CN104478129B - A kind of method removing Trace Cadmium in the aqueous solution - Google Patents
A kind of method removing Trace Cadmium in the aqueous solution Download PDFInfo
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- BDOSMKKIYDKNTQ-UHFFFAOYSA-N cadmium atom Chemical compound [Cd] BDOSMKKIYDKNTQ-UHFFFAOYSA-N 0.000 title claims abstract description 62
- 229910052793 cadmium Inorganic materials 0.000 title claims abstract description 60
- 238000000034 method Methods 0.000 title claims abstract description 28
- 239000007864 aqueous solution Substances 0.000 title claims abstract description 19
- 239000000243 solution Substances 0.000 claims abstract description 70
- KJFMBFZCATUALV-UHFFFAOYSA-N phenolphthalein Chemical compound C1=CC(O)=CC=C1C1(C=2C=CC(O)=CC=2)C2=CC=CC=C2C(=O)O1 KJFMBFZCATUALV-UHFFFAOYSA-N 0.000 claims abstract description 20
- LDKDGDIWEUUXSH-UHFFFAOYSA-N Thymophthalein Chemical compound C1=C(O)C(C(C)C)=CC(C2(C3=CC=CC=C3C(=O)O2)C=2C(=CC(O)=C(C(C)C)C=2)C)=C1C LDKDGDIWEUUXSH-UHFFFAOYSA-N 0.000 claims abstract description 9
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 8
- 238000004062 sedimentation Methods 0.000 claims abstract description 4
- 238000003756 stirring Methods 0.000 claims description 26
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 claims description 24
- 239000000701 coagulant Substances 0.000 claims description 12
- 229910052742 iron Inorganic materials 0.000 claims description 12
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 claims description 8
- 239000003651 drinking water Substances 0.000 claims description 8
- 235000020188 drinking water Nutrition 0.000 claims description 8
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 claims description 6
- 229910000029 sodium carbonate Inorganic materials 0.000 claims description 4
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 claims 2
- -1 pH value < 8 Substances 0.000 claims 1
- 238000005345 coagulation Methods 0.000 abstract description 14
- 230000015271 coagulation Effects 0.000 abstract description 14
- 238000001556 precipitation Methods 0.000 abstract description 12
- BVKZGUZCCUSVTD-UHFFFAOYSA-L Carbonate Chemical compound [O-]C([O-])=O BVKZGUZCCUSVTD-UHFFFAOYSA-L 0.000 abstract description 5
- 238000006243 chemical reaction Methods 0.000 abstract description 5
- 239000002253 acid Substances 0.000 abstract description 4
- 239000002351 wastewater Substances 0.000 abstract description 4
- 239000002696 acid base indicator Substances 0.000 abstract description 3
- 239000003513 alkali Substances 0.000 abstract description 3
- 229910000011 cadmium carbonate Inorganic materials 0.000 abstract description 3
- PLLZRTNVEXYBNA-UHFFFAOYSA-L cadmium hydroxide Chemical compound [OH-].[OH-].[Cd+2] PLLZRTNVEXYBNA-UHFFFAOYSA-L 0.000 abstract description 3
- GKDXQAKPHKQZSC-UHFFFAOYSA-L cadmium(2+);carbonate Chemical compound [Cd+2].[O-]C([O-])=O GKDXQAKPHKQZSC-UHFFFAOYSA-L 0.000 abstract description 3
- 239000002245 particle Substances 0.000 abstract description 3
- 238000012545 processing Methods 0.000 abstract description 3
- 230000009897 systematic effect Effects 0.000 abstract description 2
- 238000012360 testing method Methods 0.000 abstract description 2
- 230000001112 coagulating effect Effects 0.000 abstract 1
- ZBJWWKFMHOAPNS-UHFFFAOYSA-N loretin Chemical compound C1=CN=C2C(O)=C(I)C=C(S(O)(=O)=O)C2=C1 ZBJWWKFMHOAPNS-UHFFFAOYSA-N 0.000 abstract 1
- 229950010248 loretin Drugs 0.000 abstract 1
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 description 16
- 239000002244 precipitate Substances 0.000 description 13
- 239000003153 chemical reaction reagent Substances 0.000 description 12
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 9
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 6
- 229910021578 Iron(III) chloride Inorganic materials 0.000 description 6
- RBTARNINKXHZNM-UHFFFAOYSA-K iron trichloride Chemical compound Cl[Fe](Cl)Cl RBTARNINKXHZNM-UHFFFAOYSA-K 0.000 description 6
- 230000007613 environmental effect Effects 0.000 description 5
- 239000000126 substance Substances 0.000 description 5
- 239000002352 surface water Substances 0.000 description 5
