JPH0221995A - Treatment of waste solution - Google Patents
Treatment of waste solutionInfo
- Publication number
- JPH0221995A JPH0221995A JP17188888A JP17188888A JPH0221995A JP H0221995 A JPH0221995 A JP H0221995A JP 17188888 A JP17188888 A JP 17188888A JP 17188888 A JP17188888 A JP 17188888A JP H0221995 A JPH0221995 A JP H0221995A
- Authority
- JP
- Japan
- Prior art keywords
- copper
- waste liquid
- waste
- plating
- soln
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
- 239000002699 waste material Substances 0.000 title claims abstract description 65
- PXHVJJICTQNCMI-UHFFFAOYSA-N Nickel Chemical compound [Ni] PXHVJJICTQNCMI-UHFFFAOYSA-N 0.000 claims abstract description 49
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 claims abstract description 42
- 239000010949 copper Substances 0.000 claims abstract description 41
- 229910052802 copper Inorganic materials 0.000 claims abstract description 41
- 239000002244 precipitate Substances 0.000 claims abstract description 29
- 229910052751 metal Inorganic materials 0.000 claims abstract description 26
- 239000002184 metal Substances 0.000 claims abstract description 26
- 229910052759 nickel Inorganic materials 0.000 claims abstract description 25
- 239000003518 caustics Substances 0.000 claims abstract description 15
- 239000010941 cobalt Substances 0.000 claims abstract description 13
- 229910017052 cobalt Inorganic materials 0.000 claims abstract description 13
- GUTLYIVDDKVIGB-UHFFFAOYSA-N cobalt atom Chemical compound [Co] GUTLYIVDDKVIGB-UHFFFAOYSA-N 0.000 claims abstract description 13
- BQCADISMDOOEFD-UHFFFAOYSA-N Silver Chemical compound [Ag] BQCADISMDOOEFD-UHFFFAOYSA-N 0.000 claims abstract description 12
- 239000003513 alkali Substances 0.000 claims abstract description 12
- PCHJSUWPFVWCPO-UHFFFAOYSA-N gold Chemical compound [Au] PCHJSUWPFVWCPO-UHFFFAOYSA-N 0.000 claims abstract description 12
- 229910052737 gold Inorganic materials 0.000 claims abstract description 12
- 239000010931 gold Substances 0.000 claims abstract description 12
- 229910052709 silver Inorganic materials 0.000 claims abstract description 12
- 239000004332 silver Substances 0.000 claims abstract description 12
- 238000006243 chemical reaction Methods 0.000 claims abstract description 6
- 239000007788 liquid Substances 0.000 claims description 56
- 238000000034 method Methods 0.000 claims description 40
- JVBXVOWTABLYPX-UHFFFAOYSA-L sodium dithionite Chemical compound [Na+].[Na+].[O-]S(=O)S([O-])=O JVBXVOWTABLYPX-UHFFFAOYSA-L 0.000 claims description 15
- 150000004699 copper complex Chemical class 0.000 claims description 4
- 150000004696 coordination complex Chemical class 0.000 claims 1
- 238000007747 plating Methods 0.000 abstract description 32
- 150000002739 metals Chemical class 0.000 abstract description 8
- 238000001914 filtration Methods 0.000 abstract description 6
- 229910001385 heavy metal Inorganic materials 0.000 abstract description 6
- 150000003839 salts Chemical class 0.000 abstract description 6
- 239000002738 chelating agent Substances 0.000 abstract description 4
- OMZSGWSJDCOLKM-UHFFFAOYSA-N copper(II) sulfide Chemical compound [S-2].[Cu+2] OMZSGWSJDCOLKM-UHFFFAOYSA-N 0.000 abstract description 4
- 230000001105 regulatory effect Effects 0.000 abstract 3
- GRWZHXKQBITJKP-UHFFFAOYSA-L dithionite(2-) Chemical compound [O-]S(=O)S([O-])=O GRWZHXKQBITJKP-UHFFFAOYSA-L 0.000 abstract 2
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 27
- WSFSSNUMVMOOMR-UHFFFAOYSA-N Formaldehyde Chemical compound O=C WSFSSNUMVMOOMR-UHFFFAOYSA-N 0.000 description 14
- KRKNYBCHXYNGOX-UHFFFAOYSA-N citric acid Chemical compound OC(=O)CC(O)(C(O)=O)CC(O)=O KRKNYBCHXYNGOX-UHFFFAOYSA-N 0.000 description 12
- 238000003756 stirring Methods 0.000 description 10
- 235000011121 sodium hydroxide Nutrition 0.000 description 9
- 239000002351 wastewater Substances 0.000 description 9
- KCXVZYZYPLLWCC-UHFFFAOYSA-N EDTA Chemical compound OC(=O)CN(CC(O)=O)CCN(CC(O)=O)CC(O)=O KCXVZYZYPLLWCC-UHFFFAOYSA-N 0.000 description 8
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 8
- 239000000706 filtrate Substances 0.000 description 6
- RWSOTUBLDIXVET-UHFFFAOYSA-M hydrosulfide Chemical compound [SH-] RWSOTUBLDIXVET-UHFFFAOYSA-M 0.000 description 6
- 238000007772 electroless plating Methods 0.000 description 5
- 239000000243 solution Substances 0.000 description 5
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 4
- MHAJPDPJQMAIIY-UHFFFAOYSA-N Hydrogen peroxide Chemical compound OO MHAJPDPJQMAIIY-UHFFFAOYSA-N 0.000 description 4
- 239000002253 acid Substances 0.000 description 4
- 235000015165 citric acid Nutrition 0.000 description 4
- 238000004140 cleaning Methods 0.000 description 4
- 229910052742 iron Inorganic materials 0.000 description 4
- 150000002815 nickel Chemical class 0.000 description 4
- QTBSBXVTEAMEQO-UHFFFAOYSA-N Acetic acid Chemical compound CC(O)=O QTBSBXVTEAMEQO-UHFFFAOYSA-N 0.000 description 3
- FEWJPZIEWOKRBE-UHFFFAOYSA-N Tartaric acid Natural products [H+].[H+].[O-]C(=O)C(O)C(O)C([O-])=O FEWJPZIEWOKRBE-UHFFFAOYSA-N 0.000 description 3
- 230000000052 comparative effect Effects 0.000 description 3
- 239000000203 mixture Substances 0.000 description 3
- 239000004033 plastic Substances 0.000 description 3
- 229920003023 plastic Polymers 0.000 description 3
- 239000000843 powder Substances 0.000 description 3
- 239000000047 product Substances 0.000 description 3
- 229910000033 sodium borohydride Inorganic materials 0.000 description 3
- 239000012279 sodium borohydride Substances 0.000 description 3
- 239000001509 sodium citrate Substances 0.000 description 3
- NLJMYIDDQXHKNR-UHFFFAOYSA-K sodium citrate Chemical compound O.O.[Na+].[Na+].[Na+].[O-]C(=O)CC(O)(CC([O-])=O)C([O-])=O NLJMYIDDQXHKNR-UHFFFAOYSA-K 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- 239000011975 tartaric acid Substances 0.000 description 3
- 235000002906 tartaric acid Nutrition 0.000 description 3
- KXDHJXZQYSOELW-UHFFFAOYSA-N Carbamic acid Chemical class NC(O)=O KXDHJXZQYSOELW-UHFFFAOYSA-N 0.000 description 2
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 2
