, let it cool down naturally, and let it stand for 0.5 to 48 hours.
(5)水热处理或者加热处理结束后,废渣固体沉淀在底部,上层清液含浓度较高的六价铬。(5) After the hydrothermal treatment or heat treatment, the solid waste residue is deposited at the bottom, and the supernatant contains higher concentration of hexavalent chromium.
(6)将固体渣与含铬上清液过滤分离,并将固体渣渣进行洗涤、脱水和干燥。(6) Filtrating and separating the solid slag from the chromium-containing supernatant, washing, dehydrating and drying the solid slag.
(7)分离出的上层清液和洗涤滤渣的水可回用到生产中或者进行回收铬处理。(7) The separated supernatant and the water for washing the filter residue can be reused in production or processed for recovery of chromium.
本发明提供的一种铬渣的清洁脱毒处理及铬的提取方法原理如下:The cleaning and detoxification treatment of a kind of chromium slag provided by the invention and the extraction method principle of chromium are as follows:
本发明加入矿化剂(双氧水)在进行水热处理或加热处理时,弱碱性条件下铬渣中少量的三价铬被双氧水氧化为具有较高溶解度的重铬酸根更容易进入溶液中;同时加热条件下过量的双氧水会分解成水和氧气,在氧气分压下的水热作用下致使固体颗粒晶体生长、晶格完整,从而比表面积减小,吸附活性位点减少,实现六价铬从颗粒表面脱附并分离。The present invention adds mineralizer (hydrogen peroxide) when carrying out hydrothermal treatment or heat treatment, a small amount of trivalent chromium in the chromium slag is oxidized by hydrogen peroxide into dichromate with higher solubility under weakly alkaline conditions and is more likely to enter the solution; at the same time Under heating conditions, excess hydrogen peroxide will be decomposed into water and oxygen, and under the hydrothermal action of oxygen partial pressure, the solid particle crystal will grow and the crystal lattice will be complete, thereby reducing the specific surface area and reducing the active sites for adsorption, and realizing hexavalent chromium from The particle surface desorbs and separates.
2Cr3+ + 4H2O2 →Cr2O7 2- + H2O2Cr 3+ + 4H 2 O 2 →Cr 2 O 7 2- + H 2 O
2H2O2 →2H2O + O2↑2H 2 O 2 →2H 2 O + O 2 ↑
与现有技术相比,本发明具有如下优点与技术效果:Compared with the prior art, the present invention has the following advantages and technical effects:
本发明解决了铬渣处理难的问题,所采用的矿化剂绿色无污染,处理中不引入杂离子,废渣处理后的上层清液可以直接在铬盐生产或铬盐使用的工艺中回用,大大减少了企业成本。处理后的滤渣可进行综合利用。本方法工艺清洁简单、投资小见效快、可回收六价铬,有效治理铬污染又不造成二次污染。The invention solves the problem of difficult treatment of chromium slag, the adopted mineralizer is green and pollution-free, no miscellaneous ions are introduced in the treatment, and the supernatant liquid after waste slag treatment can be directly reused in the process of chromium salt production or chromium salt use , greatly reducing business costs. The treated filter residue can be used comprehensively. The method has the advantages of clean and simple process, small investment and quick effect, recyclable hexavalent chromium, and effectively controls chromium pollution without causing secondary pollution.
具体实施方式Detailed ways
以下结合具体实施例对本发明作进一步地说明,但本发明的实施方式不限于此。The present invention will be further described below in conjunction with specific examples, but the embodiments of the present invention are not limited thereto.
实施例1Example 1
1)取0.5 kg含六价铬的废渣放入水热釜中,再加入水使固液比(w/w)为1:1,充分搅拌,加入双氧水,使体系中的双氧水浓度为0.1mol/L,设定温度为130℃,保温6 h。1) Put 0.5 kg of waste residue containing hexavalent chromium into a hydrothermal kettle, then add water to make the solid-to-liquid ratio (w/w) 1:1, stir well, add hydrogen peroxide, and make the concentration of hydrogen peroxide in the system 0.1mol /L, set the temperature at 130°C, and keep warm for 6 h.
2)6 h后,停止加热,自然缓慢冷却至室温,静置24 h。2) After 6 h, stop heating, cool down to room temperature naturally, and let stand for 24 h.
3)静置结束后,倒出上层含六价铬的溶液。对水热处理后的渣进行离心洗涤脱水,将滤渣干燥,得白色或白色偏黄固体。3) After standing still, pour out the solution containing hexavalent chromium in the upper layer. Carry out centrifugal washing and dehydration to the residue after hydrothermal treatment, and dry the filter residue to obtain a white or white yellowish solid.
