JPH04330991A - Treatment of heavy metal containing waste water and treating agent therefor - Google Patents
Treatment of heavy metal containing waste water and treating agent thereforInfo
- Publication number
- JPH04330991A JPH04330991A JP3099223A JP9922391A JPH04330991A JP H04330991 A JPH04330991 A JP H04330991A JP 3099223 A JP3099223 A JP 3099223A JP 9922391 A JP9922391 A JP 9922391A JP H04330991 A JPH04330991 A JP H04330991A
- Authority
- JP
- Japan
- Prior art keywords
- heavy metal
- wastewater
- waste water
- heavy metals
- treatment
- 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
- 229910001385 heavy metal Inorganic materials 0.000 title claims abstract description 52
- 239000002351 wastewater Substances 0.000 title claims abstract description 46
- 239000003795 chemical substances by application Substances 0.000 title description 3
- 229920002873 Polyethylenimine Polymers 0.000 claims abstract description 21
- YXIWHUQXZSMYRE-UHFFFAOYSA-N 1,3-benzothiazole-2-thiol Chemical compound C1=CC=C2SC(S)=NC2=C1 YXIWHUQXZSMYRE-UHFFFAOYSA-N 0.000 claims abstract description 19
- 150000003839 salts Chemical class 0.000 claims abstract description 19
- 238000000034 method Methods 0.000 claims description 27
- 238000007747 plating Methods 0.000 claims description 11
- 238000001556 precipitation Methods 0.000 claims description 5
- 239000004480 active ingredient Substances 0.000 claims description 2
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 abstract description 5
- 244000144992 flock Species 0.000 abstract 1
- 239000007788 liquid Substances 0.000 description 10
- 239000000203 mixture Substances 0.000 description 8
- 238000004062 sedimentation Methods 0.000 description 7
- 239000000126 substance Substances 0.000 description 7
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 description 6
- 239000010949 copper Substances 0.000 description 6
- 229910052802 copper Inorganic materials 0.000 description 6
- 230000000694 effects Effects 0.000 description 6
- 150000002500 ions Chemical class 0.000 description 6
- VLDHWMAJBNWALQ-UHFFFAOYSA-N sodium;3h-1,3-benzothiazole-2-thione Chemical compound [Na+].C1=CC=C2SC(S)=NC2=C1 VLDHWMAJBNWALQ-UHFFFAOYSA-N 0.000 description 6
- 238000003756 stirring Methods 0.000 description 6
- -1 dithiocarbamate compound Chemical class 0.000 description 5
- 239000011734 sodium Substances 0.000 description 5
- 239000007864 aqueous solution Substances 0.000 description 4
- 238000001479 atomic absorption spectroscopy Methods 0.000 description 4
- 239000003814 drug Substances 0.000 description 4
- 229940079593 drug Drugs 0.000 description 4
- 238000009472 formulation Methods 0.000 description 4
- 238000000926 separation method Methods 0.000 description 4
- 239000006228 supernatant Substances 0.000 description 4
- KWYUFKZDYYNOTN-UHFFFAOYSA-M Potassium hydroxide Chemical compound [OH-].[K+] KWYUFKZDYYNOTN-UHFFFAOYSA-M 0.000 description 3
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 3
- 238000002156 mixing Methods 0.000 description 3
- VSCWAEJMTAWNJL-UHFFFAOYSA-K aluminium trichloride Chemical compound Cl[Al](Cl)Cl VSCWAEJMTAWNJL-UHFFFAOYSA-K 0.000 description 2
- 230000000052 comparative effect Effects 0.000 description 2
- 150000001875 compounds Chemical class 0.000 description 2
- 150000004679 hydroxides Chemical class 0.000 description 2
- 229920000642 polymer Polymers 0.000 description 2
- 229910052979 sodium sulfide Inorganic materials 0.000 description 2
- GRVFOGOEDUUMBP-UHFFFAOYSA-N sodium sulfide (anhydrous) Chemical compound [Na+].[Na+].[S-2] GRVFOGOEDUUMBP-UHFFFAOYSA-N 0.000 description 2
- 150000004763 sulfides Chemical class 0.000 description 2
- 238000010998 test method Methods 0.000 description 2
- 238000000108 ultra-filtration Methods 0.000 description 2
- GSFSVEDCYBDIGW-UHFFFAOYSA-N 2-(1,3-benzothiazol-2-yl)-6-chlorophenol Chemical compound OC1=C(Cl)C=CC=C1C1=NC2=CC=CC=C2S1 GSFSVEDCYBDIGW-UHFFFAOYSA-N 0.000 description 1
- OCVLSHAVSIYKLI-UHFFFAOYSA-N 3h-1,3-thiazole-2-thione Chemical class SC1=NC=CS1 OCVLSHAVSIYKLI-UHFFFAOYSA-N 0.000 description 1
- QGZKDVFQNNGYKY-UHFFFAOYSA-O Ammonium Chemical compound [NH4+] QGZKDVFQNNGYKY-UHFFFAOYSA-O 0.000 description 1
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 description 1