- RGHNJXZEOKUKBD-SQOUGZDYSA-N D-gluconic acid Chemical compound OC[C@@H](O)[C@@H](O)[C@H](O)[C@@H](O)C(O)=O RGHNJXZEOKUKBD-SQOUGZDYSA-N 0.000 description 2
- FEWJPZIEWOKRBE-JCYAYHJZSA-N Dextrotartaric acid Chemical compound OC(=O)[C@H](O)[C@@H](O)C(O)=O FEWJPZIEWOKRBE-JCYAYHJZSA-N 0.000 description 2
- OFOBLEOULBTSOW-UHFFFAOYSA-N Malonic acid Chemical compound OC(=O)CC(O)=O OFOBLEOULBTSOW-UHFFFAOYSA-N 0.000 description 2
- 150000007513 acids Chemical class 0.000 description 2
- 229910021529 ammonia Inorganic materials 0.000 description 2
- BFNBIHQBYMNNAN-UHFFFAOYSA-N ammonium sulfate Chemical compound N.N.OS(O)(=O)=O BFNBIHQBYMNNAN-UHFFFAOYSA-N 0.000 description 2
- 229910052921 ammonium sulfate Inorganic materials 0.000 description 2
- 235000011130 ammonium sulphate Nutrition 0.000 description 2
- 150000001669 calcium Chemical class 0.000 description 2
- 159000000007 calcium salts Chemical class 0.000 description 2
- 239000013522 chelant Substances 0.000 description 2
- 238000009713 electroplating Methods 0.000 description 2
- 229910052500 inorganic mineral Inorganic materials 0.000 description 2
- 229910021645 metal ion Inorganic materials 0.000 description 2
- 239000011707 mineral Substances 0.000 description 2
- 235000010755 mineral Nutrition 0.000 description 2
- 230000001376 precipitating effect Effects 0.000 description 2
- 239000011347 resin Substances 0.000 description 2
- 229920005989 resin Polymers 0.000 description 2
- SQGYOTSLMSWVJD-UHFFFAOYSA-N silver(1+) nitrate Chemical compound [Ag+].[O-]N(=O)=O SQGYOTSLMSWVJD-UHFFFAOYSA-N 0.000 description 2
- KDYFGRWQOYBRFD-UHFFFAOYSA-N succinic acid Chemical compound OC(=O)CCC(O)=O KDYFGRWQOYBRFD-UHFFFAOYSA-N 0.000 description 2
- 239000006228 supernatant Substances 0.000 description 2
- BJEPYKJPYRNKOW-REOHCLBHSA-N (S)-malic acid Chemical compound OC(=O)[C@@H](O)CC(O)=O BJEPYKJPYRNKOW-REOHCLBHSA-N 0.000 description 1
- KWSLGOVYXMQPPX-UHFFFAOYSA-N 5-[3-(trifluoromethyl)phenyl]-2h-tetrazole Chemical compound FC(F)(F)C1=CC=CC(C2=NNN=N2)=C1 KWSLGOVYXMQPPX-UHFFFAOYSA-N 0.000 description 1
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 description 1
- KZBUYRJDOAKODT-UHFFFAOYSA-N Chlorine Chemical compound ClCl KZBUYRJDOAKODT-UHFFFAOYSA-N 0.000 description 1
- RGHNJXZEOKUKBD-UHFFFAOYSA-N D-gluconic acid Natural products OCC(O)C(O)C(O)C(O)C(O)=O RGHNJXZEOKUKBD-UHFFFAOYSA-N 0.000 description 1
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 description 1
- UCKMPCXJQFINFW-UHFFFAOYSA-N Sulphide Chemical compound [S-2] UCKMPCXJQFINFW-UHFFFAOYSA-N 0.000 description 1
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 description 1
- BJEPYKJPYRNKOW-UHFFFAOYSA-N alpha-hydroxysuccinic acid Natural products OC(=O)C(O)CC(O)=O BJEPYKJPYRNKOW-UHFFFAOYSA-N 0.000 description 1
- -1 amine boron compound Chemical class 0.000 description 1
- 239000007864 aqueous solution Substances 0.000 description 1
- 239000006227 byproduct Substances 0.000 description 1
- 229940043430 calcium compound Drugs 0.000 description 1
- 150000001674 calcium compounds Chemical class 0.000 description 1
- 150000001735 carboxylic acids Chemical class 0.000 description 1
- 239000012320 chlorinating reagent Substances 0.000 description 1
- 150000001805 chlorine compounds Chemical class 0.000 description 1
- 239000012459 cleaning agent Substances 0.000 description 1
- 150000001868 cobalt Chemical class 0.000 description 1
- 238000004737 colorimetric analysis Methods 0.000 description 1
- 230000000536 complexating effect Effects 0.000 description 1
- 238000011109 contamination Methods 0.000 description 1
- 150000001879 copper Chemical class 0.000 description 1
- 230000018044 dehydration Effects 0.000 description 1
- 238000006297 dehydration reaction Methods 0.000 description 1
- 230000006866 deterioration Effects 0.000 description 1
- 239000012065 filter cake Substances 0.000 description 1
- 239000011521 glass Substances 0.000 description 1
- 239000000174 gluconic acid Substances 0.000 description 1
- 235000012208 gluconic acid Nutrition 0.000 description 1
- FDWREHZXQUYJFJ-UHFFFAOYSA-M gold monochloride Chemical compound [Cl-].[Au+] FDWREHZXQUYJFJ-UHFFFAOYSA-M 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 150000004679 hydroxides Chemical class 0.000 description 1
- 150000002506 iron compounds Chemical class 0.000 description 1
- 159000000014 iron salts Chemical class 0.000 description 1
- 238000010169 landfilling Methods 0.000 description 1
- 239000001630 malic acid Substances 0.000 description 1
- 235000011090 malic acid Nutrition 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 230000001590 oxidative effect Effects 0.000 description 1
- 238000010979 pH adjustment Methods 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- ACVYVLVWPXVTIT-UHFFFAOYSA-M phosphinate Chemical compound [O-][PH2]=O ACVYVLVWPXVTIT-UHFFFAOYSA-M 0.000 description 1
- 238000001556 precipitation Methods 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 238000009991 scouring Methods 0.000 description 1
- 238000004062 sedimentation Methods 0.000 description 1
- 150000003378 silver Chemical class 0.000 description 1
- 229910001961 silver nitrate Inorganic materials 0.000 description 1
- 239000010802 sludge Substances 0.000 description 1
- 229910001379 sodium hypophosphite Inorganic materials 0.000 description 1
- 239000002689 soil Substances 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 239000001384 succinic acid Substances 0.000 description 1
- 238000004065 wastewater treatment Methods 0.000 description 1
- 229910052725 zinc Inorganic materials 0.000 description 1
- 239000011701 zinc Substances 0.000 description 1
Landscapes
- Removal Of Specific Substances (AREA)
Abstract
Description
【発明の詳細な説明】
技術分野
本発明はメツキ廃水の処理方法に関し、更に詳しくは、
銅又はニッケル或いはコバルト、銀、金等の金属錯体を
含むメツキ廃液の簡便かつ経済的な処理方法に関する。DETAILED DESCRIPTION OF THE INVENTION Technical Field The present invention relates to a method for treating wastewater, more specifically:
The present invention relates to a simple and economical method for treating plating waste liquid containing copper, nickel, or metal complexes such as cobalt, silver, and gold.
