CN105347635B - One kind extracts chromium and resource utilization method from leather industry chromium-bearing sludge - Google Patents

One kind extracts chromium and resource utilization method from leather industry chromium-bearing sludge Download PDF

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CN105347635B
CN105347635B CN201510724096.0A CN201510724096A CN105347635B CN 105347635 B CN105347635 B CN 105347635B CN 201510724096 A CN201510724096 A CN 201510724096A CN 105347635 B CN105347635 B CN 105347635B
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CN105347635A (en
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孙钰
罗建勋
马贺伟
丁晓良
易玉丹
田勇
陈佳艳
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Jiaxing University
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/12Treatment of sludge; Devices therefor by de-watering, drying or thickening
    • C02F11/121Treatment of sludge; Devices therefor by de-watering, drying or thickening by mechanical de-watering
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/12Treatment of sludge; Devices therefor by de-watering, drying or thickening
    • C02F11/14Treatment of sludge; Devices therefor by de-watering, drying or thickening with addition of chemical agents
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B34/00Obtaining refractory metals
    • C22B34/30Obtaining chromium, molybdenum or tungsten
    • C22B34/32Obtaining chromium
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    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/20Heavy metals or heavy metal compounds
    • C02F2101/22Chromium or chromium compounds, e.g. chromates
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    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
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    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/22Nature of the water, waste water, sewage or sludge to be treated from the processing of animals, e.g. poultry, fish, or parts thereof
    • C02F2103/24Nature of the water, waste water, sewage or sludge to be treated from the processing of animals, e.g. poultry, fish, or parts thereof from tanneries

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Abstract

本发明公开了一种从皮革工业含铬污泥中提取铬及资源化利用方法。在皮革行业中,铬鞣是重要的鞣制方法之一,基于裸皮及毛皮在铬鞣过程中铬鞣剂用量大、皮对铬鞣剂的吸收率低等原因,产生大量的含铬污泥。本发明首先测定含铬污泥中主要成分的含量,采用硫酸溶液酸解来提取铬,然后过滤并将滤液用氢氧化钠溶液调节至碱性,再用阴离子聚丙烯酰胺絮凝,接着压滤并酸化,随后用过硫酸铵和重铬酸钾组成的复合氧化剂消解,最后采用葡萄糖还原得到铬鞣剂。采用该铬鞣剂鞣制后的蓝湿革的质量、性能可与商品铬鞣剂的相媲美。本发明对铬污泥中铬的提取率可达90%以上,并将其制成铬鞣剂,变废为宝,减少了含铬污泥对环境的污染并节约了铬资源。The invention discloses a method for extracting chromium from chromium-containing sludge in the leather industry and utilizing it as a resource. In the leather industry, chrome tanning is one of the important tanning methods. Due to the large amount of chrome tanning agent used in the chrome tanning process of bare hides and furs, and the low absorption rate of chrome tanning agents by leather, a large amount of chrome-containing sludge is generated. . In the present invention, the content of the main components in the chromium-containing sludge is first measured, the chromium is extracted by acid hydrolysis with sulfuric acid solution, then filtered and the filtrate is adjusted to alkaline with sodium hydroxide solution, and then flocculated with anionic polyacrylamide, followed by pressure filtration and dehydration. Acidification, followed by digestion with a compound oxidant consisting of ammonium persulfate and potassium dichromate, and finally reduction with glucose to obtain chrome tanning agent. The quality and performance of the wet blue leather tanned by the chrome tanning agent are comparable to those of the commercial chrome tanning agent. The invention can extract more than 90% of the chromium in the chrome sludge, and make it into a chrome tanning agent, turn waste into wealth, reduce environmental pollution from chromium-containing sludge and save chromium resources.

Description

一种从皮革工业含铬污泥中提取铬及资源化利用方法A method for extracting chromium from leather industry chromium-containing sludge and resource utilization

技术领域technical field

本发明涉及皮革鞣剂领域,具体地说是一种从皮革工业含铬污泥中提取铬及资源化利用方法。The invention relates to the field of leather tanning agents, in particular to a method for extracting chromium from chromium-containing sludge in the leather industry and utilizing it as a resource.

