CN102976467A - Treating method of electroplating wastewater - Google Patents
Treating method of electroplating wastewater Download PDFInfo
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Abstract
本发明公开一种环境污染控制领域中电镀废水的处理方法,将电镀废水过滤去除固体颗粒,根据生产工艺分析其中可能存在的离子,添加金属阳离子或将多种电镀废水混合,使二价离子浓度是三价离子浓度的2~4倍;向电镀废水中快速滴加50%~70%的NaOH溶液,直至pH值至8~10为止,滴加时在300~400rpm下快速搅拌60~120分钟,金属离子通过共沉淀作用生成水滑石;将生成的水滑石沉淀分离,加入盐酸或硫酸,调节pH至7;利用电镀废水中的金属离子,通过简单的步骤,制备具有广泛应用范围的水滑石,实现废物利用,同时能去除电镀废水中的重金属,合成得到的水滑石可以作为吸附材料,继续用于环境治理。The invention discloses a method for treating electroplating wastewater in the field of environmental pollution control. The electroplating wastewater is filtered to remove solid particles, the ions that may exist therein are analyzed according to the production process, metal cations are added or various electroplating wastewater are mixed to make the concentration of divalent ions It is 2~4 times of the concentration of trivalent ions; quickly add 50%~70% NaOH solution dropwise to the electroplating wastewater until the pH value reaches 8~10, and stir rapidly at 300~400rpm for 60~120 minutes during the dropwise addition , metal ions generate hydrotalcite through co-precipitation; precipitate and separate the generated hydrotalcite, add hydrochloric acid or sulfuric acid, and adjust the pH to 7; use metal ions in electroplating wastewater to prepare hydrotalcite with a wide range of applications through simple steps , realize waste utilization, and can remove heavy metals in electroplating wastewater, and the synthesized hydrotalcite can be used as an adsorption material and continue to be used for environmental governance.
Description
技术领域 technical field
本发明涉及环境污染控制新技术的开发,尤其涉及一种电镀废水的处理方法。 The invention relates to the development of new technologies for environmental pollution control, in particular to a treatment method for electroplating wastewater.
背景技术 Background technique
电镀工厂(或车间)排出的废水和废液,如镀件漂洗水、废槽液、设备冷却水和冲洗地面水等,其水质因生产工艺而异,往往含油多种金属离子,一般来说,常含有Cr6+、Cd2+、Ni2+、Cu2+、Zn2+、Fe2+等重金属;电镀废水多有毒,危害较大。如氰可引起人畜急性中毒,致死,低浓度长期作用也能造成慢性中毒。镉可使肾脏发生病变,并会引起痛痛病。六价铬可引起肺癌、肠胃道疾病和贫血,并会在骨、脾和肝脏内蓄积。因此,电镀废水必须严格控制,妥善处理。 Wastewater and waste liquid discharged from electroplating factories (or workshops), such as rinsing water for plated parts, waste bath liquid, equipment cooling water and flushing ground water, etc., the water quality varies with the production process, and often contains oil and various metal ions. , often contain Cr 6+ , Cd 2+ , Ni 2+ , Cu 2+ , Zn 2+ , Fe 2+ and other heavy metals; electroplating wastewater is mostly toxic and harmful. For example, cyanide can cause acute poisoning of humans and animals and cause death, and long-term effects of low concentrations can also cause chronic poisoning. Cadmium can cause pathological changes in the kidneys and cause itai disease. Hexavalent chromium can cause lung cancer, gastrointestinal disorders, and anemia, and can accumulate in bones, spleen, and liver. Therefore, electroplating wastewater must be strictly controlled and properly disposed of.