- DGAQECJNVWCQMB-PUAWFVPOSA-M Ilexoside XXIX Chemical compound C[C@@H]1CC[C@@]2(CC[C@@]3(C(=CC[C@H]4[C@]3(CC[C@@H]5[C@@]4(CC[C@@H](C5(C)C)OS(=O)(=O)[O-])C)C)[C@@H]2[C@]1(C)O)C)C(=O)O[C@H]6[C@@H]([C@H]([C@@H]([C@H](O6)CO)O)O)O.[Na+] DGAQECJNVWCQMB-PUAWFVPOSA-M 0.000 description 1
- WHXSMMKQMYFTQS-UHFFFAOYSA-N Lithium Chemical compound [Li] WHXSMMKQMYFTQS-UHFFFAOYSA-N 0.000 description 1
- ZLMJMSJWJFRBEC-UHFFFAOYSA-N Potassium Chemical compound [K] ZLMJMSJWJFRBEC-UHFFFAOYSA-N 0.000 description 1
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 150000007513 acids Chemical class 0.000 description 1
- 238000004220 aggregation Methods 0.000 description 1
- 230000002776 aggregation Effects 0.000 description 1
- 239000003513 alkali Substances 0.000 description 1
- 229910052783 alkali metal Inorganic materials 0.000 description 1
- 150000001340 alkali metals Chemical class 0.000 description 1
- 229910052785 arsenic Inorganic materials 0.000 description 1
- RQNWIZPPADIBDY-UHFFFAOYSA-N arsenic atom Chemical compound [As] RQNWIZPPADIBDY-UHFFFAOYSA-N 0.000 description 1
- 239000000440 bentonite Substances 0.000 description 1
- 229910000278 bentonite Inorganic materials 0.000 description 1
- SVPXDRXYRYOSEX-UHFFFAOYSA-N bentoquatam Chemical compound O.O=[Si]=O.O=[Al]O[Al]=O SVPXDRXYRYOSEX-UHFFFAOYSA-N 0.000 description 1
- 229910052793 cadmium Inorganic materials 0.000 description 1
- BDOSMKKIYDKNTQ-UHFFFAOYSA-N cadmium atom Chemical compound [Cd] BDOSMKKIYDKNTQ-UHFFFAOYSA-N 0.000 description 1
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 description 1
- 239000000920 calcium hydroxide Substances 0.000 description 1
- 229910001861 calcium hydroxide Inorganic materials 0.000 description 1
- 125000002091 cationic group Chemical group 0.000 description 1
- 238000004140 cleaning Methods 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 125000004119 disulfanediyl group Chemical group *SS* 0.000 description 1
- 239000012990 dithiocarbamate Substances 0.000 description 1
- 238000005189 flocculation Methods 0.000 description 1
- 230000016615 flocculation Effects 0.000 description 1
- 238000005188 flotation Methods 0.000 description 1
- 239000004088 foaming agent Substances 0.000 description 1
- 229910000037 hydrogen sulfide Inorganic materials 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-M hydroxide Chemical compound [OH-] XLYOFNOQVPJJNP-UHFFFAOYSA-M 0.000 description 1
- 239000010842 industrial wastewater Substances 0.000 description 1
- 229910052744 lithium Inorganic materials 0.000 description 1
- 159000000003 magnesium salts Chemical class 0.000 description 1
- QSHDDOUJBYECFT-UHFFFAOYSA-N mercury Chemical compound [Hg] QSHDDOUJBYECFT-UHFFFAOYSA-N 0.000 description 1
- 229910052753 mercury Inorganic materials 0.000 description 1
- 238000010979 pH adjustment Methods 0.000 description 1
- 229910052700 potassium Inorganic materials 0.000 description 1
- 239000011591 potassium Substances 0.000 description 1
- 238000002360 preparation method Methods 0.000 description 1
- 238000003672 processing method Methods 0.000 description 1
- 229910052708 sodium Inorganic materials 0.000 description 1
- HYHCSLBZRBJJCH-UHFFFAOYSA-M sodium hydrosulfide Chemical compound [Na+].[SH-] HYHCSLBZRBJJCH-UHFFFAOYSA-M 0.000 description 1
- HYHCSLBZRBJJCH-UHFFFAOYSA-N sodium polysulfide Chemical compound [Na+].S HYHCSLBZRBJJCH-UHFFFAOYSA-N 0.000 description 1
- 239000011593 sulfur Substances 0.000 description 1
- 229910052717 sulfur Inorganic materials 0.000 description 1
- 238000004065 wastewater treatment Methods 0.000 description 1
Landscapes
- Separation Of Suspended Particles By Flocculating Agents (AREA)
- Removal Of Specific Substances (AREA)
Abstract
Description
【0001】0001
【産業上の利用分野】この発明は、重金属を含有する廃
水の処理方法及び処理剤に関する。さらに詳しくは、カ
ドミウム,銅,鉛,水銀等を含有する重金属含有廃水中
の重金属を簡易な凝集沈澱法により効率的に除去する方
法及びそのための薬剤に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention This invention relates to a method and agent for treating wastewater containing heavy metals. More specifically, the present invention relates to a method for efficiently removing heavy metals from heavy metal-containing wastewater containing cadmium, copper, lead, mercury, etc. by a simple coagulation-sedimentation method, and a drug for the same.