従来技術と問題点
通常、メツキ液にはその安定化のために金属と鉛体をつ
くる各種のキレート剤か使われている。Prior Art and Problems Generally, plating solutions contain various chelating agents that create metal and lead bodies to stabilize them.
そのためメツキ工場からは銅、ニッケル等の金属とエチ
レンジアミン四酢酸(以下、EDTAと略記する)、酒
石酸、クエン酸なととの錯体を含有する廃水か発生する
。Therefore, the Metsuki factory generates wastewater containing complexes of metals such as copper and nickel with ethylenediaminetetraacetic acid (hereinafter abbreviated as EDTA), tartaric acid, and citric acid.
近年、電子機器の小型化、軽量化のためのプリント配線
基板か開発され、プラスチック基板のスルーホール上に
導電性を付与するために無電解メツキ(別名、化学メツ
キともいう)技術が応用されている。In recent years, printed wiring boards have been developed to make electronic devices smaller and lighter, and electroless plating (also known as chemical plating) technology has been applied to add conductivity to the through holes of plastic boards. There is.
この技術は自動車の部品、家庭電化機器、装飾品等に多
用されているプラスチック表面のメッキにも活用されて
いる。This technology is also used for plating the surfaces of plastics, which are often used in automobile parts, home appliances, decorative items, etc.
グラスチックは非導電性のため、電解メツキ法では金属
メツキは不可能であったが、無電解メツキの開発により
装飾品や金属代替のプラスチック製品の表面処理等が可
能となり、この技術か多用されつつある。Because glass is non-conductive, it was impossible to plate it with metal using the electrolytic plating method, but with the development of electroless plating, it became possible to treat the surface of decorative items and plastic products as a substitute for metals, and this technology became widely used. It's coming.
無電解メツキでは金属のメツキ浴への溶解促進や安定性
を高める等の目的で、通常EDTAなとのアミノカルボ
ン酸;酒石酸、クエン酸、グルコン酸、リンゴ酸などの
オキシカルボン酸:マロン酸、コハク酸、酢酸などのカ
ルボン酸等のキレト剤か使用される。このうちアミノカ
ルボン酸とオキシカルボン酸は液中の金属イオンと安定
な錯体を形成するため、通常の廃水処理で採用されてい
る凝集沈殿による処理では溶存金属の分離除去は困難で
ある。そのためメツキ廃液による河川及び土壌汚染がし
ばしば問題にされている。In electroless plating, aminocarboxylic acids such as EDTA; oxycarboxylic acids such as tartaric acid, citric acid, gluconic acid, and malic acid; malonic acid, Chelating agents such as carboxylic acids such as succinic acid and acetic acid are used. Among these, aminocarboxylic acids and oxycarboxylic acids form stable complexes with metal ions in the liquid, so it is difficult to separate and remove dissolved metals by coagulation-sedimentation treatment, which is commonly used in wastewater treatment. For this reason, river and soil contamination due to wastewater is often a problem.
従来、メツキ廃液の処理法としては、過酸化水素等によ
る化学的処理法又は電解酸化処理法などが知られている
。また、重金属錯体含有廃水の処理法として、該廃水に
可溶性鉄塩又はカルシウム塩を添加するこ七により重金
属錯体を鉄又はカルシウムの錯体に変え、遊離した重金
属を水酸化物として沈殿さゼ分離する置換処理法、又は
重金属錯体をそのまま活性炭に吸着させる方法等か提案
されているか、これらの方法は処理工程か複雑で、その
上副生ずる鉄又はカルシウムの錯体の処理に手間かかか
り処理コストか高くなる等の欠点かあり必らずしも満足
のいくものではなかった。Conventionally, methods for treating plating waste liquid include chemical treatment using hydrogen peroxide or the like, electrolytic oxidation treatment, and the like. In addition, as a method for treating wastewater containing heavy metal complexes, soluble iron salts or calcium salts are added to the wastewater to convert the heavy metal complexes into iron or calcium complexes, and the liberated heavy metals are precipitated and separated as hydroxides. Has there been any proposal for a replacement treatment method or a method for directly adsorbing heavy metal complexes onto activated carbon?These methods involve complicated treatment steps, and in addition, treatment of the iron or calcium complexes produced as by-products is time-consuming and expensive. It was not always satisfactory due to some shortcomings.
例えは特開昭50−10780号公報には、鉄とクエン
酸との錯体を含む化学洗浄廃液にカルシウム化合物を過
剰に添加することにより、該廃液中の金属分及びクエン
酸分を難溶性のカルシウム塩として同時に沈殿させて分
離し、その上澄液をさらに過酸化水素や過塩化物等で酸
化し、COD成分を分解する方法か開示されている。For example, JP-A No. 50-10780 discloses that by adding an excessive amount of calcium compound to a chemical cleaning waste liquid containing a complex of iron and citric acid, the metal content and citric acid content in the waste liquid are reduced to a poorly soluble form. A method is disclosed in which COD components are decomposed by simultaneously precipitating and separating the calcium salt, and further oxidizing the supernatant with hydrogen peroxide, perchloride, or the like.