电镀废水处理工艺很多:20世纪70年代流行树脂交换,80年代电解法、化学法与气浮等。电解法:能耗高,电耗和铁耗均高,对高浓度含铬废水产生污泥量太多,不适应,同时对含氰废水处理不理想,所以含氰废水还要用化学法。化学药剂和气浮法:采用化学药品氧化还原中和,用气浮上浮方法进行泥水分离,因电镀污泥比重大,并且废水中含有多种有机添加剂,实际使用时气浮分离不彻底,并且运行管理不便,到90年代末,气浮法应用越来越少。化学药剂和沉淀:该方法是最早应用的方法,经过30多年不同处理工艺实际使用比较后。目前又回到了最早,也是最有效的处理工艺上来,国外在电镀处理上也大多采用该方法,但实际固液分离运行时间长后,沉淀池会有污泥翻上来,出水难以保证稳定达标。近年开发的生物处理工艺:小水量单一镀种运行效果高,许多大工程使用很不稳定,因水质水量难以恒定,微生物对水温,品种,重金属离子的浓度,PH值的变化难稳定适应,出现瞬间大批微生物死亡,出现环境污染事故,而且培菌不易。 There are many electroplating wastewater treatment processes: resin exchange was popular in the 1970s, electrolysis, chemical methods and air flotation in the 1980s. Electrolysis method: high energy consumption, high power consumption and iron consumption, too much sludge generated for high-concentration chromium-containing wastewater, unsuitable, and unsatisfactory treatment of cyanide-containing wastewater, so cyanide-containing wastewater must use chemical methods. Chemical agents and air flotation method: use chemical redox neutralization, and use air flotation to separate mud and water. Due to the large proportion of electroplating sludge and various organic additives in wastewater, the air flotation separation is not complete in actual use, and the operation Management is inconvenient. By the end of the 1990s, the application of air flotation was less and less. Chemical agents and precipitation: This method is the earliest applied method, after more than 30 years of actual use and comparison of different treatment processes. At present, it has returned to the earliest and most effective treatment process. Most foreign countries also use this method in electroplating treatment. However, after a long time of actual solid-liquid separation operation, sludge will turn up in the sedimentation tank, and it is difficult to ensure that the effluent is stable and up to standard. The biological treatment process developed in recent years: a small amount of water with a single type of plating has a high operating effect, and many large projects are very unstable. Because the water quality and quantity are difficult to maintain, microorganisms are difficult to adapt to changes in water temperature, species, concentration of heavy metal ions, and pH value. A large number of microorganisms die instantly, environmental pollution accidents occur, and it is not easy to cultivate bacteria.
层状双羟基复合金属氧化物(Layered Double Hydroxides,简称LDH),又称水滑石,是一类重要的无机功能材料。其独特的层状结构及层板元素和层间阴离子的可调变性受到人们的广泛关注,经离子交换向层间引入新的客体阴离子可使层状结构和组成产生相应的变化,因而可以制备一大类具有特殊性质的功能材料。水滑石材料属于阴离子型层状化合物。层状化合物是指具有层状结构、层间离子具有可交换性的一类化合物,利用层状化合物主体在强极性分子作用下所具有的可插层性和层间离子的可交换性,将一些功能性客体物质引入层间空隙并将层板距离撑开从而形成层柱化合物。 Layered Double Hydroxides (LDH for short), also known as hydrotalcite, is an important class of inorganic functional materials. Its unique layered structure and the tunable variability of layer elements and interlayer anions have attracted widespread attention. The introduction of new guest anions into the layer through ion exchange can cause corresponding changes in the layered structure and composition, so it can be prepared A large class of functional materials with special properties. Hydrotalcite materials belong to anionic layered compounds. Layered compounds refer to a class of compounds with a layered structure and interlayer ions that are exchangeable. Utilizing the intercalation and exchangeability of layered compounds under the action of strong polar molecules, Some functional guest substances are introduced into the interlayer space and the distance between the layers is stretched to form layer pillar compounds.
水滑石化学结构通式为:[M2+ 1-xM3+x (OH)2]x+ [(An- )x/n·mH2O],其中M2+为Mg2+,Ni2+,Mn2+,Zn2+,Ca2+,Fe2+,Cu2+等二价金属阴离子;M3+为Al3+,Cr3+,Fe3+,Co3+等三价金属阴离子;An-为阴离子,如CO3 2-,NO3 -,Cl-,OH-,SO4 2-,PO4 3-,C6H4(COO)2 2-等无机和有机离子以及络合离子,当层间无机阴离子不同,水滑石的层间距不同,同时在水滑石吸附污染物之后,层间距也会增大,以容纳更多的污染物。 The general chemical structure formula of hydrotalcite is: [M 2+ 1-x M 3+ x (OH) 2 ] x+ [(A n- ) x/n mH 2 O], where M 2+ is Mg 2+ , Ni 2+ , Mn 2+ , Zn 2+ , Ca 2+ , Fe 2+ , Cu 2+ and other divalent metal anions; M 3+ is Al 3+ , Cr 3+ , Fe 3+ , Co 3+ and other trivalent metal anions Metal anions; An- is an anion, such as CO 3 2- , NO 3 - , Cl - , OH - , SO 4 2- , PO 4 3- , C 6 H 4 (COO) 2 2- and other inorganic and organic ions As well as complex ions, when the inorganic anions between layers are different, the interlayer spacing of hydrotalcite is different. At the same time, after hydrotalcite adsorbs pollutants, the interlayer spacing will also increase to accommodate more pollutants.
