JPS5819498A - Treatment method for Metsuki wastewater - Google Patents
Treatment method for Metsuki wastewaterInfo
- Publication number
- JPS5819498A JPS5819498A JP11619981A JP11619981A JPS5819498A JP S5819498 A JPS5819498 A JP S5819498A JP 11619981 A JP11619981 A JP 11619981A JP 11619981 A JP11619981 A JP 11619981A JP S5819498 A JPS5819498 A JP S5819498A
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- JP
- Japan
- Prior art keywords
- liq
- wastewater
- tank
- treatment
- contg
- 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.)
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Abstract
Description
【発明の詳細な説明】
本発明はNi−Zn合金メッキ設備からの排水等のNi
、Znを含有するメッキ排水の処理方法に関する。DETAILED DESCRIPTION OF THE INVENTION The present invention is a method for removing Ni from wastewater from Ni-Zn alloy plating equipment.
, relates to a method for treating plating wastewater containing Zn.
メッキ設備のリンス排水のように、重金属を含有する排
水の処理方法としては、アルカリ中和法とイオン交換法
とがある。前者のアルカリ中和法は、PI(調整と凝集
沈澱(必要により最終に1過を組み入れて)との組合せ
で行う方法で、排水量が多いときに適用されることが多
い。後者のイオン交換法は、イオン交換樹脂で重金属類
を選択的に取り込み回収する方法で、重金属類を再利用
できる利点はあるが、排水中の重金属類濃度が低い場合
には、非常に効率の悪い運転になるし、また排水量が多
い場合には大規模な処理設備が必要になるという欠点が
ある0このような観点から、メッキ設備のリンス排水の
ように重金属類濃度が低く、排水量が多い場合には、ア
ルカリ中和法が適用されるのが普。Methods for treating wastewater containing heavy metals, such as rinsing wastewater from plating equipment, include an alkali neutralization method and an ion exchange method. The former alkali neutralization method is a method performed in combination with PI (adjustment and coagulation sedimentation (incorporating 1 filtration at the end if necessary)) and is often applied when the amount of wastewater is large.The latter ion exchange method is a method that selectively captures and recovers heavy metals using ion exchange resin, which has the advantage of being able to reuse heavy metals, but when the concentration of heavy metals in wastewater is low, it results in extremely inefficient operation. In addition, if the amount of wastewater is large, large-scale treatment equipment is required.From this point of view, when the concentration of heavy metals is low and the amount of wastewater is large, such as in rinsing wastewater from plating equipment, alkali treatment is recommended. The neutralization law is usually applied.
通である。I am a connoisseur.
ところで、Ni−Zn合金メッキ設備からのリンス排水
を対象とする場合、除去せねばならない重金属類はNi
2+ 、 Zn”の2種類である。従来、このリンス排
水をアルカリ中和法で処理する場合、アルカリを添加し
て中和し、水酸化金属を析出させることにより沈澱除去
していた。この際のPHは、含有される重金属の溶解度
積と排水基準(通常1.0 PPM以下が目標)により
定めている。そしてZn”+はPH8〜9でZn(OH
)tとして析出し、Ni”+はPH9〜10でNi (
OH)xで析出する。By the way, when rinsing waste water from Ni-Zn alloy plating equipment is targeted, the heavy metals that must be removed are Ni.
There are two types: Zn. The pH of Zn"+ is determined by the solubility product of the heavy metals contained and the wastewater standards (normally 1.0 PPM or less is the target).
)t, and Ni''+ precipitates as Ni (
Precipitate with OH)x.
したがってこのように、水酸化金属を析出するだめの最
適PH域が相異するNi−Zn合金メッキ設備からのリ
ンス排水を処理する場合においては、−回の処理では行
うことができず、まず排水をPH8〜9に調整しZn
(OH)2を析出させ、沈澱分離によりZn (OH)
2を除去し、その後PH9〜10に調整してNi (O
H)2を析出させ、沈澱分離によすNi (OH)2
ヲ析出すセ、沈澱分離FCヨ’り Ni (DH)zを
除去し、次に急速濾過し、最終PH調整を行った後、排
水する方法を採っている。Therefore, when treating rinsing wastewater from Ni-Zn alloy plating equipment where the optimum pH range of the basins for precipitating metal hydroxide differs, it is not possible to perform the rinsing process in one cycle; Adjust the pH to 8~9 and add Zn
(OH)2 is precipitated and Zn (OH) is separated by precipitation.