しかし、この方法は沈殿物の脱水、焼却、埋立て等にか
なりの処理費か必要て工業的に実施するにはコス1へ的
に問題がある。However, this method requires considerable processing costs for dehydration, incineration, landfilling, etc. of the precipitate, and is problematic in terms of cost for industrial implementation.
また、特開昭60−118号公報には、エチレンジアミ
ン四酢酸、銅及びホルマリンを含有する廃液を昇温し、
廃液に含まれるホルマリンを利用して還元を行う第1工
程、鉱酸を添加し液のP H値を2.5以下に調整し、
エチレンジアミン四酢酸を析出せしめて回収する第2工
程、及び第1工程と第2工程を経た廃液に3価の鉄化合
物を添加した後キレート樹脂で吸着処理するか、又は第
1工樹と第2工程を経た廃液を3価の鉄を前もって吸着
させたキレート樹脂で吸着処理し、廃液中に残存する銅
を除去する第3工程により処理する方法が開示されてい
るが、この方法ではキレート樹脂に吸着した銅を鉱酸で
溶出し、溶出した銅をさらに通常の凝集沈殿法で処理す
るという複数の工程を経るため、複雑な装置及び手間を
要し、更に処理費も高くなる等の欠点がある。In addition, JP-A-60-118 discloses that a waste liquid containing ethylenediaminetetraacetic acid, copper and formalin is heated,
The first step is to perform reduction using formalin contained in the waste liquid, add mineral acid to adjust the pH value of the liquid to 2.5 or less,
A second step in which ethylenediaminetetraacetic acid is precipitated and recovered, and a trivalent iron compound is added to the waste liquid from the first and second steps and then adsorbed with a chelate resin, or the first and second A method is disclosed in which the waste liquid that has passed through the process is adsorbed with a chelate resin that has adsorbed trivalent iron in advance, and the copper remaining in the waste liquid is removed in a third step. Since the process involves multiple steps: eluting the adsorbed copper with mineral acid and then treating the eluted copper with the usual coagulation-precipitation method, it requires complicated equipment and time, and has the disadvantages of high processing costs. be.
さらに、特開昭60−118290号公報には、ニッケ
ル、亜鉛、銅、コバルト等の金属と種々のキレ−1〜剤
からなる錯体を含有する廃水を処理するに当り、ニッケ
ルとして100〜200mg/j2が存在する条件下に
PH7〜I2で塩素化剤を添加して、金属を酸化物とし
て沈殿させる方法が開示されている。しかし、この方法
では、廃水中にニッケルが存在しない場合にはニッケル
塩を添加する必要があること、及び金属を腐蝕し易く、
且つ人体に有害な塩素ガスを発生する塩素化合物を酸化
物として使用するため、装置の耐久性や作業環境を悪化
させる等の問題点がある。Furthermore, JP-A No. 60-118290 discloses that when treating wastewater containing complexes consisting of metals such as nickel, zinc, copper, and cobalt and various cleaning agents, 100 to 200 mg of nickel/ A method is disclosed in which metals are precipitated as oxides by adding a chlorinating agent at pH 7 to I2 in the presence of j2. However, with this method, if nickel is not present in the wastewater, it is necessary to add nickel salt, and the metal is likely to corrode.
In addition, since a chlorine compound that generates chlorine gas that is harmful to the human body is used as an oxide, there are problems such as deterioration of the durability of the device and the working environment.
目的
本発明者は、上記の如き従来の廃液処理技術が有する問
題点を解決すべく検討した結果、先に、銅、ニッケル、
コバルト、銀、金等の金属錯体を含む廃液を苛性アルカ
リでPH11以上に調整後、溶存金属1重量部に対し少
なくとも1重量部の亜二チオン酸ナトリウムを添加し、
生成する沈殿を分離することからなる廃液の処理方法を
提案した(特開昭61−7894号公報)。更に簡単で
経済的な方法を鋭意検討した結果、経費が安価で作業性
・作業環境上も問題のないメツキ廃液処理方法を見い出
し、本発明を完成した。Purpose As a result of studies to solve the problems of the conventional waste liquid treatment technology as described above, the inventor first discovered that copper, nickel,
After adjusting the pH of the waste liquid containing metal complexes such as cobalt, silver, and gold to 11 or higher with caustic alkali, at least 1 part by weight of sodium dithionite is added to 1 part by weight of the dissolved metal,
A method for treating waste liquid consisting of separating the produced precipitate was proposed (Japanese Unexamined Patent Publication No. 7894/1983). As a result of intensive research into simpler and more economical methods, we have discovered a method for treating plating waste liquid that is inexpensive and has no problems in terms of workability and work environment, and has completed the present invention.
解決の手段
かくして、本発明によれば、銅錯体を含む廃液を、苛性
アルカリでPH11以上に調整した後、溶存銅1重量部
に対して少なくとも1重量部の亜二チオン酸ナトリウム
で処理することにより得られる沈殿物0.1〜1容量部
を、銅、ニッケル、コバルト、銀、金等の金属錯体含む
苛性アルカリでPH11以上に調整した廃液1,000
容量部に添加して反応せしめ、生ずる沈殿を分離するこ
とを特徴とする廃液の処理方法、が提供される。Thus, according to the present invention, a waste liquid containing a copper complex is adjusted to pH 11 or higher with caustic alkali, and then treated with at least 1 part by weight of sodium dithionite per 1 part by weight of dissolved copper. 0.1 to 1 volume part of the precipitate obtained was adjusted to pH 11 or higher with a caustic alkali containing metal complexes such as copper, nickel, cobalt, silver, and gold.
Provided is a method for treating waste liquid, which comprises adding a volumetric portion of the liquid to react, and separating the resulting precipitate.
本発明の特徴は、まず第一に、銅の錯体を含む廃液を苛
性アルカリでPH1,1以上に調整した後、溶存金属1
重量部に対して少なくとも1重量部の亜二チオン酸ナト
リウムを添加することにより生ずる沈殿物を利用する点
にある。分離した沈殿物は湿潤状態又は乾燥状態のどち
らの状態で保管してもよい。The feature of the present invention is that, first of all, after adjusting the waste liquid containing the copper complex to pH 1.1 or higher with caustic alkali, the dissolved metal
The point is to utilize the precipitate formed by adding at least 1 part by weight of sodium dithionite. The separated precipitate may be stored either wet or dry.