- UIIMBOGNXHQVGW-UHFFFAOYSA-M Sodium bicarbonate Chemical compound [Na+].OC([O-])=O UIIMBOGNXHQVGW-UHFFFAOYSA-M 0.000 description 4
- 239000002699 waste material Substances 0.000 description 3
- 238000004065 wastewater treatment Methods 0.000 description 3
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 description 2
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 description 2
- 239000000920 calcium hydroxide Substances 0.000 description 2
- 229910001861 calcium hydroxide Inorganic materials 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 238000009713 electroplating Methods 0.000 description 2
- 230000007062 hydrolysis Effects 0.000 description 2
- 238000006460 hydrolysis reaction Methods 0.000 description 2
- XLYOFNOQVPJJNP-UHFFFAOYSA-M hydroxide Chemical compound [OH-] XLYOFNOQVPJJNP-UHFFFAOYSA-M 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 229910052751 metal Inorganic materials 0.000 description 2
- 239000002184 metal Substances 0.000 description 2
- 239000002994 raw material Substances 0.000 description 2
- 238000000926 separation method Methods 0.000 description 2
- 229910000030 sodium bicarbonate Inorganic materials 0.000 description 2
- 235000017557 sodium bicarbonate Nutrition 0.000 description 2
- 239000004753 textile Substances 0.000 description 2
- VYZAMTAEIAYCRO-UHFFFAOYSA-N Chromium Chemical compound [Cr] VYZAMTAEIAYCRO-UHFFFAOYSA-N 0.000 description 1
- 229910019142 PO4 Inorganic materials 0.000 description 1
- UCKMPCXJQFINFW-UHFFFAOYSA-N Sulphide Chemical compound [S-2] UCKMPCXJQFINFW-UHFFFAOYSA-N 0.000 description 1
- 238000010170 biological method Methods 0.000 description 1
- 150000004649 carbonic acid derivatives Chemical class 0.000 description 1
- 238000005119 centrifugation Methods 0.000 description 1
- 230000009920 chelation Effects 0.000 description 1
- 238000009388 chemical precipitation Methods 0.000 description 1
- 229910052804 chromium Inorganic materials 0.000 description 1
- 239000011651 chromium Substances 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 238000004090 dissolution Methods 0.000 description 1
- 238000004070 electrodeposition Methods 0.000 description 1
- 239000006260 foam Substances 0.000 description 1
- 238000005342 ion exchange Methods 0.000 description 1
- RUTXIHLAWFEWGM-UHFFFAOYSA-H iron(3+) sulfate Chemical compound [Fe+3].[Fe+3].[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O RUTXIHLAWFEWGM-UHFFFAOYSA-H 0.000 description 1
- 229910000360 iron(III) sulfate Inorganic materials 0.000 description 1
- 239000010985 leather Substances 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 239000012528 membrane Substances 0.000 description 1
- 238000005272 metallurgy Methods 0.000 description 1
- MEFBJEMVZONFCJ-UHFFFAOYSA-N molybdate Chemical compound [O-][Mo]([O-])(=O)=O MEFBJEMVZONFCJ-UHFFFAOYSA-N 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- NBIIXXVUZAFLBC-UHFFFAOYSA-K phosphate Chemical compound [O-]P([O-])([O-])=O NBIIXXVUZAFLBC-UHFFFAOYSA-K 0.000 description 1
- 239000010452 phosphate Substances 0.000 description 1
- 238000000053 physical method Methods 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 238000001179 sorption measurement Methods 0.000 description 1
Classifications
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F9/00—Multistage treatment of water, waste water or sewage
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/38—Treatment of water, waste water, or sewage by centrifugal separation
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/5236—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/66—Treatment of water, waste water, or sewage by neutralisation; pH adjustment
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/20—Heavy metals or heavy metal compounds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2301/00—General aspects of water treatment
- C02F2301/08—Multistage treatments, e.g. repetition of the same process step under different conditions
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Separation Of Suspended Particles By Flocculating Agents (AREA)
Abstract
Description
技术领域 technical field
本发明涉及废水处理技术,特别是一种去除水溶液中微量镉的方法。 The invention relates to waste water treatment technology, in particular to a method for removing trace cadmium in aqueous solution.