4)将含铬溶液回用到生产中,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)和沉淀剂(NaOH),将溶液六价铬还原为三价铬,并生成Cr(OH)3沉淀,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。4) Reuse the chromium-containing solution in production, or collect it in the wastewater treatment station for reduction, recovery, and purification treatment, add reducing agents (such as sodium sulfide, sodium bisulfite) and precipitating agent (NaOH), and distill the solution six The valent chromium is reduced to trivalent chromium, and Cr(OH) 3 precipitates are generated, and the treated water can meet the national drainage standard. Throughout the process, water can be recycled in the system.
5)最后产物分别是主要含CaSO4的渣和主要含Cr(OH)3的铬泥,硫酸钙渣可以作为原料用于到橡胶、塑料、肥料、农药、油漆、纺织、造纸等行业。铬泥可以煅烧成Cr2O3,实现铬的回收。5) The final products are slag mainly containing CaSO 4 and chromium sludge mainly containing Cr(OH) 3. Calcium sulfate slag can be used as raw material for rubber, plastic, fertilizer, pesticide, paint, textile, paper and other industries. Chromium sludge can be calcined into Cr 2 O 3 to realize the recovery of chromium.
本实施例的原始铬渣浸出六价铬浓度为272 mg/L,处理后滤渣浸出六价铬浓度为2.53 mg/L。The concentration of hexavalent chromium leached from the original chromium residue in this embodiment was 272 mg/L, and the concentration of hexavalent chromium leached from the filter residue after treatment was 2.53 mg/L.
实施例2Example 2
取1 kg含六价铬废渣放入水热釜中,再加入水使固液比(w/w)为1:0.5,充分搅拌,加入双氧水,使体系中的双氧水浓度为1 mol/L,设定温度为50℃,保温10 h,停止加热后静置48 h。其他工艺过程与实施例1相同。Take 1 kg of waste residue containing hexavalent chromium and put it into a hydrothermal kettle, then add water to make the solid-to-liquid ratio (w/w) 1:0.5, stir well, add hydrogen peroxide, and make the concentration of hydrogen peroxide in the system 1 mol/L, Set the temperature at 50 °C, keep it warm for 10 h, and let it stand for 48 h after stopping heating. Other technological process is identical with embodiment 1.
本实施例的原始铬渣浸出六价铬浓度为269 mg/L,处理后滤渣浸出六价铬浓度为2.12 mg/L。The concentration of hexavalent chromium leached from the original chromium residue in this example was 269 mg/L, and the concentration of hexavalent chromium leached from the filter residue after treatment was 2.12 mg/L.
实施例3Example 3
取1.5kg含六价铬废渣放入水热釜中,再加入水使固液比(w/w)为1:10,充分搅拌,加入双氧水,使体系中的双氧水浓度为3 mol/L,设定温度为200℃,保温2 h,停止加热后静置0.5 h。其他工艺过程与实施例1相同。Take 1.5kg of waste residue containing hexavalent chromium and put it into a hydrothermal kettle, then add water to make the solid-to-liquid ratio (w/w) 1:10, stir well, add hydrogen peroxide, so that the concentration of hydrogen peroxide in the system is 3 mol/L, Set the temperature at 200 °C, keep it warm for 2 h, and let it stand for 0.5 h after stopping heating. Other technological process is identical with embodiment 1.
本实施例的原始铬渣浸出六价铬浓度为277 mg/L,处理后滤渣浸出六价铬浓度为1.92 mg/L。The concentration of hexavalent chromium leached from the original chromium residue in this example was 277 mg/L, and the concentration of hexavalent chromium leached from the filter residue after treatment was 1.92 mg/L.
实施例4Example 4
取1吨含六价铬废渣放入水热釜中,再加入水使固液比(w/w)为1:5,充分搅拌,加入双氧水,使体系中的双氧水浓度为5 mol/L,设定温度为180℃,保温4 h,停止加热后静置12 h。其他工艺过程与实施例1相同。Take 1 ton of waste residue containing hexavalent chromium and put it into a hydrothermal kettle, then add water to make the solid-to-liquid ratio (w/w) 1:5, stir well, add hydrogen peroxide, so that the concentration of hydrogen peroxide in the system is 5 mol/L, Set the temperature at 180 °C, keep it warm for 4 h, and let it stand for 12 h after stopping heating. Other technological process is identical with embodiment 1.
本实施例的原始铬渣浸出六价铬浓度为265 mg/L,处理后滤渣浸出六价铬浓度为1.43 mg/L。The concentration of hexavalent chromium leached from the original chromium residue in this embodiment was 265 mg/L, and the concentration of hexavalent chromium leached from the filter residue after treatment was 1.43 mg/L.
根据权利要求限定的保护范围和本说明书给出的技术解决方案,还能给出多个实施案例,都属于本发明保护范围。According to the scope of protection defined by the claims and the technical solutions provided in this specification, multiple implementation cases can also be given, all of which belong to the scope of protection of the present invention.
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