次に、銅、ニッケル、コバルト、銀、金等の錯体を含む
廃液を、PH11以上に調整した後、廃液1,000容
量部に対し、上記の如くして沈殿分離した銅及び銅硫化
物等の混合物、0.1−1容量部を単独で又は亜二チオ
ン酸ナトリウムと併せ添加し撹拌反応せしめ、生成する
沈殿を分離する。Next, after adjusting the pH of the waste liquid containing complexes of copper, nickel, cobalt, silver, gold, etc. to 11 or higher, the copper and copper sulfide etc. precipitated and separated as described above are added to 1,000 parts by volume of the waste liquid. 0.1-1 part by volume of a mixture of , alone or in combination with sodium dithionite, is stirred and reacted, and the precipitate formed is separated.
本発明の方法が処理対象としている廃液は、銅、ニッケ
ル、コバルト、銀、金等の金属の錯体を含む廃液であり
、主として、これらの金属の無電解メツキ又は電解メツ
キ工程からのメツキ老廃液、或いはメツキ浴から取り出
したメツキ製品の洗浄工程又はメツキ浴のサイクルライ
フでの濾過洗浄工程から排出される洗浄廃液等が包含さ
れる。より具体的には、例えは、(a)銅、銀又は金、
EDTA、ホルマリン及び苛性ソーダを含有する銅、銀
又は金の無電解メツキ廃液: (b)ニッケル、EDT
A、クエン酸ソーダ、アンモニア及びアミンホウ素化合
物又は次亜リン酸塩を含有するニッケルメッキ廃液;
(C)コバルト、クエン酸ソーダ、次亜リン酸ソーダ
、硫酸アンモニウム等を含有するコバルトメツキ廃液な
どが考えられる。The waste liquid to be treated by the method of the present invention is a waste liquid containing complexes of metals such as copper, nickel, cobalt, silver, and gold, and is mainly a plating waste liquid from the electroless plating or electrolytic plating process of these metals. , or cleaning waste liquid discharged from the cleaning process of plating products taken out from the plating bath or the filtration and cleaning process during the cycle life of the plating bath. More specifically, for example: (a) copper, silver or gold;
Copper, silver or gold electroless plating waste containing EDTA, formalin and caustic soda: (b) Nickel, EDT
A, nickel plating waste liquid containing sodium citrate, ammonia and amine boron compound or hypophosphite;
(C) Cobalt plating waste liquid containing cobalt, sodium citrate, sodium hypophosphite, ammonium sulfate, etc. can be considered.
これらの廃液を本発明の方法に従って処理する場合、先
ず、銅メツキ廃液を苛性アルカリによりPH11以上、
好ましくは11〜13の範囲内に調整する。このPH調
整に使用される苛性アルカリはそのまま固体粉末の形で
加えてもよいが、作業性の容易な5〜50%の濃度の水
溶液の形で加えるのが好都合である。When these waste liquids are treated according to the method of the present invention, first, the copper plating waste liquid is adjusted to pH 11 or higher with caustic alkali.
Preferably, it is adjusted within the range of 11 to 13. The caustic alkali used for this pH adjustment may be added as is in the form of a solid powder, but it is convenient to add it in the form of an aqueous solution with a concentration of 5 to 50%, which is easier to work with.
PHを調整した廃液に亜二チオン酸ナトリウムを添加し
撹拌する。亜二チオン酸ナトリウムの添加量は廃液中の
溶存銅1重量部に対して、少なくとも1重量部であり、
この亜二チオン酸ナトリウムは無水塩又は工水塩(ハイ
ドロサルファイド)の形で使用することができる。Add sodium dithionite to the pH-adjusted waste solution and stir. The amount of sodium dithionite added is at least 1 part by weight per 1 part by weight of dissolved copper in the waste liquid,
This sodium dithionite can be used in the form of anhydrous salt or hydrosulfide.
亜二チオン酸ナトリウムの添加により溶存銅がこれと反
応し、溶存銅は銅単体又は硫化物として沈殿析出する。By adding sodium dithionite, dissolved copper reacts with the sodium dithionite, and the dissolved copper precipitates as simple copper or sulfide.
ここで生成した沈殿物はフィルタプレス等で濾過しケー
クとして取り出し、湿潤状態又は、乾燥粉末状態で保管
する。The precipitate generated here is filtered using a filter press or the like, taken out as a cake, and stored in a wet state or in a dry powder state.
次いで、メツキ工程から出たメツキ老廃液のPHを、苛
性アルカリによって11以上、好ましくは11〜13の
範囲に調整し、上記の保管してある湿潤状態又は乾燥状
態の銅沈殿物を添加し撹拌する。ここで使う銅沈殿物の
添加量は、上記老廃液] 、000容量部に対して少な
くとも0,1容量部、通常0.1〜l容量部の範囲であ
る。溶存金属の種類によって上記の銅沈殿物の添加のみ
では溶存金属が十分に沈殿析出しない場合には、亜二チ
オン酸ナトリウムを併用することが好ましい。Next, the pH of the plating waste liquid discharged from the plating process is adjusted to 11 or more, preferably in the range of 11 to 13, using caustic alkali, and the above-mentioned stored wet or dry copper precipitate is added and stirred. do. The amount of the copper precipitate used here is at least 0.1 part by volume, and usually in the range of 0.1 to 1 part by volume, per 000 parts by volume of the waste liquid. Depending on the type of dissolved metal, if the addition of the copper precipitate alone does not sufficiently precipitate the dissolved metal, it is preferable to use sodium dithionite in combination.
ここで使う亜二チオン酸ナトリウムの添加量は一般に溶
存金属の1重量部に対し0.05〜1重量部の範囲が適
当である。The amount of sodium dithionite used here is generally in the range of 0.05 to 1 part by weight per 1 part by weight of the dissolved metal.
生成する単体の銅、金又はニッケル塩、コバルト塩、銀
塩等は、分別の容易な沈殿物を形成するので、フィルタ
ープレス等で容易にケ−りとして取り出すことができる
。The single copper, gold or nickel salts, cobalt salts, silver salts, etc. that are produced form precipitates that are easy to separate, so they can be easily taken out as a case using a filter press or the like.
上記の反応は常温で行なうこともできるが、通常20℃
以上の温度、好ましくは30°〜50℃の範囲内の温度
に加温して行なうと、短時間で反応を完結させることが
できる。Although the above reaction can be carried out at room temperature, it is usually carried out at 20°C.
The reaction can be completed in a short time by heating to the above temperature, preferably within the range of 30° to 50°C.