背景技术 Background technique
水体镉污染受到世界各国的关注。随着水体镉污染爆发频次升高和污染日益严重,重点流域及水环境敏感地区的地方部门对生产企业镉的排放限值执行《地表水环境质量标准》(GB3838-2002)Ⅱ类标准(Cd≤0.005mg/L),2006年我国新颁布的《生活饮用水卫生标准》,将镉的浓度也作了严格的限定,限定Cd≤0.005mg/L。含镉废水的处理方法较多,根据镉含量及镉存在形态的不同,所采用的处理方法也不同。目前除镉方法主要有物理法、化学法、物理化学法和生物法,其中主要是以化学法为主,包括化学吸附法、化学沉淀法(氢氧化物沉淀法和硫化物沉淀法)、电化学氧化还原法、铁氧化法、混凝沉淀法、螯合沉淀法、泡沫分离法等。 Cadmium pollution in water has attracted worldwide attention. With the increasing frequency of water body cadmium pollution outbreaks and increasingly serious pollution, local departments in key river basins and water-environmentally sensitive areas implement the Class II standard (Cd ≤0.005mg/L), in 2006, my country's newly promulgated "Drinking Water Hygienic Standards" also strictly limited the concentration of cadmium, limiting Cd≤0.005mg/L. There are many treatment methods for cadmium-containing wastewater, and the treatment methods adopted are different according to the cadmium content and cadmium existence form. At present, cadmium removal methods mainly include physical methods, chemical methods, physical chemical methods and biological methods, among which chemical methods are mainly used, including chemical adsorption method, chemical precipitation method (hydroxide precipitation method and sulfide precipitation method), electrodeposition method, etc. Chemical redox method, iron oxidation method, coagulation precipitation method, chelation precipitation method, foam separation method, etc.
专利“一种脱除水溶液中微量镉的方法”(授权公告号CN102249450B),特点是通过对在铬环境下生长植物的培养和剖析,通过控制溶液pH值,以及加入含铁试剂、碳酸盐和磷酸盐或钼酸盐等,基本上除去含镉废液中的镉。此发明所用原料经济易得,未向体系中添加任何含有害元素,废水处理时间短,试剂用量少,废渣产生量少,处理后的水溶液中镉含量小于0.01mg/L,可排入二级管网。虽是一种环境友好型处理方法,可广泛应用于金属加工业、电镀业、制革业和纺织业等领域所排放的含镉废水的处理。但此方法不能满足重点流域及水环境敏感地区的地方部门对生产企业镉的排放限值执行《地表水环境质量标准》(GB3838-2002)Ⅱ类标准或《生活饮用水卫生标准》(GB5749-2006 )(Cd≤0.005mg/L)的要求。 The patent "a method for removing trace amounts of cadmium in aqueous solution" (authorized announcement number CN102249450B) is characterized by cultivating and dissecting plants grown in a chromium environment, controlling the pH value of the solution, and adding iron-containing reagents and carbonates And phosphate or molybdate, etc., basically remove cadmium in cadmium-containing waste liquid. The raw materials used in this invention are economical and easy to obtain, no harmful elements are added to the system, the waste water treatment time is short, the amount of reagents is less, and the amount of waste residue is less. The cadmium content in the treated aqueous solution is less than 0.01mg/L, which can be discharged into secondary level pipe network. Although it is an environmentally friendly treatment method, it can be widely used in the treatment of cadmium-containing wastewater discharged from metal processing industry, electroplating industry, leather industry and textile industry. However, this method cannot meet the requirements of local departments in key river basins and water environment-sensitive areas to implement the "Surface Water Environmental Quality Standards" (GB3838-2002) Class II standards or the "Drinking Water Hygienic Standards" (GB5749- 2006 ) (Cd≤0.005mg/L) requirements.
发明内容 Contents of the invention
本发明的目的是提供一种去除水溶液中微量镉的方法,满足重点流域及水环境敏感地区的地方部门对生产企业镉的排放限值执行《地表水环境质量标准》(GB3838-2002)Ⅱ类标准或《生活饮用水卫生标准》(GB5749-2006)(Cd≤0.005mg/L)的要求。 The purpose of the present invention is to provide a method for removing trace amounts of cadmium in aqueous solution, which can meet the requirements of the cadmium discharge limit of production enterprises by local departments in key river basins and water environment sensitive areas to implement Class II of the "Surface Water Environmental Quality Standard" (GB3838-2002) Standards or "Drinking Water Hygienic Standards" (GB5749-2006) (Cd≤0.005mg/L) requirements.