【0002】0002
【従来の技術】従来から、重金属を含有する種々な廃水
の処理方法の一つとして、ジチオカルバミン酸化合物又
はメルカプトベンゾチアゾール化合物を添加して不溶性
の重金属塩を形成させる方法が知られている(特開昭5
2−136279号公報参照)。しかし、上記不溶性の
重金属塩のフロックは、小さく軽いため容易に沈降しな
い。ゆえに、上記公報の発明においては、さらに、カチ
オン系の起泡剤を添加し て浮上分離法によって固液
分離を行う必要があり、汎用性に欠ける問題があった
。
また、ことに、メッキ工場からは様々な重金属を含有す
る廃水が排出されるが、特に化学会社の銅メッキ工場か
らはpHが高く、アンミン錯塩を多量に含んだ廃水が排
出される。このような廃水について上記方法を適用した
場合には、不溶性のフロックが形成され難く、実用に供
し得ないという問題があった。重金属を含有する種々な
廃水の他の一般的な処理方法は、適正なpH下で難溶性
の水酸化物や硫化物を生成させ、無機凝集剤による凝集
に引続き高分子凝集剤による凝集処理をし、クラリファ
イアーにより処理水からフロックを分離する方法である
。上記方法の例として、特開昭60−187394号公
報においては、化学会社の銅メッキ廃水に硫化ナトリウ
ム,ジメチルジチオカルバミン酸ナトリウム等の硫黄を
含む化合物を添加し、pHを7に調整し、次いでポリ塩
化アルミニウム、ベントナイト及び高分子凝集剤を添加
した後、固液分離する方法が開示されている。この方法
においては、重金属類の水酸化物及び硫化物形成時の最
適pH範囲と無機凝集剤添加時の最適pH範囲とが異な
り、無機凝集剤添加時の最適pH範囲は一般に低い値で
あるため凝集効果が不充分となりクラリファイアーで充
分な分離ができにくくなる等の欠点を有する。また、特
公昭64−3549号公報においては、ポリエチレンイ
ミンに少なくとも1個のジチオ基又はその塩類を有する
化合物と、硫化ソーダ,多硫化ソーダ,水硫化ソーダよ
り選ばれる少なくとも1種を併用添加する方法が開示さ
れている。
上記、特公昭64−3549号公報記載の方法は、凝集
沈澱法により重金属類を処理できるため好ましいが、各
種硫化ソーダ類が廃水中に含有されpHの低下により、
硫化水素が発生する危惧があり、公害面から好ましくな
い。また、平成3年3月15日、日本水処理技術研究会
発行の「水処理技術」第32巻,第3号,第1〜10頁
には、重金属含有廃水を水酸化物として沈澱させた後、
無機凝集剤及び高分子凝集剤を添加してフロックを形成
させ、その後、限外濾過する方法が開示されている。上
記、水処理技術に記載の発明は、限外濾過法によるため
処理設備が大規模になるとともに操作も煩雑になる欠点
があるとともに、Cd(II)を含有する廃水について
は、その効果が不充分となる欠点を有する。[Prior Art] Conventionally, as one of the methods for treating various wastewater containing heavy metals, a method has been known in which a dithiocarbamate compound or a mercaptobenzothiazole compound is added to form an insoluble heavy metal salt (especially Kaisho 5
2-136279). However, the insoluble heavy metal salt flocs are small and light and do not easily settle. Therefore, in the invention disclosed in the above publication, it was necessary to further add a cationic foaming agent and perform solid-liquid separation by flotation separation, which resulted in the problem of lack of versatility.