目前,水滑石类材料的合成方法主要有盐-碱法、盐-氧化物法和离子交换法,还衍生出诱导水解法、水热法、热处理重新水合法等。其中最常用的方法是共沉淀法,即在一定温度下用构成水滑石层的金属离子混合溶液在碱的作用下发生共沉淀来制备。该方法简单易操作,是常用的制备方法,该方法中需要利用一定量的二价金属离子和三价金属离子,从经济的角度来看增加了投入;从治理环境的角度来看合成的过程中增加了废水的产生,对环境治理提出了新的问题。 At present, the synthesis methods of hydrotalcite materials mainly include salt-alkali method, salt-oxide method and ion exchange method, and induced hydrolysis method, hydrothermal method, heat treatment and rehydration method are also derived. The most commonly used method is the co-precipitation method, which is prepared by co-precipitating the mixed solution of metal ions forming the hydrotalcite layer under the action of alkali at a certain temperature. The method is simple and easy to operate, and is a commonly used preparation method. In this method, a certain amount of divalent metal ions and trivalent metal ions need to be used, which increases the investment from an economic point of view; The production of waste water has been increased, and new problems have been raised for environmental governance.
发明内容 Contents of the invention
本发明的目的是为克服现有技术中处理电镀废水的不足,提供一种能耗低、无污染、效率高的电镀废水的处理方法。 The purpose of the present invention is to overcome the shortcomings of the prior art in the treatment of electroplating wastewater, and provide a treatment method for electroplating wastewater with low energy consumption, no pollution and high efficiency. the
本发明采用的技术方案是依次包括如下步骤: The technical scheme that the present invention adopts is to comprise the following steps successively:
1)将电镀废水过滤去除固体颗粒,根据生产工艺分析其中可能存在的离子,添加金属阳离子或将多种电镀废水混合,使二价离子浓度是三价离子浓度的2~4倍; 1) Filter the electroplating wastewater to remove solid particles, analyze the ions that may exist in it according to the production process, add metal cations or mix various electroplating wastewater, so that the concentration of divalent ions is 2 to 4 times that of trivalent ions;
2)向电镀废水中快速滴加50%~70% 的NaOH 溶液[B1] ,直至pH值至8~10为止,滴加时在300~400 rpm下快速搅拌60~120分钟,金属离子通过共沉淀作用生成水滑石; 2) Quickly add 50%~70% NaOH solution [B1] to the electroplating wastewater until the pH value reaches 8~10, and stir rapidly at 300~400 rpm for 60~120 minutes during the dropwise addition, and the metal ions pass through the total Precipitation produces hydrotalcite;
3)将生成的水滑石沉淀分离,加入盐酸或硫酸,调节pH至7。 3) Separate the generated hydrotalcite precipitate, add hydrochloric acid or sulfuric acid, and adjust the pH to 7.
本发明的优点是利用电镀废水中的金属离子,通过简单的步骤,制备具有广泛应用范围的水滑石,实现废物利用,同时去除电镀废水中的重金属,合成得到的水滑石可以作为吸附材料,继续用于环境治理。 The advantage of the present invention is that the metal ions in the electroplating wastewater are used to prepare hydrotalcites with a wide range of applications through simple steps, realize waste utilization, and remove heavy metals in the electroplating wastewater at the same time, and the synthesized hydrotalcites can be used as adsorption materials. for environmental governance.
具体实施方式 Detailed ways
将电镀废水过滤去除固体颗粒,根据生产工艺分析其中可能存在的离子,添加适当的金属阳离子,或将多种电镀废水混合,保证二价离子浓度是三价离子浓度的2~4倍,如果只有二价金属阳离子,则加入少量三价金属阳离子,如比较便宜的Al3+、Fe3+等;如果只有三价金属阳离子,则加入少量二价金属阳离子,如比较便宜的Mg2+、Fe2+等,如果已经有二价金属阳离子和三价金属阳离子,则考察一下浓度,确保二价离子浓度是三价离子浓度的2~4倍就可。 Filter the electroplating wastewater to remove solid particles, analyze the ions that may exist in it according to the production process, add appropriate metal cations, or mix various electroplating wastewater to ensure that the concentration of divalent ions is 2 to 4 times that of trivalent ions. If only For divalent metal cations, add a small amount of trivalent metal cations, such as relatively cheap Al 3+ , Fe 3+ , etc.; if there are only trivalent metal cations, add a small amount of divalent metal cations, such as relatively cheap Mg 2+ , Fe 2+ , etc. If there are already divalent metal cations and trivalent metal cations, check the concentration to ensure that the concentration of divalent ions is 2 to 4 times the concentration of trivalent ions.