背景技术Background technique

鞣制是皮革工业中的重要工序,是由皮转变为革的关键过程,鞣制方法及鞣制的程度直接影响着成品革的质量。而在各种鞣制方法中,铬鞣法由于其操作简便、鞣性优异及成革的综合性能优良等优点,故自其十九世纪中叶发明以来,一直在皮革工业中占据主导地位,成为应用最广泛的鞣制技术。但在铬鞣过程中,裸皮对铬的吸收率为60~70%,其余30%~40%的铬则残留于铬鞣废水中(霍小平,刘存海.铬鞣废水处理现状综述[J].西部皮革,2009,31(23):37-42.)。如果直接排放到环境中,则铬会在植物、污泥及水体生物中累积,具有一定的生态毒性(马宏瑞,黄宁选,张景飞等.泥炭对溶液中铬的吸附及其在制革废水处理中的应用[J].环境化学,2003,22(6):596-600.);同时铬是不可再生的资源,我国的铬矿资源尤其匮乏。因此铬鞣废水中铬的回收及有效利用,对于目前我国皮革工业的可持续的、健康的发展具有显著的现实意义。Tanning is an important process in the leather industry. It is a key process from leather to leather. The tanning method and degree of tanning directly affect the quality of finished leather. Among various tanning methods, the chrome tanning method has been occupying a leading position in the leather industry since its invention in the middle of the nineteenth century due to its advantages such as easy operation, excellent tanning properties, and excellent comprehensive performance of the finished leather. The widest range of tanning techniques. However, during the chrome tanning process, the absorption rate of chrome to bare hide is 60-70%, and the remaining 30%-40% of chromium is left in the chrome tanning wastewater (Huo Xiaoping, Liu Cunhai. A review of the current situation of chrome tanning wastewater treatment[J] . Western Leather, 2009, 31(23):37-42.). If it is directly discharged into the environment, chromium will accumulate in plants, sludge and water organisms, and has certain ecotoxicity (Ma Hongrui, Huang Ningxuan, Zhang Jingfei, etc. The adsorption of chromium in the solution by peat and its role in the treatment of tannery wastewater Application [J]. Environmental Chemistry, 2003, 22 (6): 596-600.); At the same time, chromium is a non-renewable resource, and my country's chromium ore resources are particularly scarce. Therefore, the recovery and effective utilization of chromium in chrome tanning wastewater has significant practical significance for the sustainable and healthy development of my country's leather industry.

多年来,国内外研究工作者对铬鞣废水中铬的回收利用技术进行了持续研究,这些技术可主要分为碱沉淀回收、焚烧氧化及直接循环利用三种方法,其中碱沉淀回收法因操作简便、成本低、效果好而得到普遍应用。该方法的原理是基于调节铬鞣废液pH至8~9时,溶液中的三价铬转化为氢氧化铬沉淀,然后通过压滤将沉淀物制成含铬污泥(含铬滤饼),实现了铬与水的分离。该过程中铬的回收率在99%以上,处理后的水溶液中铬含量容易达到排放标准要求,但含铬污泥的有效利用则成为制革企业面临的现实问题(董贵平,兰云军,鲍利红.皮革的绿色化工艺之路——铬鞣废弃物的回收利用[J].西部皮革,2006,28(4):12-17.)。For many years, researchers at home and abroad have conducted continuous research on the recycling technology of chromium in chrome tanning wastewater. These technologies can be mainly divided into three methods: alkali precipitation recovery, incineration oxidation and direct recycling. Simple, low cost, good effect and widely used. The principle of this method is based on adjusting the pH of the chrome tanning waste liquid to 8-9, the trivalent chromium in the solution is converted into chromium hydroxide and precipitated, and then the precipitate is made into chromium-containing sludge (chromium-containing filter cake) by pressure filtration , to achieve the separation of chromium and water. The recovery rate of chromium in this process is above 99%, and the chromium content in the treated aqueous solution can easily meet the discharge standard requirements, but the effective utilization of chromium-containing sludge has become a practical problem faced by tanning enterprises (Dong Guiping, Lan Yunjun, Bao Lihong . The road to green leather technology - recycling of chrome tanning waste [J]. West Leather, 2006,28(4):12-17.).

含铬污泥可通过再加工制备成铬鞣剂,用于制革生产过程,从而实现铬的循环利用,这也是目前含铬污泥的最佳利用途径(耿士锁,袁嗣兵.制革业铬回收及废水再用的试验研究[J].环境科学与技术,1994,67(4):8-10.王俊耀,苏海佳,谭天伟.制革厂铬鞣废水中铬的回收处理研究[J].环境工程学报,2007,1(1):23-26.)。但含铬污泥不同于常规铬鞣剂生产过程中所使用的纯度较高的红矾(重铬酸盐),因为含铬污泥成分因沉淀技术的不同而复杂多变。如沉淀用的碱可采用Ca(OH)2、NaOH或MgO,而且为提高沉淀效果,需要同时加入铁盐、铝盐或有机高分子絮凝剂(刘存海.复合絮凝剂的选配及其在处理铬鞣废水中的应用[J].中国皮革,2003,32(5):28-30.程宝箴,邹丹慧.铬鞣废水的处理及资源化利用[J].天津科技大学学报,2011,26(3):36-38.);另外,富铬泥中还含有油脂、皮纤维及蛋白等有机类物质(Boast DA.Large scale chrome recovery from chrome wash liquors[J].Journal of the American Leather Chemists Association,1988,83(1):17-24.MaiaRA.Clean technologies-targets already achieved and trends for the comingyears[J].Journal of the Society of Leather Technologists and Chemists,1998,82(3):111-113.Kanagaraj J,Chandra Babu NK,Mandal AB.Recovery and reuse ofchromium from chrome tanning waste water aiming towards zero discharge ofpollution [J].Journal of Cleaner Production,2008,16(16):1807-1813.)。因此,不同的碱沉淀技术产生的含铬污泥中无机及有机成分含量有较大差异,这将影响其资源化利用的效果。Chromium-containing sludge can be reprocessed into chrome tanning agent, which can be used in the leather production process to realize the recycling of chromium. This is also the best way to utilize chromium-containing sludge (Geng Shisuo, Yuan Sibing. Chromium recovery in leather industry and waste water reuse[J].Environmental Science and Technology,1994,67(4):8-10.Wang Junyao,Su Haijia,Tan Tianwei.Recovery and treatment of chromium in tannery chrome tanning wastewater[J].Environmental Engineering Journal, 2007, 1(1):23-26.). However, chromium-containing sludge is different from the high-purity red alum (dichromate) used in the production process of conventional chrome tanning agents, because the composition of chromium-containing sludge is complex and changeable due to different precipitation techniques. For example, the alkali used for precipitation can be Ca(OH) 2 , NaOH or MgO, and in order to improve the precipitation effect, it is necessary to add iron salt, aluminum salt or organic polymer flocculant at the same time (Liu Cunhai. Application in chrome tanning wastewater [J]. China Leather, 2003, 32(5): 28-30. Cheng Baozhen, Zou Danhui. Treatment and resource utilization of chrome tanning wastewater [J]. Journal of Tianjin University of Science and Technology, 2011, 26( 3):36-38.); In addition, chrome-rich mud also contains organic substances such as oil, leather fiber and protein (Boast DA. Large scale chrome recovery from chrome wash liquors[J].Journal of the American Leather Chemists Association ,1988,83(1):17-24.MaiaRA.Clean technologies-targets already achieved and trends for the comingyears[J].Journal of the Society of Leather Technologists and Chemists,1998,82(3):111-113. Kanagaraj J, Chandra Babu NK, Mandal AB. Recovery and reuse of chromium from chrome tanning waste water aiming towards zero discharge of pollution [J]. Journal of Cleaner Production, 2008,16(16):1807-1813.). Therefore, the content of inorganic and organic components in chromium-containing sludge produced by different alkali precipitation technologies is quite different, which will affect the effect of its resource utilization.