本发明的技术方案:一种去除水溶液中微量镉的方法,包括以下步骤: Technical solution of the present invention: a method for removing trace amounts of cadmium in an aqueous solution, comprising the following steps:
A、调pH值:先在含有二价镉的待处理水溶液中滴加质量浓度1‰的百里酚酞90%乙醇溶液指示剂3—10滴,然后用碱(氢氧化钠或氢氧化钙)调溶液使溶液由无色转变成蓝色即可,溶液的pH值≥9.4; A. Adjust the pH value: first drop 3-10 drops of thymolphthalein 90% ethanol solution indicator with a mass concentration of 1‰ in the aqueous solution to be treated containing divalent cadmium, and then use alkali (sodium hydroxide or calcium hydroxide) Adjust the solution so that the solution turns from colorless to blue, and the pH of the solution is ≥ 9.4;
B、沉淀反应:向调好pH值≥9.4的含有二价镉的待处理水溶液加入沉淀剂碳酸盐(碳酸钠或碳酸氢钠)5—50mg/L,搅拌转速600r/min,时间1—10min进行反应; B. Precipitation reaction: add precipitant carbonate (sodium carbonate or sodium bicarbonate) 5-50 mg/L to the aqueous solution to be treated containing divalent cadmium adjusted to pH ≥ 9.4, stirring speed 600r/min, time 1- 10min to react;
C、混凝:沉淀反应后,搅拌调速为200r/min的同时加入混凝剂铁试剂(氯化铁或聚合硫酸铁),溶液由蓝色转变成无色即pH<9.4,此时在溶液中滴加质量浓度5‰的酚酞90%乙醇溶液指示剂3—10滴,溶液呈鲜红色,继续搅拌的同时加入混凝剂铁试剂使溶液由鲜红色变成淡红色即控制pH≥8,中速120r/min搅拌4.5min,慢速30r/min搅拌10min,静置20分钟,沉降并离心除去含镉沉淀物; C. Coagulation: After the precipitation reaction, add the coagulant iron reagent (ferric chloride or polyferric sulfate) while the stirring speed is adjusted to 200r/min, and the solution changes from blue to colorless, that is, pH<9.4. Add 3-10 drops of phenolphthalein 90% ethanol solution indicator with a mass concentration of 5‰ in the solution, and the solution is bright red. While continuing to stir, add coagulant iron reagent to make the solution change from bright red to light red, that is, control pH ≥ 8 , stirring at a medium speed of 120r/min for 4.5min, stirring at a slow speed of 30r/min for 10min, standing for 20 minutes, settling and centrifuging to remove the cadmium-containing precipitate;
D、出水调pH值:在混凝后沉降并离心除去含镉沉淀物溶液中加酸(硫酸或盐酸)使溶液淡红色变成无色,pH<8.0即可排放。 D. Adjust the pH value of the effluent: After coagulation, settle and centrifuge to remove the cadmium-containing precipitate. Add acid (sulfuric acid or hydrochloric acid) to the solution to turn the solution from light red to colorless, and discharge when the pH is less than 8.0.