以上に述へた本発明の方法によって得られるフイルター
ケ−りは一般に約40〜80%という高い金属含有率を
有しており、金属精練の原料として再利用することがで
きる。他方、沈殿物を濾別した後の濾液は金属イオン濃
度が5mg/β以下であり、活性汚泥処理により容易に
COD値を低下させることができる。The filter cake obtained by the method of the present invention as described above generally has a high metal content of about 40 to 80% and can be reused as a raw material for metal scouring. On the other hand, the filtrate after filtering out the precipitate has a metal ion concentration of 5 mg/β or less, and the COD value can be easily lowered by activated sludge treatment.
次に実施例を掲げて本発明の方法をさらに具体的に説明
する。Next, the method of the present invention will be explained in more detail with reference to Examples.
実施例1
銅1,300mg/j!、ホルマリン30mg/l及び
ロツセル塩6,400mg/βを含み、且つ48%苛性
ソーダでPH12,5に調整したメツキ廃液に、銅濃度
の2倍量のハイドロサルファイドを撹拌しながら35℃
で添加したところ、赤銅色の金属銅の沈殿を生成した。Example 1 Copper 1,300mg/j! , 30 mg/l of formalin and 6,400 mg/β of Rothsell salt, and adjusted to pH 12.5 with 48% caustic soda, was heated at 35°C while stirring twice the amount of hydrosulfide as the copper concentration.
When added, a copper-colored precipitate of metallic copper was produced.
2時間静置後、濾過してケ−りを得た(以下、ここで得
たケークをケタAと呼称する)。After standing still for 2 hours, it was filtered to obtain a cake (hereinafter, the cake obtained here will be referred to as Keta A).
他方、ニッケル2,800mg/j2.水素化ホウ素ナ
トリウム140mg/II!及びEDTA2.200m
g/j2を含むPH8−5のメツキ廃液を48%苛性ソ
ーダを用いてPH12,Oに調整しlこ。On the other hand, nickel 2,800mg/j2. Sodium borohydride 140mg/II! and EDTA2.200m
The plating waste liquid with a pH of 8-5 containing g/j2 was adjusted to pH 12.0 using 48% caustic soda.
次いてこのニッケル廃液81.000部に対して上記で
得たケークA1.5部を撹拌しなから30℃で添加し、
2時間静置後、濾過して緑色のケークを得た。Next, 1.5 parts of cake A obtained above was added to 81.000 parts of this nickel waste liquid at 30°C without stirring,
After standing for 2 hours, it was filtered to obtain a green cake.
濾液のニッケル濃度は比色定量した結果3「IIg/β
であり、本発明が金属錯体を含有する廃水の処理方法と
して極めて有効であることを確認した。The nickel concentration of the filtrate was determined by colorimetry and was found to be 3 "IIg/β
Therefore, it was confirmed that the present invention is extremely effective as a method for treating wastewater containing metal complexes.
方、濾別したケークの中のニッケル分は分析の結果43
%であった。On the other hand, the nickel content in the filtered cake was analyzed as 43
%Met.
実施例2
実施例1と同じ組成のニッケルメッキ廃液を20℃に維
持しながら48%苛性ソーダでPH12゜0に調整した
。次いでこの廃液量1.000容量部に対し実施例1で
得たケークAO,l容量部と、溶存ニッケル1重量部l
こ対してハイドロサルファイド0.5重量部を添加して
同温度で撹拌反応させた。10時間静置後、濾過して緑
色のケタを得た。濾過のニッケル濃度を比色定量した結
果2mg/βであり、本処理方法がニッケル錯体含有廃
液の処理に優れていることがわかる。Example 2 A nickel plating waste solution having the same composition as in Example 1 was maintained at 20°C and adjusted to pH 12°0 with 48% caustic soda. Next, to 1.000 parts by volume of this waste liquid, 1 part by volume of the cake AO obtained in Example 1 and 1 part by weight of dissolved nickel were added.
To this, 0.5 parts by weight of hydrosulfide was added and reacted with stirring at the same temperature. After standing still for 10 hours, it was filtered to obtain green particles. The nickel concentration in the filtration was colorimetrically determined to be 2 mg/β, indicating that this treatment method is excellent in treating waste liquid containing nickel complexes.
実施例3
銅1.800mg/j2.ホルマリン3.5mg/j2
及びロツセル塩6.50On+g/Aを含んだメツキ廃
液を48%苛性ソーダでPH12,0に調整し35℃に
維持した。Example 3 Copper 1.800mg/j2. Formalin 3.5mg/j2
A plating waste solution containing 6.50 On+g/A of Rothsell's salt was adjusted to pH 12.0 with 48% caustic soda and maintained at 35°C.
このメツキ廃液量1,000容量部に対し、実施例1で
得たケークAの乾燥粉末0.05容量部加え撹拌反応さ
せた。2時間静置後、濾過して暗赤色のケークを得た。To 1,000 parts by volume of this plating waste liquid, 0.05 parts by volume of the dry powder of Cake A obtained in Example 1 was added and reacted with stirring. After standing for 2 hours, it was filtered to obtain a dark red cake.
濾液の銅濃度を比色定量した結果1mg//2であり、
本処理方法か銅錯体含有廃液の処理に優れていることを
確認した。一方、濾別したケークの銅分は分析の結果4
7%であった。As a result of colorimetric determination of the copper concentration of the filtrate, it was 1 mg//2,
It was confirmed that this treatment method is excellent in treating waste liquid containing copper complexes. On the other hand, the copper content of the filtered cake was analyzed as 4
It was 7%.
実施例4
硝酸銀1,400mg/β、38%ホルマリン1mj2
/11アルコール50 +nll/ j2及びアンモニ
アを含んだPH8,7のメツキ廃液に48%苛性ソーダ
を用いてPH11,5に調整した。次いで28℃に保っ
たメツキ廃液1000容量部に対して実施例Iで得たケ
ークA0.6容量部を撹拌しながら添加し2時間静置し
て、灰色の沈殿物を得た。Example 4 Silver nitrate 1,400 mg/β, 38% formalin 1 mj2
/11 alcohol 50 +nll/j2 and ammonia-containing plating waste liquid with a pH of 8.7 was adjusted to pH 11.5 using 48% caustic soda. Next, 0.6 parts by volume of the cake A obtained in Example I was added to 1000 parts by volume of the plating waste liquid kept at 28°C with stirring, and the mixture was allowed to stand for 2 hours to obtain a gray precipitate.
その後、濾過して濾液の銀濃度を比色定量した結果2+
ng / l以下であり、本方法が銀メツキ廃液の処理
に適した方法であることを確認した。After that, it was filtered and the silver concentration of the filtrate was colorimetrically determined.
ng/l or less, confirming that this method is suitable for treating silver plating waste liquid.