国内外在含铬污泥的处理方面均研究的较少。国外采用酶法水解含铬污泥中的胶原蛋白后,将剩余的铬用于颜料的生产。国内研究人员也对利用铬泥制备铬鞣剂进行了一定的研究与探索,先后采用不同的方法得到再生铬鞣剂(王坤余,潘志娟,周万键.铬泥配制含铬主鞣剂及其应用性能的探索[J].中国皮革,2002,31(19):13-15.刘娜,丁志文,刘诚,等.H2O2氧化铬泥制备铬鞣剂的研究[J].中国皮革,2012,41(1):16-20.程正平,丁志文,刘娜,等.利用铬污泥制备铬鞣剂的研究[J].皮革与化工,2012,29(1):11-14.)。由于技术不成熟及其它原因,故未得到工业化应用。At home and abroad, there is little research on the treatment of chromium-containing sludge. In foreign countries, after enzymatic hydrolysis of collagen in chromium-containing sludge, the remaining chromium is used for the production of pigments. Domestic researchers have also carried out some research and exploration on the preparation of chrome tanning agents by using chrome mud, and have adopted different methods to obtain regenerated chrome tanning agents (Wang Kunyu, Pan Zhijuan, Zhou Wanjian. The preparation of chromium-containing main tanning agents and their application properties by chrome mud Exploration [J]. China Leather, 2002,31(19):13-15. Liu Na, Ding Zhiwen, Liu Cheng, etc. Research on the preparation of chrome tanning agent from H 2 O 2 chromium oxide mud [J]. China Leather, 2012,41(1):16-20. Cheng Zhengping, Ding Zhiwen, Liu Na, etc. Preparation of chrome tanning agent from chrome sludge[J].Leather and Chemical Industry, 2012,29(1):11-14 .). Due to immature technology and other reasons, it has not been applied industrially.

因此,就目前含铬污泥的具体情况,需要对含铬泥的主要成分含量(总铬、总灰分)进行系统分析,建立统一成分含量指标,为其资源化利用奠定技术基础。同时研究可行的、循环利用的方法提取含铬污泥中的铬并资源化利用之。另外,也可对目前企业中的碱沉淀回收技术进行规范和统一,更好地促进区域皮革产业的持续与健康发展。Therefore, in view of the current specific situation of chromium-containing sludge, it is necessary to systematically analyze the main component content (total chromium, total ash) of chromium-containing sludge, establish a unified component content index, and lay a technical foundation for its resource utilization. At the same time, study the feasible and recycling method to extract the chromium in the chromium-containing sludge and utilize it as a resource. In addition, it can also standardize and unify the current alkali precipitation recovery technology in enterprises to better promote the sustainable and healthy development of the regional leather industry.

发明内容Contents of the invention

本发明针对上述问题,提供一种从皮革工业含铬污泥中提取铬及资源化利用方法,其通过对含铬污泥中相关指标的测定,分析含铬污泥的成分,实现铬的提取及资源化利用,变废为宝,减少铬对环境的污染。In view of the above problems, the present invention provides a method for extracting chromium from chromium-containing sludge in the leather industry and its resource utilization method, which realizes the extraction of chromium by measuring the relevant indicators in the chromium-containing sludge and analyzing the components of the chromium-containing sludge And resource utilization, turning waste into treasure, reducing the pollution of chromium to the environment.