向电镀废水中快速滴加50%~70% 的NaOH 溶液[B2] ,直至pH值至8~10为止,滴加时在300~400 rpm下快速搅拌60~120分钟,金属离子通过共沉淀作用,生成水滑石,将生成的水滑石沉淀分离,洗涤废水中的污染物会随着沉淀被去除,最后加入盐酸或硫酸,调节pH至7左右。 Quickly add 50%~70% NaOH solution [B2] to the electroplating wastewater until the pH value reaches 8~10. During the dropwise addition, stir rapidly at 300~400 rpm for 60~120 minutes, and the metal ions pass through coprecipitation , generate hydrotalcite, precipitate and separate the generated hydrotalcite, the pollutants in the washing wastewater will be removed with the precipitation, and finally add hydrochloric acid or sulfuric acid to adjust the pH to about 7.
以下进一步提供本发明的4个实施例: Further provide 4 embodiments of the present invention below:
实施例1Example 1
将电镀废水过滤去除固体颗粒,根据生产工艺分析,其中含有Ni2+和Cu2+,加入少量Al3+,使二价离子浓度是三价离子浓度的2倍;向电镀废水中快速滴加70% 的NaOH 溶液调节pH值至8,滴加时在400 rpm下快速搅拌120分钟,沉淀分离,洗涤废水中的污染物会随着沉淀被去除,最后加入盐酸或硫酸,调节pH至7左右。 Filter the electroplating wastewater to remove solid particles. According to the analysis of the production process, it contains Ni 2+ and Cu 2+ . Add a small amount of Al 3+ to make the concentration of divalent ions twice the concentration of trivalent ions; Adjust the pH value to 8 with 70% NaOH solution, stir rapidly at 400 rpm for 120 minutes during the dropwise addition, and precipitate and separate. .
测定处理后废水的水质,经分析电镀废水中金属离子Ni2+、Cu2+和Al3+,去除率分别为97.2%、98.1%、95.3%。 The water quality of the treated wastewater was measured. After analyzing the metal ions Ni 2+ , Cu 2+ and Al 3+ in the electroplating wastewater, the removal rates were 97.2%, 98.1%, and 95.3%, respectively.
实施例2Example 2
将电镀废水过滤去除固体颗粒,根据生产工艺分析,其中含有Fe3+和Al3+,加入少量Mg2+,使二价离子浓度是三价离子浓度的4倍;向电镀废水中快速滴加50%的NaOH 溶液调节pH值至10,滴加时在300 rpm下快速搅拌60分钟,沉淀分离,洗涤废水中的污染物会随着沉淀被去除,最后加入盐酸或硫酸,调节pH至7左右。 Filter the electroplating wastewater to remove solid particles. According to the analysis of the production process, it contains Fe 3+ and Al 3+ . Add a small amount of Mg 2+ to make the concentration of divalent ions 4 times that of trivalent ions; 50% NaOH solution to adjust the pH value to 10, stir rapidly at 300 rpm for 60 minutes when adding dropwise, precipitate and separate, the pollutants in the washing wastewater will be removed with the precipitation, and finally add hydrochloric acid or sulfuric acid to adjust the pH to about 7 .
测定处理后废水的水质,经分析电镀废水中金属离子Fe3+、Al3+和Mg2+,去除率分别为97.1%、98.5%、97.3%。 The water quality of the treated wastewater was measured. After analyzing the metal ions Fe 3+ , Al 3+ and Mg 2+ in the electroplating wastewater, the removal rates were 97.1%, 98.5% and 97.3%, respectively.
实施例3Example 3
将多种电镀废水混合,去除固体颗粒,根据生产工艺分析其中存在Ni2+、Cu2+、Fe3+和Al3+,且二价离子浓度是三价离子浓度的3倍,向电镀废水中快速滴加60% 的NaOH 溶液调节pH值至9,滴加时在300 rpm下快速搅拌80分钟,沉淀分离,洗涤废水中的污染物会随着沉淀被去除,最后加入盐酸或硫酸,调节pH至7左右。 Mix a variety of electroplating wastewater to remove solid particles, analyze the presence of Ni 2+ , Cu 2+ , Fe 3+ and Al 3+ according to the production process, and the concentration of divalent ions is three times that of trivalent ions. Quickly add 60% NaOH solution in the solution to adjust the pH value to 9, stir rapidly at 300 rpm for 80 minutes during the dropwise addition, precipitate and separate, and the pollutants in the washing wastewater will be removed along with the precipitation, and finally add hydrochloric acid or sulfuric acid to adjust pH to around 7.