. In particular, plating factories discharge wastewater containing various heavy metals, and copper plating factories of chemical companies in particular discharge wastewater that has a high pH and contains large amounts of ammine complex salts. When the above method is applied to such wastewater, there is a problem in that insoluble flocs are difficult to form and the method cannot be put to practical use. Another common treatment method for various types of wastewater containing heavy metals is to generate poorly soluble hydroxides and sulfides at an appropriate pH, and then perform flocculation treatment using an inorganic flocculant followed by a polymer flocculant. In this method, flocs are separated from the treated water using a clarifier. As an example of the above method, in JP-A-60-187394, compounds containing sulfur such as sodium sulfide and sodium dimethyldithiocarbamate are added to the copper plating wastewater of a chemical company, the pH is adjusted to 7, and then A method is disclosed in which solid-liquid separation is performed after adding aluminum chloride, bentonite, and a polymer flocculant. In this method, the optimum pH range when hydroxides and sulfides of heavy metals are formed is different from the optimum pH range when adding an inorganic flocculant, and the optimum pH range when adding an inorganic flocculant is generally a low value. It has drawbacks such as insufficient aggregation effect and difficulty in sufficient separation using a clarifier. Furthermore, Japanese Patent Publication No. 64-3549 discloses a method in which a compound having at least one dithio group or a salt thereof and at least one selected from sodium sulfide, sodium polysulfide, and sodium hydrogen sulfide are added together to polyethyleneimine. is disclosed. The method described in Japanese Patent Publication No. 64-3549 is preferable because heavy metals can be treated by the coagulation-sedimentation method, but various soda sulfides are contained in the wastewater and the pH decreases.
There is a risk of hydrogen sulfide being generated, which is undesirable from a pollution standpoint. In addition, in "Water Treatment Technology" Vol. 32, No. 3, pp. 1-10, published by the Japan Water Treatment Technology Study Group on March 15, 1991, wastewater containing heavy metals is precipitated as hydroxide. rear,
A method is disclosed in which flocs are formed by adding an inorganic flocculant and a polymeric flocculant, followed by ultrafiltration. The above-mentioned invention described in water treatment technology has the disadvantage that the treatment equipment is large-scale and the operation is complicated because it uses an ultrafiltration method, and it is not effective for wastewater containing Cd(II). It has enough drawbacks.
【0003】0003
【発明が解決しようとする課題】叙上の事情に鑑み、こ
の発明は、重金属含有廃水を容易な凝集沈澱法により効
率的に処理することをその目的とするものである。そし
て、特に従来その処理が困難と考えられていた、pHが
高く、アンミン錯塩を多量に含んだ化学銅メッキ工場か
ら排出される廃水を容易な凝集沈澱法により効率的に処
理することをその一つの目的とするものである。SUMMARY OF THE INVENTION In view of the above circumstances, an object of the present invention is to efficiently treat heavy metal-containing wastewater by a simple coagulation-sedimentation method. One of our efforts was to efficiently treat wastewater discharged from chemical copper plating plants, which has a high pH and contains a large amount of ammine complex salts, by an easy coagulation-sedimentation method, which was previously thought to be difficult to treat. It is intended to serve one purpose.
【0004】0004
【課題を解決するための手段】この発明の発明者らは、
上記観点より、メルカプトチアゾール系化合物を用いた
凝集沈殿法について鋭意研究を行なった。そして、その
結果、有機凝集剤の一つであるポリエチレンイミンと併
用することにより、とくに煩雑な処理を行なうことなく
効率よく重金属類を沈殿除去でき、さらに驚くべきこと
に、ジチオカルバミン酸類と不溶性塩を形成せず処理が
困難であった重金属類のアンミン錯塩の形態を含む廃水
に対しても、メルカプトベンゾチアゾール化合物とポリ
エチレンイミンとを併用することにより凝集沈殿法によ
り重金属類を容易に除去できる事実を見出した。かくし
て、この発明によれば、重金属含有廃水に、メルカプト
ベンゾチアゾール又はその水溶性塩とポリエチレンイミ
ンとを添加することにより重金属含有フロックを形成し
、これを沈澱除去することを特徴とする重金属含有廃水
の処理方法が提供される。この発明に用いられるメルカ
プトベンゾチアゾール又はその水溶性塩としては、メル
カプトベンゾチアゾール及びそのアルカリ金属(リチウ
ム,ナトリウム,カリウム等)塩,マグネシウム塩,ア
ンモニウムあるいはアミン塩があげられる。この発明に
用いられるポリエチレンイミンとしては水溶性のものが
用いられ、分子量(Mw)300〜750000のポリ
エチレンイミンが適している。中でも、分子量5000
0以上のものを使用するのが、形成されたフロックが大
きくなり沈降性がよくなり重金属類の除去効果の点で特
に好ましい。メルカプトベンゾチアゾール又はその水溶
性塩とポリエチレンイミンとを重金属含有廃水に添加す
る場合、両者を混合して一液製剤として添加するのが作
業の上で好ましいが、前者を先に添加し、その後、後者
を添加してもよく、添加順序を逆にしても重金属類の除
去効果ははぼ同等である。この場合、メルカプトベンゾ
チアゾール又はその水溶性塩とポリエチレンイミンとを