本发明使用酸碱指示剂百里酚酞指示剂和酚酞指示剂,通过对镉的氢氧化物性质、镉的碳酸盐性质和氯化铁水解性质的研究,利用百里酚酞指示剂由无色变成蓝色,变化明显易观察,百里酚酞变色范围pH值9.4—10.6,能很好的指示溶液pH的真实值即pH≥9.4,有利于溶液中的镉形成氢氧化镉沉淀;继续加入5—50mg/L碳酸盐使剩余的镉形成碳酸镉颗粒;然后加入铁试剂,利用铁试剂很好的混凝作用将镉的沉淀物混凝沉淀除去,但由于铁试剂水解使pH值下降同时镉的溶解沉淀平衡浓度与pH值的有关(pH=7.8时,Cd=0.0051mg/L;pH≥8.0时,Cd≤0.0032mg/L。),因此混凝过程采用沉淀反应后搅拌调速200r/min的同时加入混凝剂铁试剂,溶液由蓝色转变成无色即pH<9.4,此时在溶液中滴加酚酞指示剂溶液呈鲜红色,继续搅拌的同时加入混凝剂铁试剂使溶液由鲜红色变成淡红色即控制pH≥8,在混凝后沉降并离心除去含镉沉淀物溶液,基本上完全除去含镉溶液中的微量镉(Cd≤0.0032mg/L);出水调pH值可在混凝后沉降并离心除去含镉沉淀物溶液中加酸使溶液淡红色变成无色即pH<8.0可排放。 The present invention uses acid-base indicator thymolphthalein indicator and phenolphthalein indicator, through the research of the hydroxide property of cadmium, the carbonate property of cadmium and the hydrolysis property of ferric chloride, utilizes thymolphthalein indicator to form colorless It turns blue, and the change is obvious and easy to observe. The color change range of thymolphthalein is pH 9.4-10.6, which can well indicate the true value of the solution pH, that is, pH ≥ 9.4, which is conducive to the cadmium in the solution to form cadmium hydroxide precipitation; continue to add 5—50mg/L carbonate makes the remaining cadmium form cadmium carbonate particles; then add iron reagent, use the good coagulation effect of iron reagent to remove the cadmium precipitate, but the pH value drops due to the hydrolysis of iron reagent At the same time, the equilibrium concentration of cadmium dissolution and precipitation is related to the pH value (when pH=7.8, Cd=0.0051mg/L; when pH≥8.0, Cd≤0.0032mg/L.), so the coagulation process adopts precipitation reaction and then stirs the speed. Add the coagulant iron reagent at the same time at 200r/min, the solution turns from blue to colorless, that is, pH<9.4, at this time, add the phenolphthalein indicator dropwise in the solution and the solution turns bright red, continue stirring while adding the coagulant iron reagent Make the solution change from bright red to light red, that is, control the pH ≥ 8, settle and centrifuge to remove the cadmium-containing precipitate solution after coagulation, and basically completely remove the trace cadmium (Cd≤0.0032mg/L) in the cadmium-containing solution; effluent The pH value can be adjusted after coagulation, sedimentation and centrifugation to remove cadmium-containing precipitates. Add acid to the solution to make the solution light red and colorless, that is, pH<8.0 can be discharged.
本发明的优点是巧妙的利用酸碱指示剂百里酚酞指示剂和酚酞指示剂有效的控制适宜的pH值,避免了使用pH试纸有显色误差或pH计的有系统误差不能获得准确pH值,使大量的镉既能形成氢氧化镉沉淀,又能适当的控制碱的加入量,保证加入碳酸盐后剩余的镉尽可能形成碳酸镉颗粒,溶液中的镉Cd≤0.0032mg/L,利用铁试剂很好的混凝作用将镉的沉淀物混凝沉淀除去,并在混凝后沉降并离心除去含镉沉淀物溶液中加酸使溶液淡红色变成无色即可,pH<8.0可排放。 The advantage of the present invention is that the acid-base indicator thymolphthalein indicator and phenolphthalein indicator are cleverly used to effectively control the appropriate pH value, avoiding the use of pH test paper with color development errors or systematic errors of the pH meter that cannot obtain accurate pH values , so that a large amount of cadmium can not only form cadmium hydroxide precipitation, but also properly control the amount of alkali added to ensure that the remaining cadmium after adding carbonate can form cadmium carbonate particles as much as possible, and the cadmium in the solution Cd≤0.0032mg/L, Use the good coagulation effect of iron reagent to remove the cadmium precipitate by coagulation and precipitation, and after coagulation, settle and centrifuge to remove the cadmium-containing precipitate. Add acid to the solution to make the solution light red to colorless, pH<8.0 can be discharged.