测定处理后废水的水质,经分析电镀废水中金属离子Ni2+、Cu2+、Fe3+和Al3+,去除率分别为97.3%、96.9%、97.4%、97.1%。 The water quality of the treated wastewater was measured. After analyzing the metal ions Ni 2+ , Cu 2+ , Fe 3+ and Al 3+ in the electroplating wastewater, the removal rates were 97.3%, 96.9%, 97.4% and 97.1%, respectively.
将该水滑石粉末加入含25 mg/L酸性大红的染料废水中,每克水滑石对应的所处理的废水体积约为1 L,快速搅拌60分钟;反应产物在沉淀池停留30分钟,固液分离,紫外可见分光光度计测定上清液浓度,污染物去除率为98.7%。 Add the hydrotalcite powder into the dye wastewater containing 25 mg/L acid scarlet, the volume of treated wastewater corresponding to each gram of hydrotalcite is about 1 L, and stir rapidly for 60 minutes; the reaction product stays in the sedimentation tank for 30 minutes, and the solid-liquid After separation, the concentration of the supernatant was measured by an ultraviolet-visible spectrophotometer, and the removal rate of pollutants was 98.7%.
实施例4Example 4
将多种电镀废水混合,去除固体颗粒,根据生产工艺分析其中存在Ni2+、Cu2+、Zn2+和Al3+,且二价离子浓度是三价离子浓度的4倍,向电镀废水中快速滴加60% 的NaOH 溶液调节pH值至9,滴加时在300 rpm下快速搅拌120分钟,沉淀分离,洗涤废水中的污染物会随着沉淀被去除,最后加入盐酸或硫酸,调节pH至7左右。 Mix a variety of electroplating wastewater to remove solid particles, and analyze the presence of Ni 2+ , Cu 2+ , Zn 2+ and Al 3+ according to the production process, and the concentration of divalent ions is 4 times that of trivalent ions. Quickly add 60% NaOH solution in the solution to adjust the pH value to 9, stir rapidly at 300 rpm for 120 minutes during the dropwise addition, and precipitate and separate, the pollutants in the washing wastewater will be removed along with the precipitation, and finally add hydrochloric acid or sulfuric acid to adjust pH to around 7.
测定处理后废水的水质,经分析电镀废水中金属离子Ni2+、Cu2+、Zn2+和Al3+,去除率分别为97.6%、97.9%、98.2%、97.8%。 The water quality of the treated wastewater was measured. After analyzing the metal ions Ni 2+ , Cu 2+ , Zn 2+ and Al 3+ in the electroplating wastewater, the removal rates were 97.6%, 97.9%, 98.2% and 97.8%, respectively.
将该水滑石粉末加入含25 mg/L染料金橙II的废水中,每克水滑石对应的所处理的废水体积约为1 L,快速搅拌60分钟;反应产物在沉淀池停留30分钟,固液分离,紫外可见分光光度计测定上清液浓度,污染物去除率为98.3%。 Add the hydrotalcite powder into the waste water containing 25 mg/L dye Golden Orange II, the volume of the treated waste water per gram of hydrotalcite is about 1 L, stir rapidly for 60 minutes; the reaction product stays in the sedimentation tank for 30 minutes, solidifies The liquid was separated, and the concentration of the supernatant was measured by an ultraviolet-visible spectrophotometer. The removal rate of pollutants was 98.3%.
这里总体积不一定,根据水量、水的初始pH和金属离子的量,但最终pH在8~10即可。 The total volume here is not necessarily, according to the amount of water, the initial pH of the water and the amount of metal ions, but the final pH is 8~10.
这里总体积不一定,根据水量、水的初始pH和金属离子的量,但最终pH在8~10即可。 The total volume here is not necessarily, according to the amount of water, the initial pH of the water and the amount of metal ions, but the final pH is 8~10.