20:1〜1:5の配合割合(好ましくは10:1〜1
:1の配合割合)で、併用添加するのが適している。そ
して、廃水中に存在する重金属イオンの総量に対して、
メルカプトベンゾチアゾール又はその水溶性塩が0.1
〜5倍モル、好ましくは0.2〜3倍モルとなる量を添
加するのがよい。上記配合割合以外では、他方の有効成
分が無駄になり添加量が増加するため好ましくない。ま
た、添加量が上記範囲より少ないと重金属類の除去効果
が充分ではなくなるため好ましくなく、添加量を上記範
囲より多くしても重金属類の除去効果に変化はなく経済
的ではない。この発明の処理方法は、重金属を含有しそ
のまま系外へ放出できない種々の廃水、ことに工業廃水
に適用でき、ことに、対象となる重金属としては、カド
ミウム,銅,鉛,水銀,ニッケル,クロム,砒素等があ
げられる。但し、処理される重金属含有廃水のpHが6
未満であると沈澱可能なフロックができにくくなり好ま
しくない。そして、廃水のpHが9以上の場合が重金属
類の除去効果の点で特に好ましい。従って、pH6未満
の廃水については、アルカリ(水酸化ナトリウム,水酸
化カリウム,等)を添加してpH6以上、好ましくはp
H9〜12程度に液性調整した後に実施するのが適して
いる。なお、メッキ廃水等は通常pH9以上であるので
かかるpH調整は、とくに不要であり、直接実施するこ
とができる。
このような処理により、廃水中に重金属類を含有するフ
ロックが迅速に形成され、経時的にこれが沈降する。従
って、フロックの形成後、公知の沈殿除去法によってこ
れを除去することにより廃水の処理が完了する。そして
、かかる処理により、種々の重金属の除去処理が可能と
なり、ことに困難なメッキ廃水中の重金属類の除去処理
を簡便かつ効率良く行なうことができる。[Means for solving the problem] The inventors of this invention
From the above viewpoint, we conducted intensive research on the coagulation-precipitation method using mercaptothiazole compounds. As a result, by using it together with polyethyleneimine, which is an organic flocculant, heavy metals can be efficiently precipitated and removed without any complicated treatment, and even more surprisingly, dithiocarbamic acids and insoluble salts can be removed by precipitation. Even for wastewater that contains ammine complex salts of heavy metals, which are difficult to treat because they do not form, it is possible to easily remove heavy metals by the coagulation-sedimentation method by using a mercaptobenzothiazole compound and polyethyleneimine in combination. I found it. Thus, according to the present invention, heavy metal-containing flocs are formed by adding mercaptobenzothiazole or a water-soluble salt thereof and polyethyleneimine to the heavy metal-containing wastewater, and the flocs are removed by precipitation. A processing method is provided. Examples of mercaptobenzothiazole or its water-soluble salt used in this invention include mercaptobenzothiazole and its alkali metal (lithium, sodium, potassium, etc.) salts, magnesium salts, ammonium or amine salts. The polyethyleneimine used in this invention is water-soluble, and polyethyleneimine having a molecular weight (Mw) of 300 to 750,000 is suitable. Among them, molecular weight 5000
It is particularly preferable to use 0 or more in terms of the size of the formed flocs, improved sedimentation properties, and the effect of removing heavy metals. When adding mercaptobenzothiazole or its water-soluble salt and polyethyleneimine to heavy metal-containing wastewater, it is preferable to mix the two and add them as a one-component preparation, but it is preferable to add the former first, and then, The latter may be added, and even if the order of addition is reversed, the effect of removing heavy metals is almost the same. In this case, the mixing ratio of mercaptobenzothiazole or its water-soluble salt and polyethyleneimine is 20:1 to 1:5 (preferably 10:1 to 1).
It is suitable to add them together at a blending ratio of :1). And, relative to the total amount of heavy metal ions present in wastewater,
Mercaptobenzothiazole or its water-soluble salt is 0.1
It is preferable to add the amount in an amount of 5 to 5 times the mole, preferably 0.2 to 3 times the mole. Mixing ratios other than the above are not preferred because the other active ingredient is wasted and the amount added increases. Further, if the amount added is less than the above range, the effect of removing heavy metals will not be sufficient, which is not preferable, and even if the amount added is larger than the above range, the effect of removing heavy metals will not change, which is not economical. The treatment method of this invention can be applied to various types of wastewater that contain heavy metals and cannot be directly discharged outside the system, especially industrial wastewater. , arsenic, etc. However, if the pH of the heavy metal-containing wastewater to be treated is 6.
If it is less than that, it becomes difficult to form flocs that can be precipitated, which is not preferable. It is particularly preferable that the pH of the wastewater is 9 or higher in terms of the effect of removing heavy metals. Therefore, for wastewater with a pH of less than 6, add alkali (sodium hydroxide, potassium hydroxide, etc.) to raise the pH to 6 or more, preferably pH 6.