为此,本发明采用如下的技术方案:一种从皮革工业含铬污泥中提取铬及资源化利用方法,其特征在于,首先测定含铬污泥中主要成分含量,并用29~31wt%的硫酸溶液酸解来提取铬,然后过滤并将滤液用氢氧化钠溶液调节至碱性,再用阴离子聚丙烯酰胺絮凝(PAM),接着压滤并酸化,随后用过硫酸铵和重铬酸钾组成的复合氧化剂消解,最后采用葡萄糖还原得到铬鞣剂。For this reason, the present invention adopts the following technical scheme: a method for extracting chromium from chromium-containing sludge in the leather industry and its resource utilization method, which is characterized in that, firstly, the content of main components in the chromium-containing sludge is measured, and 29-31wt% of Chromium is extracted by acidolysis with sulfuric acid solution, then filtered and the filtrate made alkaline with sodium hydroxide solution, flocculated with anionic polyacrylamide (PAM), followed by press filtration and acidified, followed by ammonium persulfate and potassium dichromate The composite oxidant is digested, and finally the chrome tanning agent is obtained by glucose reduction.

上述方法包括以下具体步骤:The above method includes the following specific steps:

1)含铬污泥相关指标的测试1) Testing of related indicators of chromium-containing sludge

含铬污泥的相关指标为水分含量、Cr2O3含量和灰分含量,分别采用烘箱法(国家标准法)、过氧化钠氧化及分光光度法和马弗炉灼烧法测试;The relevant indicators of chromium-containing sludge are moisture content, Cr 2 O 3 content and ash content, which are tested by oven method (national standard method), sodium peroxide oxidation and spectrophotometry and muffle furnace burning method;

2)酸解2) Acid hydrolysis

将390~530重量份含铬污泥投入反应釜中,所述含铬污泥的水分含量为48~62%、Cr2O3含量为18~26%、灰分含量为40~50%,在搅拌的同时分两次加入460~490重量份29~31wt%的硫酸溶液,在35~45℃下搅拌70~80min,冷却至室温,过滤;Put 390-530 parts by weight of chromium-containing sludge into the reaction kettle, the moisture content of the chromium-containing sludge is 48-62 %, the Cr2O3 content is 18-26%, and the ash content is 40-50%. While stirring, add 460-490 parts by weight of 29-31wt% sulfuric acid solution twice, stir at 35-45°C for 70-80min, cool to room temperature, and filter;

3)絮凝3) Flocculation

将500重量份步骤2)得到的滤液投入到反应釜中,加入200~240重量份29-31wt%的氢氧化钠溶液,在常温下搅拌70~80min,静置过夜,使pH值稳定在8~10;然后加入140~150重量份0.04-0.06wt%的阴离子聚丙烯酰胺,搅拌使其混合均匀,静置55~65min;Put 500 parts by weight of the filtrate obtained in step 2) into the reactor, add 200 to 240 parts by weight of 29-31 wt% sodium hydroxide solution, stir at room temperature for 70 to 80 minutes, and let stand overnight to stabilize the pH value at 8 ~10; then add 140~150 parts by weight of 0.04-0.06wt% anionic polyacrylamide, stir to make it evenly mixed, and let stand for 55~65min;

4)压滤并酸化4) Press filtration and acidification

将步骤3)得到的絮凝体在压滤机上压滤成铬饼,铬饼的水分含量控制在20~30%;取铬饼500重量份置入反应釜中,加入100~120重量份的硫酸溶液,硫酸溶液中硫酸与水的体积比为1:1,搅拌使铬饼溶解,使其pH为2~4;Filter the flocs obtained in step 3) into chromium cakes on a filter press, and control the moisture content of the chromium cakes at 20-30%; take 500 parts by weight of the chromium cakes and put them into a reaction kettle, and add 100-120 parts by weight of sulfuric acid solution, the volume ratio of sulfuric acid to water in the sulfuric acid solution is 1:1, stir to dissolve the chromium cake, and make the pH 2-4;

5)消解、还原5) Digestion and reduction

在盛有500份酸化后的铬液的反应釜中加入80~120重量份过硫酸铵、8~10重量份重铬酸钾,在温度为95~105℃下消解40~60min;然后降温至90~95℃,在搅拌过程中加入20~30重量份葡萄糖,反应25~35min,冷却;再用8~10重量份纯碱调碱度,得到pH为2~4、Cr2O3为8~12%、碱度为33~35%的铬鞣液。Add 80 to 120 parts by weight of ammonium persulfate and 8 to 10 parts by weight of potassium dichromate in a reactor containing 500 parts of acidified chromium solution, and digest it for 40 to 60 minutes at a temperature of 95 to 105° C.; then cool down to 90-95°C, add 20-30 parts by weight of glucose during the stirring process, react for 25-35 minutes, and cool down; then adjust the alkalinity with 8-10 parts by weight of soda ash to obtain a pH of 2-4 and a Cr 2 O 3 of 8- 12% chrome tanning liquor with an alkalinity of 33-35%.