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Cited By (10)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103253754A (en) * | 2013-05-17 | 2013-08-21 | 上海大学 | Method for rapid treatment of electroplating wastewater containing cyanogen and zinc-nickel |
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Citations (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2004099391A (en) * | 2002-09-11 | 2004-04-02 | Mizusawa Ind Chem Ltd | Method for producing layered double hydroxide |
CN1631506A (en) * | 2004-11-26 | 2005-06-29 | 北京化工大学 | A layered adsorption functional material for hydrophobic organic matter and its preparation method |
CN101376537A (en) * | 2008-09-24 | 2009-03-04 | 上海大学 | Method for processing electroplating waste containing Ni2+, Zn2+ and Cr3+ |
CN101746735A (en) * | 2008-12-19 | 2010-06-23 | 中国科学院大连化学物理研究所 | Method for preparing hydrotalcite material |
WO2010105303A1 (en) * | 2009-03-20 | 2010-09-23 | Commonwealth Scientific And Industrial Research Organisation | Treatment or remediation of natural or waste water |
CN102179253A (en) * | 2011-03-10 | 2011-09-14 | 上海大学 | Method for preparing catalyst by using electrolysis waste water and electrolysis sludge |
CN102553625A (en) * | 2011-11-20 | 2012-07-11 | 湖州师范学院 | Preparation method of Mn(III)-containing hydrotalcite by oxidation and precipitation |
-
2012
- 2012-11-28 CN CN2012104916802A patent/CN102976467A/en active Pending
Patent Citations (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2004099391A (en) * | 2002-09-11 | 2004-04-02 | Mizusawa Ind Chem Ltd | Method for producing layered double hydroxide |
CN1631506A (en) * | 2004-11-26 | 2005-06-29 | 北京化工大学 | A layered adsorption functional material for hydrophobic organic matter and its preparation method |
CN101376537A (en) * | 2008-09-24 | 2009-03-04 | 上海大学 | Method for processing electroplating waste containing Ni2+, Zn2+ and Cr3+ |
CN101746735A (en) * | 2008-12-19 | 2010-06-23 | 中国科学院大连化学物理研究所 | Method for preparing hydrotalcite material |
WO2010105303A1 (en) * | 2009-03-20 | 2010-09-23 | Commonwealth Scientific And Industrial Research Organisation | Treatment or remediation of natural or waste water |
CN102179253A (en) * | 2011-03-10 | 2011-09-14 | 上海大学 | Method for preparing catalyst by using electrolysis waste water and electrolysis sludge |
CN102553625A (en) * | 2011-11-20 | 2012-07-11 | 湖州师范学院 | Preparation method of Mn(III)-containing hydrotalcite by oxidation and precipitation |
Cited By (13)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103253754B (en) * | 2013-05-17 | 2015-08-12 | 上海大学 | Fast processing is containing cyanogen and the method containing zinc-nickel electroplating wastewater |
CN103253754A (en) * | 2013-05-17 | 2013-08-21 | 上海大学 | Method for rapid treatment of electroplating wastewater containing cyanogen and zinc-nickel |
CN103276214A (en) * | 2013-05-30 | 2013-09-04 | 上海交通大学 | Method for preparing anticorrosive coating by using electroplating wastewater |
WO2015096536A1 (en) * | 2013-12-27 | 2015-07-02 | 中国科学院过程工程研究所 | Method for removing cyanide in wastewater by recycling electroplating sludge |
CN112573550A (en) * | 2020-11-24 | 2021-03-30 | 衢州学院 | Method for preparing magnesium-based flame retardant by utilizing Grignard wastewater |
CN114368821B (en) * | 2021-11-11 | 2024-07-09 | 西部矿业股份有限公司 | Preparation method and application of hyperstable mineralizer for treating heavy metal pollution |
CN114368821A (en) * | 2021-11-11 | 2022-04-19 | 西部矿业股份有限公司 | A kind of preparation method and application of ultra-stable mineralizer for treating heavy metal pollution |
CN114634258A (en) * | 2022-03-25 | 2022-06-17 | 合肥工业大学 | Treatment method of acid mine wastewater |
CN114920275B (en) * | 2022-06-17 | 2023-08-22 | 陕西科技大学 | Recycling recovery method for forming specific minerals by directional induction of heavy metals |
CN114920275A (en) * | 2022-06-17 | 2022-08-19 | 陕西科技大学 | Resource recycling method for forming specific minerals by directionally inducing heavy metals |
CN115716658A (en) * | 2022-08-23 | 2023-02-28 | 中冶赛迪工程技术股份有限公司 | Method for preparing magnesium-iron hydrotalcites by using metal ions in industrial wastewater |
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