実施例5
コバルト2 、000 mg / 1. 、次亜1,1
7酸5.000mg/l、クエン酸ソーダ4,500m
g/β及び硫酸アンモニウム10.000mg/l ヲ
含み、且つ48%苛性ソーダでPH12,2に調整した
メツキ廃液を38℃に保ちながら、メツキ廃液1,00
0容量部に対して実施例1で得たケークAl容量部を撹
拌しなから添加して反応させた。Example 5 Cobalt2, 000 mg/1. , Dia 1,1
7 acid 5.000mg/l, sodium citrate 4,500m
g/β and ammonium sulfate 10.000 mg/l, and the pH was adjusted to 12.2 with 48% caustic soda.
To 0 part by volume, part by volume of the cake Al obtained in Example 1 was added without stirring to cause a reaction.
2時間静置後、濾過して赤褐色のケークを得た。After standing for 2 hours, it was filtered to obtain a reddish-brown cake.
濾液のコバルト濃度を比色定量した結果2 mg /!
以下であり、本方法がコバルトメツキ廃液の処理に適し
た方法であることを確認した。The cobalt concentration of the filtrate was measured colorimetrically and was found to be 2 mg/!
It was confirmed that this method is suitable for treating cobalt plating waste liquid.
実施例6
塩化金2,500mg/β、酒石酸6,800mg/l
及び苛性ソーダ28 tng/ 1を含むPH8,6の
メツキ廃液を48%苛性ソーダでPH11,5に調整し
た。Example 6 Gold chloride 2,500mg/β, tartaric acid 6,800mg/l
The plating waste liquid with a pH of 8.6 and containing 28 tng/1 of caustic soda was adjusted to pH 11.5 with 48% caustic soda.
次いで25℃に保ったメツキ廃液1,000容量部に対
して実施例1で得たケークAO95容量部撹拌しながら
添加して全単体を沈殿させた。Next, 95 parts by volume of the cake AO obtained in Example 1 was added to 1,000 parts by volume of plating waste liquid kept at 25 DEG C. with stirring to precipitate all the elements.
8時間静置後、濾過して金のケークを得た。濾過中の全
濃度を比色定量した結果1mg//2以下であり、本方
法が処理方法として極めて効果のあることを確認した。After standing for 8 hours, it was filtered to obtain a gold cake. As a result of colorimetric determination of the total concentration during filtration, it was less than 1 mg//2, confirming that this method is extremely effective as a treatment method.
比較例1
ニッケル2,800mg/β、水素化ホウ素ナトリウム
140mg//!及びEDTA2,200mg/βを含
むP H8,5のメツキ廃液を48%苛性ツタを用いて
PH12,0に調整した。Comparative Example 1 Nickel 2,800mg/β, sodium borohydride 140mg//! and EDTA 2,200 mg/β and pH 8.5 was adjusted to pH 12.0 using 48% caustic ivy.
次いで、ニッケル濃度の5倍量のハイドロサルファイド
を添加して35℃で反応させた。2時間静置後濾過して
黒色のケークを得た(ここで得たケークをケークBと呼
称する)。次いで銅1.300mg/J、ホルマリン3
0IIg/It及びロツセル塩6,400mg/lを含
み、かつ48%苛性ソータでPH12,Oに調整し35
℃に維持したメツキ廃液1,000容量部に対して、先
に得たケ−りB4容量部を撹拌しながら添加した。Next, hydrosulfide in an amount 5 times the nickel concentration was added and reacted at 35°C. After standing for 2 hours, it was filtered to obtain a black cake (the cake obtained here is referred to as cake B). Next, copper 1.300mg/J, formalin 3
0 IIg/It and 6,400 mg/l of Lotusel salt, and adjusted to pH 12,0 with a 48% caustic sorter.
To 1,000 parts by volume of the plating waste liquid maintained at .degree. C., 4 parts by volume of the cake B obtained earlier was added with stirring.
20時間静置後も銅の沈殿物が得られず不適であること
を確認した。Even after standing still for 20 hours, no copper precipitate was obtained, confirming that the product was unsuitable.
比較例2
ニッケル2.800+og/ R1水素化ホウ素ナトリ
ウム1401og/ l及びEDTA2.200mg/
βを含むP H8,5のメツキ廃液を48%苛性ツタを
用いてPH12゜0に調整した。この液を40℃に保ち
ながら比較例1で得たケークBをメツキ廃液1.000
容量部に対してl容量部と溶存ニッケル1重量部に対し
ハイドロサルファイド0.5重量部を撹拌しながら添加
した。Comparative Example 2 Nickel 2.800+og/R1 sodium borohydride 1401og/l and EDTA 2.200mg/l
A plating waste solution containing β with a pH of 8.5 was adjusted to pH 12.0 using 48% caustic ivy. While maintaining this liquid at 40°C, the cake B obtained in Comparative Example 1 was mixed with 1.000% of the waste liquid.
1 volume part per volume part and 0.5 parts by weight of hydrosulfide per 1 part by weight of dissolved nickel were added with stirring.
20時間静置後、少量の沈殿を生成した上澄液のニッケ
ル濃度を比色定量した結果2,500mg/lあり、廃
液処理に適していないことを確認しIこ。After being allowed to stand still for 20 hours, the nickel concentration of the supernatant liquid, which produced a small amount of precipitate, was colorimetrically determined and found to be 2,500 mg/l, which confirmed that it was not suitable for waste liquid treatment.
然迷
以上詳述したように、本発明は銅メツキ廃液を苛性アル
カリでPH11,0以上に調整し、次いでハイドロサル
ファイドを添加して、銅及び硫化銅の沈殿物を得、この
沈殿物を、メツキ工場から発生する銅、ニッケル、コバ
ルト、銀、金等とキレート剤との錯体を含有したメツキ
廃液に苛性アルカリでPH11,0以上、好ましくはP
H11,0〜13.0に調整後、メツキ廃液1.000
容量部に対して0.1〜1容量部の割合で単独で又は亜
二チオン酸ナトリウムを併せ添加し、これによって錯体
を分解し金属単体又は金属塩類として沈殿させ、然る後
濾別することにより濾液の重金属濃度を工場排出規準値
以下に処理するものであり、処理費用が少なく且つ作業
性の良好なメツキ廃水処理方法である。As detailed above, in the present invention, copper plating waste liquid is adjusted to pH 11.0 or higher with caustic alkali, then hydrosulfide is added to obtain a precipitate of copper and copper sulfide, and this precipitate is A caustic alkali is applied to the metallurgical waste liquid containing a complex of copper, nickel, cobalt, silver, gold, etc. and a chelating agent generated from the metallurgical factory to a pH of 11.0 or higher, preferably P.