本发明提取到pH为2~4、Cr2O3为12%、碱度为33~35%的铬鞣液,其鞣制后的蓝湿革的收缩温度可达100℃以上,外观为浅灰蓝色且粒纹清晰、自然,可与商品铬鞣剂鞣革效果相比拟。所得成革的抗张强度、撕裂强度、断裂伸长率、柔软度均达到相应的铬鞣革的部颁标准,适用于对猪、牛、羊皮鞣制成各种轻革的鞣制和复鞣。The present invention extracts the chrome tanning liquor with a pH of 2-4, a Cr2O3 of 12%, and an alkalinity of 33-35%. After tanning, the shrinkage temperature of the wet blue leather can reach above 100°C, and the appearance is light gray It is blue with clear and natural grain pattern, which can be compared with commercial chrome tanning agent tanning effect. The tensile strength, tear strength, elongation at break, and softness of the resulting leather all meet the corresponding ministerial standards for chrome tanned leather, and are suitable for tanning and retanning of various light leathers tanned from pig, cow, and sheepskin .

进一步,所述的过硫酸铵、重铬酸钾、葡萄糖和纯碱均为工业品。Further, described ammonium persulfate, potassium dichromate, glucose and soda ash are all industrial products.

进一步,阴离子聚丙烯酰胺的分子量优选为1800万。Furthermore, the molecular weight of anionic polyacrylamide is preferably 18 million.

进一步,所述的反应釜装有锚式或框式搅拌浆,搅拌转速控制在60~80rpm。Further, the reactor is equipped with an anchor type or a frame type stirring blade, and the stirring speed is controlled at 60-80 rpm.

本发明与现有技术相比,具有如下有益效果:Compared with the prior art, the present invention has the following beneficial effects:

1.适合于当前市场上需求的所有轻革铬鞣和铬复鞣的要求,成革的收缩温度、物理机械指标达到2005年执行的轻工部颁铬鞣革标准。1. It is suitable for all light leather chrome tanning and chrome retanning requirements in the current market. The shrinkage temperature and physical and mechanical indicators of the finished leather meet the chrome tanned leather standards issued by the Ministry of Light Industry in 2005.

2.采用该提取法,铬的提取率可达85~95%。2. With this extraction method, the extraction rate of chromium can reach 85-95%.

3.采用阴离子聚丙烯酰胺(PAM)絮凝剂对铬液进行了有效地浓缩。3. The chromium solution is effectively concentrated by using anionic polyacrylamide (PAM) flocculant.

4.采用过硫酸铵、重铬酸钾复合氧化剂消解了铬液中的有机物,也起到补充铬的效果。4. Ammonium persulfate and potassium dichromate composite oxidant are used to digest the organic matter in the chromium solution, which also has the effect of supplementing chromium.

5.本发明鞣制后的蓝湿革的收缩温度为100℃以上,呈浅灰蓝色且粒面平细,其状态和成革性能可与商品铬鞣剂的鞣革效果相媲美。5. The shrinkage temperature of the wet blue leather tanned by the present invention is above 100° C., it is light gray blue and has a flat and fine grain surface, and its state and leather-forming performance can be compared with the tanning effect of commercial chrome tanning agents.

具体实施方式Detailed ways

下面通过实施例对本发明进行具体的描述。有必要在此指出的是以下实施例只是用于对本发明进行进一步说明,不能理解为对本发明保护范围的限制,该领域的技术熟练人员可以根据上述发明的内容对本发明作出一些非本质的改进和调整。The present invention is specifically described below by way of examples. It is necessary to point out that the following examples are only used to further illustrate the present invention, and cannot be interpreted as limiting the protection scope of the present invention. Those skilled in the art can make some non-essential improvements and improvements to the present invention according to the content of the above-mentioned invention. Adjustment.

实施例1Example 1

1)含铬污泥相关指标的测试1) Testing of related indicators of chromium-containing sludge

含铬污泥的相关指标为水分含量、Cr2O3含量、灰分含量等,分别采用烘箱法(国家标准法)、过氧化钠氧化及分光光度法、马弗炉灼烧法测试。The relevant indicators of chromium-containing sludge are moisture content, Cr 2 O 3 content, ash content, etc., which are tested by oven method (national standard method), sodium peroxide oxidation and spectrophotometry, and muffle furnace burning method.

2)酸解2) Acid hydrolysis

将390份含铬污泥(水分含量为48%、Cr2O3含量为18%、灰分含量为40%)投入反应釜中,在搅拌的同时分两次缓慢加入460份30wt%的硫酸溶液,在温度为40℃下搅拌60min,冷却至室温,过滤。Put 390 parts of chromium-containing sludge (moisture content is 48%, Cr2O3 content is 18 %, ash content is 40%) into the reaction kettle, slowly add 460 parts of 30wt% sulfuric acid solution twice while stirring , stirred at 40°C for 60 min, cooled to room temperature, and filtered.

3)絮凝3) Flocculation

将500份滤液投入到反应釜中,缓慢加入200份30wt%的氢氧化钠溶液,在常温下搅拌60min,静置过夜,使pH值稳定在8。然后加入140份0.05wt%的阴离子聚丙烯酰胺,搅拌使其混合均匀,静置60min。Put 500 parts of the filtrate into the reactor, slowly add 200 parts of 30wt% sodium hydroxide solution, stir at room temperature for 60 min, and let stand overnight to stabilize the pH value at 8. Then add 140 parts of 0.05 wt% anionic polyacrylamide, stir to make it evenly mixed, and let stand for 60 minutes.