It is suitable to carry out after adjusting the liquid property to about H9-12. Note that since plating wastewater and the like usually have a pH of 9 or higher, such pH adjustment is not particularly necessary and can be carried out directly. Such treatment rapidly forms flocs containing heavy metals in the wastewater, which settle out over time. Therefore, after the flocs are formed, the wastewater treatment is completed by removing the flocs by a known precipitation removal method. Through such treatment, various heavy metals can be removed, and the particularly difficult process of removing heavy metals from plating wastewater can be carried out simply and efficiently.
【0005】[0005]
【実施例】この発明を以下の実施例及び比較例により説
明する。
実施例1
(試験方法)某化学会社の銅メッキ工場より排出された
下記性状を持つ重金属含有廃水をビーカーに500ml
採取し、供試薬剤を所定量添加して、所定時間120r
pmで攪拌した後、5分間静置した。この時、形成され
たフロック径を肉眼で観察した。その後上澄液100m
lを採取し、その外観を観察するとともにss濃度及び
原子吸光法により液中の重金属イオン濃度を測定した。
その結果を併せて表1に示す。EXAMPLES The present invention will be explained by the following examples and comparative examples. Example 1 (Test method) 500 ml of heavy metal-containing wastewater with the following properties discharged from a copper plating factory of a certain chemical company was placed in a beaker.
A sample was taken, a predetermined amount of the test drug was added, and the sample was heated for a predetermined period of 120 r.
After stirring at pm, the mixture was allowed to stand for 5 minutes. At this time, the diameter of the formed flocs was observed with the naked eye. Then 100m of supernatant
1 was collected, and its appearance was observed, and the ss concentration and heavy metal ion concentration in the liquid were measured by atomic absorption spectrometry. The results are also shown in Table 1.
【0006】[0006]
【表1】
表1中、No.2〜4は、この発明の実施例であり、供
試薬剤としてメルカプトベンゾチアゾールナトリウム塩
(MBT−Naと略記する)を添加し、120rpmで
15分間攪拌後、平均分子量500000のポリエチレ
ンイミン(PEI と略記する)を添加し、120rp
mで1分間攪拌した時の結果である。No.1及び5は
、比較例であり、この時は供試薬剤を添加後、120r
pm で15分間攪拌した時の結果である。また、No
.6〜11は、この発明の実施例であり、供試薬剤とし
てメルカプトベンゾチアゾールナトリウム塩(MBT−
Naと略記する)と平均分子量500000のポリエチ
レンイミン(PEI と略記する)との一液製剤品(水
溶液)を添加した後、120rpmで15分間攪拌した
時の結果である。
(廃水の性状) pH :9.5Cu++:2
68mg/l(アンミン錯塩の形態で存在)[Table 1] In Table 1, No. Examples 2 to 4 are examples of the present invention, in which mercaptobenzothiazole sodium salt (abbreviated as MBT-Na) was added as a test agent, and after stirring at 120 rpm for 15 minutes, polyethyleneimine (PEI) with an average molecular weight of 500,000 was added. ) and 120 rpm.
These are the results when stirring was performed for 1 minute at m. No. 1 and 5 are comparative examples, in which 120 r after adding the test drug.
These are the results obtained after stirring at pm for 15 minutes. Also, no
.. 6 to 11 are Examples of the present invention, in which mercaptobenzothiazole sodium salt (MBT-
These are the results obtained when a one-component formulation (aqueous solution) of polyethyleneimine (abbreviated as PEI) with an average molecular weight of 500,000 was added and stirred at 120 rpm for 15 minutes. (Properties of wastewater) pH: 9.5 Cu++: 2
68 mg/l (present in the form of ammine complex salt)
【0007
】実施例2
某メッキ工場より排出された下記性状を持つ重金属含有
廃水をビーカーに500ml採取し、供試薬剤として、
メルカプトベンゾチアゾールナトリウム塩(MBT−N
aと略記する)と平均分子量100000のポリエチレ
ンイミン(PEI と略記する)との一液製剤品(水溶
液)を所定量添加し、15分間120rpm で攪拌し
た後、5分間静置した。この時、形成されたフロック径
を肉眼で観察した。その後上澄液100mlを採取し、
その外観を観察するとともに原子吸光法により液中の重
金属イオン濃度を測定した。その結果を併せて表2に示
す。
(廃水の性状) pH :9.0Pb++:1
5mg/l
Cd++:19mg/l
(試験結果)0007
] Example 2 500 ml of heavy metal-containing wastewater discharged from a certain plating factory with the following properties was collected in a beaker, and used as a test chemical.