2 was removed, and then the pH was adjusted to 9 to 10 and Ni (O
H) 2 is precipitated and subjected to precipitation separation.Ni(OH)2
After the Ni(DH)z is precipitated, the Ni(DH)z is removed by precipitation separation, followed by rapid filtration, final pH adjustment, and then draining.
しかし、この方法では、PH調整操作と沈澱分離操作を
2回繰り返すため合理的でなく、連続排水処理を行う場
合には、同処理設備を2組配設せねばならず、経済的で
ない。However, in this method, the PH adjustment operation and the precipitation separation operation are repeated twice, which is not rational, and when continuous wastewater treatment is performed, two sets of the same treatment equipment must be installed, which is not economical.
本発明はかかる問題点を解決すべく提案されたもので、
その目的は従来のように処理を2回行うことなく、1回
の処理で足り、もって経済的なメッキ排水処理方法を提
供することにある0この目的の達成のため、本発明は、
Ni、Znを含有するメッキ排水にFe”十含有液を添
加するとともに、PHを8.5〜9.5に調整してFe
(OH) sを析出させ、その際Zn (OH)2お
よびNi (OH)2を共析させて分離除去するもので
ある。The present invention was proposed to solve such problems,
The purpose of the present invention is to provide an economical plating wastewater treatment method that requires only one treatment instead of the conventional two-time treatment.To achieve this purpose, the present invention
A Fe-containing liquid was added to the plating wastewater containing Ni and Zn, and the pH was adjusted to 8.5 to 9.5 to remove Fe.
(OH) s is precipitated, and at that time Zn (OH) 2 and Ni (OH) 2 are eutectoid and separated and removed.
上記したように、ZnとNiの析出域はPH= 9で一
致しているから、PHを9に正確に調整すれば、Zn
(OH) 2とNi (OH) 2を同時に析出させる
ことができるはすである。しかし、実設備でゆ、たとえ
PHを9に調整したとしても、PH=8.5〜9.5の
範囲で変動してしまい、Zn 2” + Nt ”+を
排出基準まで下げることは困難である。ここに、本発明
者は、Zn (OH)2およびNi (OH)2を共析
させて一度に除去すべく鋭意研究の結果、Fe”+含有
液を添加混合すれば共析させることができることを見出
した。As mentioned above, the precipitation regions of Zn and Ni coincide at pH = 9, so if the pH is adjusted accurately to 9, Zn
(OH) 2 and Ni (OH) 2 can be precipitated simultaneously. However, in actual equipment, even if the pH is adjusted to 9, the pH will fluctuate in the range of 8.5 to 9.5, making it difficult to lower Zn 2'' + Nt ''+ to the emission standard. be. Here, as a result of intensive research in order to eutectoid Zn (OH)2 and Ni (OH)2 and remove them at once, the present inventor found that it is possible to eutectoid by adding and mixing Fe''+ containing liquid. I found out.
すなわち、Ni、Zn含有メッキ排水に、Fe2+含有
液、好適には工場の他の工程から排出されるFe2+含
有する酸洗リンス排水を混合し、曝気しながらPH=8
.5〜9.5に調整すれば、析出するFe (OH)s
が核となって、Zn (OH)2とNi (OH)2が
強制的に析出することを見出したものである。That is, plating wastewater containing Ni and Zn is mixed with a Fe2+-containing liquid, preferably pickling rinse wastewater containing Fe2+ discharged from other processes in the factory, and the mixture is heated to pH=8 while being aerated.
.. If adjusted to 5 to 9.5, Fe(OH)s to precipitate
It was discovered that Zn(OH)2 and Ni(OH)2 are forcibly precipitated with Zn(OH)2 acting as a nucleus.
Fe (OH)sの析出域は、PH=8.0以上であシ
、Fe2+含有液の添加状態でのZn(OH)z析出域
はほぼ8.0〜9.5 、 Ni (OH)2の析出域
はほぼ8.5〜10.0である。そこで、PH=8.5
〜9.sの領域ではZn(OH)2もN1(OHhも析
出する重複域となっている0したがって、PHを8.5
〜9.5に調整すれば、Zn2+およびNi2+が共析
する0よって、これを分離除去すれば、1回の処理で足
りる。The precipitation region of Fe(OH)s is PH=8.0 or higher, and the precipitation region of Zn(OH)z in the addition state of Fe2+-containing liquid is approximately 8.0 to 9.5, Ni(OH)2. The precipitation range is approximately 8.5-10.0. Therefore, PH=8.5
~9. In the region of s, there is an overlapping region where both Zn(OH)2 and N1(OHh) precipitate.