4)压滤并酸化4) Press filtration and acidification

将絮凝体在压滤机上压滤成铬饼(铬饼的水分含量为65%)。取铬饼500份置入反应釜中,加入100份为1:1(VH2SO4:V)的硫酸溶液,搅拌使其溶解,使其pH为2;The flocs are press-filtered on a filter press to form a chromium cake (the moisture content of the chromium cake is 65%). Get 500 parts of chrome cake and insert in the reactor, add 100 parts and be the sulfuric acid solution of 1:1 (V H SO : V water ), stir and make it dissolve, make its pH 2;

5)消解、还原5) Digestion and reduction

在盛有500份酸化后的铬液的反应釜中加入80份过硫酸铵、8份重铬酸钾,在温度为100℃下消解40min;然后降温至90℃,在搅拌过程中加入20份葡萄糖,反应30min,冷却;再用8份纯碱调碱度,得到pH为2、Cr2O3为8%、碱度为33%的铬鞣液。Add 80 parts of ammonium persulfate and 8 parts of potassium dichromate to the reaction kettle containing 500 parts of acidified chromium solution, digest at 100°C for 40 minutes; then cool down to 90°C, and add 20 parts of Glucose was reacted for 30 minutes and cooled; then 8 parts of soda ash was used to adjust the alkalinity to obtain a chrome tanning solution with a pH of 2 , a Cr2O3 of 8%, and an alkalinity of 33%.

实施例2Example 2

1)含铬污泥相关指标的测试1) Testing of related indicators of chromium-containing sludge

含铬污泥的相关指标为水分含量、Cr2O3含量、灰分含量等,分别采用烘箱法(国家标准法)、过氧化钠氧化及分光光度法、马弗炉灼烧法测试。The relevant indicators of chromium-containing sludge are moisture content, Cr 2 O 3 content, ash content, etc., which are tested by oven method (national standard method), sodium peroxide oxidation and spectrophotometry, and muffle furnace burning method.

2)酸解2) Acid hydrolysis

将530份含铬污泥(水分含量为62%、Cr2O3含量为26%、灰分含量为50%)投入反应釜中,在搅拌的同时分两次缓慢加入490份30wt%的硫酸溶液,在温度为40℃下搅拌60min,冷却至室温,过滤;Put 530 parts of chromium-containing sludge (moisture content is 62%, Cr2O3 content is 26 %, ash content is 50%) into the reaction kettle, slowly add 490 parts of 30wt% sulfuric acid solution twice while stirring , stirred at a temperature of 40°C for 60min, cooled to room temperature, and filtered;

3)絮凝3) Flocculation

将500份滤液投入到反应釜中,缓慢加入240份30wt%的氢氧化钠溶液,在常温下搅拌60min,静置过夜,使pH值稳定在10。然后加入150份0.05wt%的阴离子聚丙烯酰胺,搅拌使其混合均匀,静置60min。Put 500 parts of the filtrate into the reactor, slowly add 240 parts of 30wt% sodium hydroxide solution, stir at room temperature for 60 min, and let stand overnight to stabilize the pH value at 10. Then add 150 parts of 0.05 wt% anionic polyacrylamide, stir to make it evenly mixed, and let stand for 60 minutes.

4)压滤并酸化4) Press filtration and acidification

将絮凝体在压滤机上压滤成铬饼(铬饼的水分含量为72.5%)。取铬饼500份置入反应釜中,加入120份为1:1(VH2SO4:V)的硫酸溶液,搅拌使其溶解,使其pH为4。The flocs were press-filtered on a filter press to form a chromium cake (the moisture content of the chromium cake was 72.5%). Get 500 parts of chromium cakes and insert in the reactor, add 120 parts of sulfuric acid solution that is 1:1 (V H SO : V water ), stir to make it dissolve, make its pH 4.

5)消解、还原5) Digestion and reduction

在盛有500份酸化后的铬液的反应釜中加入120份过硫酸铵、10份重铬酸钾,在温度为100℃下消解60min;然后降温至95℃,在搅拌过程中加入30份葡萄糖,反应30min,冷却;再用10份纯碱调碱度,得到pH为4、Cr2O3为12%、碱度为35%的铬鞣液。Add 120 parts of ammonium persulfate and 10 parts of potassium dichromate to the reaction kettle containing 500 parts of acidified chromium solution, and digest at 100°C for 60 minutes; then cool down to 95°C, and add 30 parts of Glucose was reacted for 30 minutes and cooled; then 10 parts of soda ash was used to adjust the alkalinity to obtain a chrome tanning solution with a pH of 4 , a Cr2O3 of 12%, and an alkalinity of 35%.

实施例3Example 3

1)含铬污泥相关指标的测试1) Testing of related indicators of chromium-containing sludge

含铬污泥的相关指标为水分含量、Cr2O3含量、灰分含量等,分别采用烘箱法(国家标准法)、过氧化钠氧化及分光光度法、马弗炉灼烧法测试。The relevant indicators of chromium-containing sludge are moisture content, Cr 2 O 3 content, ash content, etc., which are tested by oven method (national standard method), sodium peroxide oxidation and spectrophotometry, and muffle furnace burning method.