Mercaptobenzothiazole sodium salt (MBT-N
A predetermined amount of a one-component formulation (aqueous solution) of polyethyleneimine (abbreviated as PEI) having an average molecular weight of 100,000 was added, stirred at 120 rpm for 15 minutes, and then left to stand for 5 minutes. At this time, the diameter of the formed flocs was observed with the naked eye. After that, 100 ml of supernatant liquid was collected,
The appearance of the liquid was observed and the concentration of heavy metal ions in the liquid was measured using atomic absorption spectrometry. The results are also shown in Table 2. (Properties of wastewater) pH: 9.0Pb++: 1
5mg/l Cd++: 19mg/l (test results)
【0008】[0008]
【表2】[Table 2]
【0009】実施例3
某電気機器工場より排出された下記性状を持つ重金属含
有洗浄廃水500mlをビーカーに採取し、水酸化カル
シウムを添加して該廃液のpHを10に調整した。その
後、供試薬剤として、メルカプトベンゾチアゾールナト
リウム塩(MBT−Naと略記する)と平均分子量30
0000のポリエチレンイミン(PEI と略記する)
との一液製剤品(水溶液)を所定量添加し、15分間1
20rpm で攪拌した後、5分間静置した。この時、
形成されたフロック径を肉眼で観察した。その後上澄液
100mlを採取し、その外観を観察するとともにss
濃度及び原子吸光法により液中の重金属イオン濃度を測
定した。その結果を表3に示す。
(廃水の性状) pH :1.5Pb++:3
00mg/l
(試験結果)Example 3 500 ml of heavy metal-containing cleaning wastewater discharged from a certain electrical equipment factory and having the following properties was collected in a beaker, and calcium hydroxide was added to adjust the pH of the wastewater to 10. Thereafter, as a test drug, mercaptobenzothiazole sodium salt (abbreviated as MBT-Na) and an average molecular weight of 30
0000 polyethyleneimine (abbreviated as PEI)
Add a predetermined amount of a one-component formulation (aqueous solution) and leave it for 15 minutes.
After stirring at 20 rpm, the mixture was allowed to stand for 5 minutes. At this time,
The diameter of the formed flocs was observed with the naked eye. After that, 100 ml of supernatant liquid was collected, its appearance was observed, and ss
The concentration of heavy metal ions in the liquid was measured by concentration and atomic absorption spectrometry. The results are shown in Table 3. (Properties of wastewater) pH: 1.5Pb++: 3
00mg/l (test results)
【0010】0010
【表3】[Table 3]
【0011】実施例4
(試験方法)某メッキ工場より排出された下記性状を持
つ重金属含有廃水をビーカーに500ml採取し、供試
薬剤として、メルカプトベンゾチアゾールナトリウム塩
(MBT−Naと略記する)と平均分子量500000
のポリエチレンイミン(PEI と略記する)との一液
製剤品(水溶液)を所定量添加し、15分間120rp
m で攪拌した後、5分間静置した。この時、形成され
たフロック径を肉眼で観察した。その後上澄液100m
lを採取し、その外観を観察するとともにss濃度及び
原子吸光法により液中の重金属イオン濃度を測定した。
その結果を表4に示す。
(廃水の性状) pH :10Ni++:30
0mg/l(アンミン錯塩の形態で存在)(試験結果)Example 4 (Test method) 500 ml of heavy metal-containing wastewater discharged from a certain plating factory and having the following properties was collected in a beaker, and mercaptobenzothiazole sodium salt (abbreviated as MBT-Na) and mercaptobenzothiazole sodium salt (abbreviated as MBT-Na) were used as test chemicals. Average molecular weight 500000
A predetermined amount of a one-component formulation (aqueous solution) with polyethyleneimine (abbreviated as PEI) was added, and the mixture was heated at 120 rpm for 15 minutes.
After stirring at m, the mixture was allowed to stand for 5 minutes. At this time, the diameter of the formed flocs was observed with the naked eye. Then 100m of supernatant
1 was collected, and its appearance was observed, and the ss concentration and heavy metal ion concentration in the liquid were measured by atomic absorption spectrometry. The results are shown in Table 4. (Properties of wastewater) pH: 10Ni++: 30
0 mg/l (present in the form of ammine complex salt) (test results)
【0012】0012
【表4】[Table 4]
【0013】[0013]
【発明の効果】この発明によれば、種々の重金属含有廃
水中の重金属を簡易な凝集沈澱法により効率的に除去す
ることができる。特に、従来その処理が困難であった化
学会社の銅メッキ工場から排出されるpHが高く、アン
ミン錯塩を多量に含んだ廃水についてもpH調整せずに
処理後の重金属イオンを排出基準以下まで低減すること
ができる。According to the present invention, heavy metals in various heavy metal-containing wastewaters can be efficiently removed by a simple coagulation-sedimentation method. In particular, wastewater discharged from copper plating plants of chemical companies that has a high pH and contains a large amount of ammine complex salts, which has been difficult to treat in the past, has been treated to reduce heavy metal ions to below the emission standards without adjusting the pH. can do.