When adjusted to ~9.5, Zn2+ and Ni2+ co-deposit as 0, so if this is separated and removed, one treatment is sufficient.
PH調整に際しては、Ca(OH)2またはNaOH等
を用いることができる。Ni 、 Zn含有メッキ排水
とFe2+含有液との混合は、圧空による曝気でもよい
し、表面を急速に攪拌させる方式など適宜の手法を用い
ればよい。また処理設備は種々の組合せが可能である。For pH adjustment, Ca(OH)2, NaOH, or the like can be used. The Ni, Zn-containing plating wastewater and the Fe2+-containing liquid may be mixed by aeration using compressed air, or by using an appropriate method such as a method of rapidly stirring the surface. Furthermore, various combinations of processing equipment are possible.
Fe2+含有液としては、Fe2+を含有する酸洗リン
ス排水を用いると、この排水処理をも可能になりきわめ
て経済的で、好ましい態様である0次に本発明に係る処
理装置の一例を図面によって説明すると、Ni”、Zn
”十含有リンス排水AとFe2+含有排水Bとが、第1
曝気PH調整槽1に導かれる。この第1曝気PH調整槽
1および第2曝気PH調整槽2下部には、圧空導管3が
設けられ、この導管3の各噴出口から吹き出される空気
が槽1または2の液を混合し、曝気を図るOPH調整槽
1および2には、Ca (OH)2またはNaOH等の
アルカIJ Cが添加され、液のPHが8.5〜9.5
に調整される。第1曝気PR調整槽1での処理液は第2
曝気PH調整槽2へ順次移行する。第2曝気PH調整槽
2の処理液は、沈澱分離装置、たとえばケラリファイヤ
ー4に供給され、沈澱物は底部から除去され、上澄液は
、一旦貯槽5に貯えられた後、ポンプ6により急速濾過
器7に導かれ、P液が後中和槽8に供給される。後中和
槽8では、酸たとえば塩酸りが添加され■=5.6〜8
.5に中和された後、排水Eとして系外へ排出される。If pickling rinse wastewater containing Fe2+ is used as the Fe2+-containing liquid, this wastewater treatment becomes possible and is extremely economical, which is a preferred embodiment. An example of the treatment apparatus according to the present invention will be explained with reference to the drawings. Then, Ni”, Zn
``The 10-containing rinsing wastewater A and the Fe2+-containing wastewater B are
It is led to the aeration PH adjustment tank 1. A compressed air conduit 3 is provided at the bottom of the first aeration PH adjustment tank 1 and the second aeration PH adjustment tank 2, and the air blown out from each outlet of this conduit 3 mixes the liquid in the tank 1 or 2. Alkaline IJC such as Ca(OH)2 or NaOH is added to OPH adjustment tanks 1 and 2 for aeration, and the pH of the liquid is adjusted to 8.5 to 9.5.
is adjusted to The treatment liquid in the first aeration PR adjustment tank 1 is
Sequentially transfer to aeration PH adjustment tank 2. The treated liquid in the second aeration PH adjustment tank 2 is supplied to a sedimentation separation device, for example, a keralifier 4, and the sediment is removed from the bottom. The P solution is guided to a rapid filter 7 and supplied to a post-neutralization tank 8 . In the post-neutralization tank 8, an acid such as hydrochloric acid is added to
.. After being neutralized to 5, it is discharged as wastewater E to the outside of the system.
−いま図面に示す処理装置で処理した場合と、前述の2
回処理を行う方法とで処理性能を比較してみたとζろ、
次表に示すように本発明法によれば、処理性能の格段の
向上がみられた。同表には処理条件も示した。-When processed with the processing equipment shown in the drawing and the case of the above-mentioned 2
When I compared the processing performance with the method of performing multiple processing,
As shown in the following table, according to the method of the present invention, a marked improvement in processing performance was observed. The treatment conditions are also shown in the same table.
以上の通り、本発明は、Ni、Zn含有メ、キ排水にF
e2+含有液を添加してPHを8.5〜9.5に調整す
るから、Fe(O)flaを析出させる際、Zn(OH
)2およびNi(OH)2を共析させることができる。As described above, the present invention applies F to wastewater containing Ni and Zn.