2)酸解2) Acid hydrolysis

将460份含铬污泥(水分含量为55%、Cr2O3含量为22%、灰分含量为45%)投入反应釜中,在搅拌的同时分两次缓慢加入475份30wt%的硫酸溶液,在温度为40℃下搅拌60min,冷却至室温,过滤。Put 460 parts of chromium-containing sludge (moisture content is 55 %, Cr2O3 content is 22%, ash content is 45%) into the reaction kettle, and slowly add 475 parts of 30wt% sulfuric acid solution twice while stirring , stirred at 40°C for 60 min, cooled to room temperature, and filtered.

3)絮凝3) Flocculation

将500份滤液投入到反应釜中,缓慢加入220份30wt%的氢氧化钠溶液,在常温下搅拌60min,静置过夜,使pH值稳定在9。然后加入145份0.05wt%的阴离子聚丙烯酰胺,搅拌使其混合均匀,静置60min。Put 500 parts of the filtrate into the reactor, slowly add 220 parts of 30wt% sodium hydroxide solution, stir at room temperature for 60 min, and let stand overnight to stabilize the pH value at 9. Then add 145 parts of 0.05 wt% anionic polyacrylamide, stir to make it evenly mixed, and let it stand for 60 minutes.

4)压滤并酸化4) Press filtration and acidification

将絮凝体在压滤机上压滤成铬饼(铬饼的水分含量为80%)。取铬饼500份置入反应釜中,加入110份为1:1(VH2SO4:V)的硫酸溶液,搅拌使其溶解,使其pH为3。The flocs are press-filtered on a filter press to form a chromium cake (the moisture content of the chromium cake is 80%). Get 500 parts of chromium cakes and insert in the reactor, add 110 parts of sulfuric acid solution that is 1:1 (V H SO : V water ), stir to make it dissolve, make its pH 3.

5)消解、还原5) Digestion and reduction

在盛有500份酸化后的铬液的反应釜中加入100份过硫酸铵、9份重铬酸钾,在温度为100℃下消解50min;然后降温至92.5℃,在搅拌过程中加入25份葡萄糖,反应30min,冷却;再用9份纯碱调碱度,得到pH为3、Cr2O3为12%、碱度为34%的铬鞣液。Add 100 parts of ammonium persulfate and 9 parts of potassium dichromate into the reaction kettle containing 500 parts of acidified chromium solution, and digest at 100°C for 50 minutes; then cool down to 92.5°C, and add 25 parts of Glucose was reacted for 30 minutes and cooled; then 9 parts of soda ash was used to adjust the alkalinity to obtain a chrome tanning solution with a pH of 3 , a Cr2O3 of 12%, and an alkalinity of 34%.

Claims (4)