Claims (4)
チアゾール又はその水溶性塩とポリエチレンイミンとを
添加することにより重金属含有フロックを形成し、この
フロックを沈殿除去することからなる重金属含有廃水の
処理方法。1. A method for treating heavy metal-containing wastewater, which comprises adding mercaptobenzothiazole or a water-soluble salt thereof and polyethyleneimine to heavy metal-containing wastewater to form a heavy metal-containing floc, and removing the floc by precipitation.
請求項1の処理方法。2. The treatment method according to claim 1, wherein the pH of the heavy metal-containing wastewater is 6 or more.
される廃水である請求項1の処理方法。3. The treatment method according to claim 1, wherein the heavy metal-containing wastewater is wastewater discharged from a plating factory.
水溶性塩とポリエチレンイミンとを有効成分として含有
する重金属含有廃水の処理剤。4. A treatment agent for heavy metal-containing wastewater, which contains mercaptobenzothiazole or a water-soluble salt thereof and polyethyleneimine as active ingredients.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP3099223A JPH04330991A (en) | 1991-04-30 | 1991-04-30 | Treatment of heavy metal containing waste water and treating agent therefor |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP3099223A JPH04330991A (en) | 1991-04-30 | 1991-04-30 | Treatment of heavy metal containing waste water and treating agent therefor |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH04330991A true JPH04330991A (en) | 1992-11-18 |
Family
ID=14241667
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP3099223A Pending JPH04330991A (en) | 1991-04-30 | 1991-04-30 | Treatment of heavy metal containing waste water and treating agent therefor |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH04330991A (en) |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2008018311A (en) * | 2006-07-11 | 2008-01-31 | Nicca Chemical Co Ltd | Treating agent for heavy metal-containing waste water and method for waste water treatment using the same |
JP2017154066A (en) * | 2016-03-01 | 2017-09-07 | 東ソー株式会社 | Purifier for nickel-containing aqueous solution and method of purifying nickel-containing aqueous solution |
JP2018043232A (en) * | 2016-09-08 | 2018-03-22 | 東ソー株式会社 | Purification agent for mercury-containing aqueous solution, and method of purifying mercury-containing aqueous solution |
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JPS52111684A (en) * | 1976-03-16 | 1977-09-19 | Nichidou Denkou Kk | Polisher for electric wire |
JPS56141708A (en) * | 1980-04-03 | 1981-11-05 | Kansai Electric Power Co | Method and device for exfoliating and polishing coating of active wire |
JPS61251407A (en) * | 1985-04-25 | 1986-11-08 | 株式会社泉精器製作所 | Peeler for wire |
JPS63187517U (en) * | 1987-05-23 | 1988-12-01 | ||
JPH02246714A (en) * | 1989-03-20 | 1990-10-02 | Furukawa Electric Co Ltd:The | Cable stripping and polishing tool |
JPH042916U (en) * | 1990-04-24 | 1992-01-10 | ||
JPH0461409U (en) * | 1990-09-28 | 1992-05-26 |
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1991
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Patent Citations (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS52111684A (en) * | 1976-03-16 | 1977-09-19 | Nichidou Denkou Kk | Polisher for electric wire |
JPS56141708A (en) * | 1980-04-03 | 1981-11-05 | Kansai Electric Power Co | Method and device for exfoliating and polishing coating of active wire |
JPS61251407A (en) * | 1985-04-25 | 1986-11-08 | 株式会社泉精器製作所 | Peeler for wire |
JPS63187517U (en) * | 1987-05-23 | 1988-12-01 | ||
JPH02246714A (en) * | 1989-03-20 | 1990-10-02 | Furukawa Electric Co Ltd:The | Cable stripping and polishing tool |
JPH042916U (en) * | 1990-04-24 | 1992-01-10 | ||
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Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2008018311A (en) * | 2006-07-11 | 2008-01-31 | Nicca Chemical Co Ltd | Treating agent for heavy metal-containing waste water and method for waste water treatment using the same |
JP4555801B2 (en) * | 2006-07-11 | 2010-10-06 | 日華化学株式会社 | Heavy metal-containing wastewater treatment agent and wastewater treatment method using the same |
JP2017154066A (en) * | 2016-03-01 | 2017-09-07 | 東ソー株式会社 | Purifier for nickel-containing aqueous solution and method of purifying nickel-containing aqueous solution |
JP2018043232A (en) * | 2016-09-08 | 2018-03-22 | 東ソー株式会社 | Purification agent for mercury-containing aqueous solution, and method of purifying mercury-containing aqueous solution |
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