Since the e2+-containing liquid is added to adjust the pH to 8.5 to 9.5, when precipitating Fe(O)fla, Zn(OH
)2 and Ni(OH)2 can be eutectoid.
よって、PH調整と析出物の分離除去とが1回の処理で
済み、操作的にも経済的にも大きな効果がある。Therefore, pH adjustment and separation and removal of precipitates can be carried out in one treatment, which has great operational and economical effects.
さらに処理効率も従来法の場合より高く、公害防止上の
利点も大きい。Furthermore, the treatment efficiency is higher than that of conventional methods, and there are great advantages in terms of pollution prevention.
なお、p62+含有液としてFe2+含有酸洗リンス排
水を用いれば、このリンス排水の処理をも可能となシ、
きわめて経済的となる。In addition, if Fe2+-containing pickling rinse wastewater is used as the p62+-containing liquid, it is also possible to treat this rinse wastewater.
It is extremely economical.
図面は本発明法を実施するための処理設備の一例を示す
フローシートである。
1.2・・・・PH調整槽
3・・・・圧空導管 4・・・・クラリファイヤ−
7・・・・急速r過器 8・・・・後中和槽A・・・
・Ni” * Zn”十含有リンス排水B・・・・Fe
2+含有排水
特許出願人 住友金属工業株式会社The drawing is a flow sheet showing an example of processing equipment for carrying out the method of the present invention. 1.2...PH adjustment tank 3...Pressed air conduit 4...Clarifier
7... Rapid r-passage device 8... Post-neutralization tank A...
・Ni" * Zn" containing rinsing wastewater B...Fe
2+ containing wastewater patent applicant Sumitomo Metal Industries, Ltd.
Claims (1)
+含有液を添加するとともに、PHを8.5〜9.5に
調整してFe 0)11 sを析出させ、その際Zn
(OH)zおよびNi (OB)zを共析させて分離除
去することを特徴とするメッキ排水の処理方法。(1) Adding Fe to plating wastewater containing Ni*Zn
In addition to adding the + containing liquid, the pH was adjusted to 8.5 to 9.5 to precipitate Fe 0)
A method for treating plating wastewater, characterized by eutectoiding and separating and removing (OH)z and Ni (OB)z.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP11619981A JPS5819498A (en) | 1981-07-24 | 1981-07-24 | Treatment method for Metsuki wastewater |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP11619981A JPS5819498A (en) | 1981-07-24 | 1981-07-24 | Treatment method for Metsuki wastewater |
Publications (1)
Publication Number | Publication Date |
---|---|
JPS5819498A true JPS5819498A (en) | 1983-02-04 |
Family
ID=14681282
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP11619981A Pending JPS5819498A (en) | 1981-07-24 | 1981-07-24 | Treatment method for Metsuki wastewater |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS5819498A (en) |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US6409927B1 (en) * | 1998-06-03 | 2002-06-25 | Enrique-Ruben Cardenas-Granguillhome | Process for the treatment of polluted metal-mechanic industrial wastewater and urban water |
KR100401994B1 (en) * | 1998-12-21 | 2003-12-31 | 주식회사 포스코 | A METHOD FOR MANUFACTURING OF Ni-Zn MIXED OXIDE BY USING OF Zn-Ni SPENT ELECTROLYTE |
KR100966093B1 (en) | 2009-11-05 | 2010-06-25 | 주식회사 지오웍스 | Method clearing wastewater by eco-friendly clarifier |
JP2014080648A (en) * | 2012-10-15 | 2014-05-08 | Fukuoka Prefecture | Method and apparatus for regenerating waste water of nickel plating |
-
1981
- 1981-07-24 JP JP11619981A patent/JPS5819498A/en active Pending
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US6409927B1 (en) * | 1998-06-03 | 2002-06-25 | Enrique-Ruben Cardenas-Granguillhome | Process for the treatment of polluted metal-mechanic industrial wastewater and urban water |
KR100401994B1 (en) * | 1998-12-21 | 2003-12-31 | 주식회사 포스코 | A METHOD FOR MANUFACTURING OF Ni-Zn MIXED OXIDE BY USING OF Zn-Ni SPENT ELECTROLYTE |
KR100966093B1 (en) | 2009-11-05 | 2010-06-25 | 주식회사 지오웍스 | Method clearing wastewater by eco-friendly clarifier |
JP2014080648A (en) * | 2012-10-15 | 2014-05-08 | Fukuoka Prefecture | Method and apparatus for regenerating waste water of nickel plating |
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