本发明与专利“一种脱除水溶液中微量镉的方法”(授权公告号CN102249450B)对比,一样具有所用原料经济易得,未向体系中添加任何含有害元素,废水处理时间短,因其改变了操作方式及控制pH值的范围,使试剂品种量减少,试剂用量减少,废渣产生量减少,运行简单且成本低,混凝后不需增加离子交换或膜分离等设备,处理后的水溶液中镉含量更小(Cd≤0.0032mg/L),满足重点流域及水环境敏感地区的地方部门对生产企业镉的排放限值执行《地表水环境质量标准》(GB3838-2002)Ⅱ类标准或《生活饮用水卫生标准》(GB5749-2006)(Cd≤0.005mg/L)的要求。本发明是一种环境友好型处理方法,可广泛应用于选矿、冶金、金属加工业、电镀业、制革业和纺织业等领域所排放的含镉废水的处理。 Compared with the patent "a method for removing trace cadmium in aqueous solution" (authorized announcement number CN102249450B), the present invention has the same advantages as the raw materials used are economical and easy to obtain, no harmful elements are added to the system, and the waste water treatment time is short. The operation mode and the range of pH value are controlled, so that the amount of reagents is reduced, the amount of reagents is reduced, the amount of waste residue is reduced, the operation is simple and the cost is low, and there is no need to increase ion exchange or membrane separation equipment after coagulation. The cadmium content is smaller (Cd≤0.0032mg/L), which meets the cadmium discharge limit of production enterprises in key river basins and water environment-sensitive areas. Sanitary Standards for Drinking Water (GB5749-2006) (Cd≤0.005mg/L) requirements. The invention is an environment-friendly treatment method, which can be widely used in the treatment of cadmium-containing waste water discharged from fields such as ore dressing, metallurgy, metal processing industry, electroplating industry, tanning industry and textile industry.
具体实施方式 detailed description
实施例1:量取镉含量为50mg/L的水溶液1L,在水溶液滴加质量浓度1‰的百里酚酞90%乙醇溶液指示剂3滴,然后用氢氧化钙质量浓度10%溶液调节溶液,溶液由无色转变成蓝色即可,溶液pH值即pH≥9.4,加入5mg碳酸钠搅拌转速600r/min,时间1min进行反应之后,搅拌调速200r/min的同时加入混凝剂氯化铁使溶液由蓝色转变成无色即pH<9.4,在溶液中滴加质量浓度5‰的酚酞90%乙醇溶液指示剂10滴,继续搅拌的同时加入混凝剂氯化铁使溶液由鲜红色变成淡红色,即控制pH≥8,中速120r/min搅拌4.5min,低速30r/min搅拌10min,静置20分钟,沉降并离心除去含镉沉淀物;在除去含镉沉淀物溶液中加硫酸使溶液淡红色变成无色,即pH值<8,出水镉浓度为0.0031mg/L,达到《地表水环境质量标准》(GB3838-2002)Ⅱ类标准或《生活饮用水卫生标准》(GB5749-2006)(Cd≤0.005mg/L)的要求。 Embodiment 1: measure cadmium content and be the aqueous solution 1L of 50mg/L, add 3 drops of Thymolphthalein 90% ethanol solution indicator of mass concentration 1‰ in aqueous solution, adjust solution with calcium hydroxide mass concentration 10% solution then, The solution can change from colorless to blue. The pH value of the solution is pH ≥ 9.4. Add 5mg of sodium carbonate and stir at a speed of 600r/min. After the reaction takes 1min, add the coagulant ferric chloride while stirring at a speed of 200r/min. Make the solution change from blue to colorless, that is, pH<9.4, add 10 drops of phenolphthalein 90% ethanol solution indicator with a mass concentration of 5‰ in the solution, and add the coagulant ferric chloride while continuing to stir to make the solution change from bright red Turn into light red, that is, control the pH ≥ 8, stir at a medium speed of 120r/min for 4.5min, stir at a low speed of 30r/min for 10min, let stand for 20 minutes, settle and centrifuge to remove the cadmium-containing precipitate; add to the solution for removing the cadmium-containing precipitate Sulfuric acid turns the solution from light red to colorless, that is, the pH value is <8, and the concentration of cadmium in the effluent is 0.0031mg/L, which meets the Class II standard of "Environmental Quality Standards for Surface Water" (GB3838-2002) or "Hygienic Standards for Drinking Water" ( GB5749-2006) (Cd≤0.005mg/L) requirements.