After adjusting to H11.0 to 13.0, the waste liquid was 1.000
Adding sodium dithionite alone or in combination at a ratio of 0.1 to 1 part by volume to part by volume, thereby decomposing the complex and precipitating it as an elemental metal or a metal salt, and then filtering it out. This method reduces the heavy metal concentration of the filtrate to below the factory discharge standard value, and is a method for treating plating wastewater with low treatment costs and good workability.
Claims (3)
上に調整した後、溶存銅1重量部に対して少なくとも1
重量部の亜二チオン酸ナトリウムで処理することにより
得られる沈殿物0.1〜1容量部を、銅、ニッケル、コ
バルト、銀、金等の金属錯体含む苛性アルカリでPH1
1以上に調整した廃液1,000重量部に添加して反応
せしめ、生ずる沈殿を分離することを特徴とする廃液の
処理方法。(1) After adjusting the waste liquid containing the copper complex to pH 11 or higher with caustic alkali, at least 1 part by weight of dissolved copper is added.
0.1 to 1 part by volume of the precipitate obtained by treatment with part by weight of sodium dithionite is heated to pH 1 with a caustic alkali containing a metal complex such as copper, nickel, cobalt, silver, or gold.
1. A method for treating a waste liquid, which comprises adding the waste liquid to 1,000 parts by weight of the waste liquid adjusted to a concentration of 1 or more, causing a reaction, and separating the resulting precipitate.
加して得られる沈殿物0.1〜1重量部と溶存金属1重
量部に対し亜二チオン酸ナトリウム0.05〜1重量部
とを併用する特許請求の範囲第1項記載の方法。(2) 0.1 to 1 part by weight of a precipitate obtained by adding sodium dithionite to a waste solution containing a copper complex and 0.05 to 1 part by weight of sodium dithionite per 1 part by weight of dissolved metal. The method according to claim 1, which is used in combination with.
の範囲第1項記載の方法。(3) The method according to claim 1, wherein the reaction is carried out at a temperature of at least 20°C.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP17188888A JPH0221995A (en) | 1988-07-12 | 1988-07-12 | Treatment of waste solution |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP17188888A JPH0221995A (en) | 1988-07-12 | 1988-07-12 | Treatment of waste solution |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH0221995A true JPH0221995A (en) | 1990-01-24 |
Family
ID=15931661
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP17188888A Pending JPH0221995A (en) | 1988-07-12 | 1988-07-12 | Treatment of waste solution |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH0221995A (en) |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
FR2669620A1 (en) * | 1990-11-22 | 1992-05-29 | Sandoz Sa | NEW PROCESS FOR RECOVERING COPPER IN INDUSTRIAL WASTEWATER CONTAINING IT. |
JP2009120921A (en) * | 2007-11-16 | 2009-06-04 | Niigata Univ | Method and apparatus for recovering nickel from nickel-containing aqueous solution |
JP2015155084A (en) * | 2014-02-20 | 2015-08-27 | 栗田工業株式会社 | Method and apparatus for treating water containing ammonia |
JP2018158325A (en) * | 2017-03-24 | 2018-10-11 | Dowaテクノロジー株式会社 | Method for treating liquid to be treated and method for recovering silver |
-
1988
- 1988-07-12 JP JP17188888A patent/JPH0221995A/en active Pending
Cited By (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
FR2669620A1 (en) * | 1990-11-22 | 1992-05-29 | Sandoz Sa | NEW PROCESS FOR RECOVERING COPPER IN INDUSTRIAL WASTEWATER CONTAINING IT. |
JP2009120921A (en) * | 2007-11-16 | 2009-06-04 | Niigata Univ | Method and apparatus for recovering nickel from nickel-containing aqueous solution |
JP2015155084A (en) * | 2014-02-20 | 2015-08-27 | 栗田工業株式会社 | Method and apparatus for treating water containing ammonia |
WO2015125667A1 (en) * | 2014-02-20 | 2015-08-27 | 栗田工業株式会社 | Method and apparatus for treating ammonia-containing water |
US10550026B2 (en) | 2014-02-20 | 2020-02-04 | Kurita Water Industries Ltd. | Method for treating ammonia-containing water |
JP2018158325A (en) * | 2017-03-24 | 2018-10-11 | Dowaテクノロジー株式会社 | Method for treating liquid to be treated and method for recovering silver |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
US3957505A (en) | Gold reclamation process | |
KR960009172B1 (en) | Method for concurrent production of copper powder and a metal chloride | |
US5389262A (en) | Process for removing heavy metals from solutions with ferrous dithionite and hydroxide | |
CA1223375A (en) | Treating cyanide-containing effluents | |
EP0355418B1 (en) | Process for the treatment of effluents containing cyanide and toxid metals, using hydrogen peroxide and trimercaptotriazine | |
US4172785A (en) | Process for the separation of Cu++ -ions from sewage, waste water and aqueous solutions | |
EP0308175B1 (en) | Stripping and recovery of dichromate in electrolytic chlorate systems | |
CA1090583A (en) | Stepwise process for recovering precious metals from solution | |
USH1852H (en) | Waste treatment of metal plating solutions | |
JPH0221995A (en) | Treatment of waste solution | |
JP2013056328A (en) | Treatment method and treatment apparatus of cyanide-containing water | |
JPH01224091A (en) | Treatment of waste containing cyanogen compound | |
CN114933352A (en) | Treatment method of cyanide-containing wastewater | |
JPS6339693A (en) | Method for treating waste water containing cyanogen | |
CN108689427A (en) | It is a kind of to produce the method and its application that feed grade zinc oxide is recycled in mother liquor from basic zinc chloride | |
NZ203055A (en) | Removing copper from cyanide-containing waste water | |
KR20000035098A (en) | Process for preparing usable products from an impure ferric sulfate solution | |
JPS637894A (en) | Treatment of waste liquid | |
JPH0475285B2 (en) | ||
JP4423734B2 (en) | Cyanide wastewater treatment method | |
JPS60118288A (en) | Water treating method | |
RU2049544C1 (en) | Method of production of sorbent for sewage treatment from heavy metal ions | |
KR100434637B1 (en) | Process for preparing cuprous cynide from cupric chloride waste | |
CN113060860B (en) | Treatment method of chemical nickel wastewater | |
US4324666A (en) | Method of removing ferrocyanide ions from rinse water of an alkaline cyanide metal plating process |