1.一种从皮革工业含铬污泥中提取铬及资源化利用方法,其特征在于,首先测定含铬污泥中主要成分含量,并用29~31wt%的硫酸溶液酸解来提取铬,然后过滤并将滤液用氢氧化钠溶液调节至碱性,再用阴离子聚丙烯酰胺絮凝,接着压滤并酸化,随后用过硫酸铵和重铬酸钾组成的复合氧化剂消解,最后采用葡萄糖还原得到铬鞣剂;1. A method for extracting chromium and resource utilization from leather industry chromium-containing sludge, characterized in that, at first measure the main component content in the chromium-containing sludge, and extract chromium with 29~31wt% sulfuric acid solution acidolysis, and then Filtrate and adjust the filtrate to alkaline with sodium hydroxide solution, then flocculate with anionic polyacrylamide, then press filter and acidify, then digest with a composite oxidant composed of ammonium persulfate and potassium dichromate, and finally use glucose to reduce to obtain chromium Tanning agent; 所述的方法包括以下具体步骤:Described method comprises the following specific steps: 1)含铬污泥相关指标的测试1) Testing of related indicators of chromium-containing sludge 含铬污泥的相关指标为水分含量、Cr2O3含量和灰分含量,分别采用烘箱法、过氧化钠氧化及分光光度法和马弗炉灼烧法测试;The relevant indicators of chromium-containing sludge are moisture content, Cr 2 O 3 content and ash content, which are tested by oven method, sodium peroxide oxidation and spectrophotometry method and muffle furnace burning method respectively; 2)酸解2) Acid hydrolysis 将390~530重量份含铬污泥投入反应釜中,所述含铬污泥的水分含量为48~62%、Cr2O3含量为18~26%、灰分含量为40~50%,在搅拌的同时分两次加入460~490重量份29~31wt%的硫酸溶液,在35~45℃下搅拌70~80min,冷却至室温,过滤;Put 390-530 parts by weight of chromium-containing sludge into the reaction kettle, the moisture content of the chromium-containing sludge is 48-62 %, the Cr2O3 content is 18-26%, and the ash content is 40-50%. While stirring, add 460-490 parts by weight of 29-31wt% sulfuric acid solution twice, stir at 35-45°C for 70-80min, cool to room temperature, and filter; 3)絮凝3) Flocculation 将500重量份步骤2)得到的滤液投入到反应釜中,加入200~240重量份29~31wt%的氢氧化钠溶液,在常温下搅拌70~80min,静置过夜,使pH值稳定在8~10;然后加入140~150重量份0.04~0.06wt%的阴离子聚丙烯酰胺,搅拌使其混合均匀,静置55~65min;Put 500 parts by weight of the filtrate obtained in step 2) into the reactor, add 200 to 240 parts by weight of 29 to 31 wt% sodium hydroxide solution, stir at room temperature for 70 to 80 minutes, and let stand overnight to stabilize the pH value at 8 ~10; then add 140~150 parts by weight of 0.04~0.06wt% anionic polyacrylamide, stir to make it evenly mixed, and let stand for 55~65min; 4)压滤并酸化4) Press filtration and acidification 将步骤3)得到的絮凝体在压滤机上压滤成铬饼,铬饼的水分含量控制在65~80%;取铬饼500重量份置入反应釜中,加入100~120重量份的硫酸溶液,硫酸溶液中硫酸与水的体积比为1:1,搅拌使铬饼溶解,使其pH为2~4;Filter the flocs obtained in step 3) into chromium cakes on a filter press, the moisture content of the chromium cakes is controlled at 65-80%; take 500 parts by weight of the chromium cakes and put them into the reactor, add 100-120 parts by weight of sulfuric acid solution, the volume ratio of sulfuric acid to water in the sulfuric acid solution is 1:1, stir to dissolve the chromium cake, and make the pH 2-4; 5)消解、还原5) Digestion and reduction 在盛有500份酸化后的铬液的反应釜中加入80~120重量份过硫酸铵、8~10重量份重铬酸钾,在温度为95~105℃下消解40~60min;然后降温至90~95℃,在搅拌过程中加入20~30重量份葡萄糖,反应25~35min,冷却;再用8~10重量份纯碱调碱度,得到pH为2~4、Cr2O3为8~12%、碱度为33~35%的铬鞣液。Add 80 to 120 parts by weight of ammonium persulfate and 8 to 10 parts by weight of potassium dichromate in a reactor containing 500 parts of acidified chromium solution, and digest it for 40 to 60 minutes at a temperature of 95 to 105° C.; then cool down to 90-95°C, add 20-30 parts by weight of glucose during the stirring process, react for 25-35 minutes, and cool down; then adjust the alkalinity with 8-10 parts by weight of soda ash to obtain a pH of 2-4 and a Cr 2 O 3 of 8- 12% chrome tanning liquor with an alkalinity of 33-35%. 2.如权利要求1所述的从皮革工业含铬污泥中提取铬及资源化利用方法,其特征在于,所述的过硫酸铵、重铬酸钾、葡萄糖和纯碱均为工业品。2. the method for extracting chromium and resource utilization from leather industry chromium-containing sludge as claimed in claim 1, is characterized in that, described ammonium persulfate, potassium dichromate, glucose and soda ash are all industrial products. 3.如权利要求1所述的从皮革工业含铬污泥中提取铬及资源化利用方法,其特征在于,阴离子聚丙烯酰胺的分子量为1800万。3. The method for extracting chromium and resource utilization from leather industry chromium-containing sludge as claimed in claim 1, wherein the molecular weight of the anionic polyacrylamide is 18 million. 4.如权利要求1所述的从皮革工业含铬污泥中提取铬及资源化利用方法,其特征在于,所述的反应釜装有锚式或框式搅拌浆,搅拌转速控制在60~80rpm。4. The method for extracting chromium and resource utilization from chromium-containing sludge in the leather industry as claimed in claim 1, wherein the reactor is equipped with an anchor type or frame type stirring paddle, and the stirring speed is controlled at 60 ~ 80rpm.
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Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2012146324A1 (en) * 2011-04-29 2012-11-01 Feralco Ab Method for treatment of sludge from water and wastewater treatment plants with chemical treatment
CN103555428A (en) * 2013-10-30 2014-02-05 南京求是化工工程有限公司 Method for extracting wool fat in wool-scouring wastewater sludge by extractive distillation
CN104558597A (en) * 2014-09-30 2015-04-29 南京新月材料科技有限公司 Preparation method of porous graphene/polyaniline composite
EP2870986A1 (en) * 2012-07-05 2015-05-13 Aisin Seiki Kabushiki Kaisha Alkali metal and/or alkali earth metal extraction method

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2012146324A1 (en) * 2011-04-29 2012-11-01 Feralco Ab Method for treatment of sludge from water and wastewater treatment plants with chemical treatment
EP2870986A1 (en) * 2012-07-05 2015-05-13 Aisin Seiki Kabushiki Kaisha Alkali metal and/or alkali earth metal extraction method
CN103555428A (en) * 2013-10-30 2014-02-05 南京求是化工工程有限公司 Method for extracting wool fat in wool-scouring wastewater sludge by extractive distillation
CN104558597A (en) * 2014-09-30 2015-04-29 南京新月材料科技有限公司 Preparation method of porous graphene/polyaniline composite

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
制革厂铬鞣废水中铬的回收处理研究;王俊耀等;《环境工程学报》;20070131;第1卷(第1期);第24页2结果与讨论 *
制革富铬泥中总铬及总灰分含量的测定;麻淑娟等;《中国皮革》;20140731;第43卷(第13期);第31页前言中栏第1行-第32页左栏第5行,第32页1试验部分 *

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