实施例2:量取镉含量为50mg/L的水溶液1L,在水溶液滴加质量浓度1‰的百里酚酞90%乙醇溶液指示剂6滴,然后用氢氧化钠溶液调节溶液,溶液由无色转变成蓝色即可,溶液pH值即pH≥9.4,加入50mg碳酸钠搅拌转速600r/min,时间10min进行反应之后,搅拌调速200r/min的同时加入混凝剂氯化铁溶液由蓝色转变成无色即pH<9.4,在溶液中滴加质量浓度5‰的酚酞90%乙醇溶液指示剂6滴,继续搅拌的同时加入混凝剂氯化铁使溶液由鲜红色变成淡红色,即控制pH≥8,中速120r/min搅拌4.5min,低速30r/min搅拌10min,静置20分钟,沉降并离心除去含镉沉淀物。在除去含镉沉淀物溶液中加盐酸使溶液淡红色变成无色,即pH值<8,出水镉浓度为0.0029mg/L,达到《地表水环境质量标准》(GB3838-2002)Ⅱ类标准或《生活饮用水卫生标准》(GB5749-2006)(Cd≤0.005mg/L)的要求。 Embodiment 2: Measure cadmium content and be 1L of aqueous solution of 50mg/L, drip 6 drops of Thymolphthalein 90% ethanol solution indicator of mass concentration 1‰ in aqueous solution, then adjust solution with sodium hydroxide solution, solution is by colorless Just turn blue, the pH value of the solution is pH ≥ 9.4, add 50 mg of sodium carbonate and stir at a speed of 600r/min, and react for 10 minutes, then add the coagulant ferric chloride solution while stirring at a speed of 200r/min. Change to colorless, that is, pH<9.4, add 6 drops of phenolphthalein 90% ethanol solution indicator with a mass concentration of 5‰ in the solution, and add coagulant ferric chloride while continuing to stir to make the solution change from bright red to light red. That is, control the pH ≥ 8, stir at a medium speed of 120r/min for 4.5min, stir at a low speed of 30r/min for 10min, let stand for 20 minutes, settle and centrifuge to remove the cadmium-containing precipitate. Add hydrochloric acid to the solution for removing cadmium-containing precipitates to turn the solution from light red to colorless, that is, the pH value is <8, and the cadmium concentration in the effluent is 0.0029mg/L, which meets the Class II standard of "Surface Water Environmental Quality Standards" (GB3838-2002) Or the requirements of "Hygienic Standards for Drinking Water" (GB5749-2006) (Cd≤0.005mg/L).
实施例3:量取镉含量为50mg/L的水溶液1L,在水溶液滴加质量浓度5‰的酚酞90%乙醇溶液指示剂10滴,然后用氢氧化钠溶液调节溶液,溶液由无色转变成蓝色即可,溶液pH值即pH≥9.4,加入25mg碳酸氢钠搅拌转速600r/min,时间5min进行反应之后,搅拌调速200r/min的同时加入混凝剂聚合硫酸铁溶液由蓝色转变成无色,即pH<9.4,在溶液中滴加质量浓度5‰的酚酞90%乙醇溶液指示剂3滴,继续搅拌的同时加入混凝剂聚合硫酸铁使溶液由鲜红色变成淡红色,即控制pH≥8,中速120r/min搅拌4.5min,低速30r/min搅拌10min,静置20分钟,沉降并离心除去含镉沉淀物。在除去含镉沉淀物溶液中加盐酸使溶液淡红色变成无色即pH值<8,出水镉浓度为0.0028mg/L,达到《地表水环境质量标准》(GB3838-2002)Ⅱ类标准或《生活饮用水卫生标准》(GB5749-2006)(Cd≤0.005mg/L)的要求。 Embodiment 3: measure cadmium content and be the aqueous solution 1L of 50mg/L, add dropwise 10 drops of phenolphthalein 90% ethanol solution indicator of mass concentration 5‰ in aqueous solution, then adjust solution with sodium hydroxide solution, solution changes from colorless to Blue is enough, the pH value of the solution is pH ≥ 9.4, add 25 mg of sodium bicarbonate and stir at a speed of 600r/min, and react for 5 minutes, then add a coagulant polymerized ferric sulfate solution to change from blue while stirring at a speed of 200r/min become colorless, that is, pH<9.4, add 3 drops of phenolphthalein 90% ethanol solution indicator with a mass concentration of 5‰ in the solution, and add coagulant polyferric sulfate while continuing to stir to make the solution change from bright red to light red. That is, control the pH ≥ 8, stir at a medium speed of 120r/min for 4.5min, stir at a low speed of 30r/min for 10min, let stand for 20 minutes, settle and centrifuge to remove the cadmium-containing precipitate. Add hydrochloric acid to the solution to remove cadmium-containing precipitates to turn the solution from light red to colorless, that is, the pH value is <8, and the cadmium concentration in the effluent is 0.0028mg/L, which meets the Class II standard of "Surface Water Environmental Quality Standards" (GB3838-2002) or "Drinking Water Hygienic Standard" (GB5749-2006) (Cd≤0.005mg/L) requirements.
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