JPS5836695A - Treatment of waste liquid of chemical washing - Google Patents

Treatment of waste liquid of chemical washing

Info

Publication number
JPS5836695A
JPS5836695A JP13422981A JP13422981A JPS5836695A JP S5836695 A JPS5836695 A JP S5836695A JP 13422981 A JP13422981 A JP 13422981A JP 13422981 A JP13422981 A JP 13422981A JP S5836695 A JPS5836695 A JP S5836695A
Authority
JP
Japan
Prior art keywords
iron
citric acid
waste liquid
recovered
content
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.)
Granted
Application number
JP13422981A
Other languages
Japanese (ja)
Other versions
JPS60119B2 (en
Inventor
Tadao Imamura
今村 忠夫
Hajime Kitazato
北里 元
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Chiyoda Corp
Chiyoda Chemical Engineering and Construction Co Ltd
Original Assignee
Chiyoda Corp
Chiyoda Chemical Engineering and Construction Co Ltd
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Chiyoda Corp, Chiyoda Chemical Engineering and Construction Co Ltd filed Critical Chiyoda Corp
Priority to JP13422981A priority Critical patent/JPS60119B2/en
Publication of JPS5836695A publication Critical patent/JPS5836695A/en
Publication of JPS60119B2 publication Critical patent/JPS60119B2/en
Expired legal-status Critical Current

Links

Abstract

PURPOSE:To recover iron and citric acid efficiently by controlling waste liquid of chemical washing contg. chelate of iron and citric acid to pH higher than specific values with caustic soda, settling iron as hydroxide, and adding a soluble Ca compd. to the filtrate. CONSTITUTION:If the pH of waste liquid of chemical washing contg. chelate of iron and citric acid is controlled to >=11.5 (more particularly 11.5-13) by adding an about 10% aq. caustic soda soln. thereto, the iron settles as hydroxide. After iron content is recovered by filtering out the sediment, a soluble Ca compd. such as CaCl2, Ca(NO3)2 or the like is added. The citric acid in the liquid reacts with the Ca compd. thereof and settles as calcium citrate which is recovered.

Description

【発明の詳細な説明】 本発明は化学洗浄液の処理方法に関し、更に詳しくは、
鉄とクエン酸とのキレートを含む化学洗浄廃液から鉄分
とクエン酸分を別々に回収する方法に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for treating chemical cleaning liquid, and more specifically, to
This invention relates to a method for separately recovering iron and citric acid from chemical cleaning waste liquid containing chelates of iron and citric acid.

発明者らは先にクエン酸を含む化学洗浄液を処理する方
法を開発し、特願昭48−62515(特開昭5O−1
0780)として開示しているがその内容は化学洗浄廃
液にカルシウム化合物を過剰に添加することにより、廃
液中の金属分、ならびにクエン酸分を難溶性のカルシウ
ム塩として同時に沈澱物として分離し、その上澄液を過
酸化水素、過塩化物等の酸化剤で酸化してCOD成分を
分解無害化する方法であり、廃液の高度の清澄化を目的
とする方法である。しかしながらこの方法は、前述のよ
うにクエン酸分を、共存する金属分と共に沈。
The inventors first developed a method for treating a chemical cleaning solution containing citric acid, and filed a patent application No. 48-62515 (Japanese Patent Application Laid-Open No. 50-198-1999).
0780), the content of which is that by adding an excessive amount of calcium compound to chemical cleaning waste liquid, the metal content and citric acid content in the waste liquid are simultaneously separated as poorly soluble calcium salts as precipitates. This is a method in which the supernatant liquid is oxidized with an oxidizing agent such as hydrogen peroxide or perchloride to decompose and render harmless COD components, and the purpose is to highly clarify the waste liquid. However, as mentioned above, this method precipitates the citric acid component together with the coexisting metal components.

澱回収する方法であるため、回収した沈澱物はこれを再
利用することが極めて困難な上、この廃棄処分にも脱水
、焼却、埋立等に2〜3万円/立方メートル程度の処理
費を必要とし、これが該処理の工業化に大きなネックと
なっていた。
Since it is a method of collecting sediment, it is extremely difficult to reuse the collected sediment, and disposal costs of approximately 20,000 to 30,000 yen per cubic meter are required for dewatering, incineration, landfilling, etc. This has been a major bottleneck in the industrialization of this process.

発明者らは、これらの問題をクエン酸分とと鉄分を別個
に回収することによって解決出来ることに着目し、研究
を進めた結果発明に至ったものである。
The inventors focused on the fact that these problems could be solved by recovering citric acid and iron separately, and conducted research that led to the invention.

即ち本発明の方法は廃液に苛性ソーダを添加してplI
を11.5以上とすることによって鉄分を水酸化物とし
て沈澱せしめ、これを回収し、更に鉄分を回収した廃液
に可溶性カルシウム化合物を加えクエン酸分をクエン酸
カルシウムとして沈澱回収する方法である。
That is, the method of the present invention adds caustic soda to the waste liquid and
is 11.5 or more, the iron content is precipitated as hydroxide, which is recovered, and then a soluble calcium compound is added to the waste liquid from which the iron content has been recovered, and the citric acid content is precipitated and recovered as calcium citrate.

この方法の特徴は、クエン酸分が第1段の苛性ソーダの
添加によってpHを11.5以上としたとき、大部分が
クエン酸ソーダとなるが、これが極めて溶解度が大きい
ため鉄分と同時に沈澱せず効果的に分離できる性質を利
用したところにある。水に溶解している金属分は、通常
pH8〜9のアルカリ性にすることによって容易に水酸
化物として沈澱することは、当業者の公知の技術である
が、クエン酸とのキレートを形成するときは、この程度
のアルカリ性では殆んど沈澱せず、錯体となった金属の
みの回収が極めて困難なことは、つとに言われていたと
ころである。
The feature of this method is that most of the citric acid becomes sodium citrate when the pH is raised to 11.5 or higher by the addition of caustic soda in the first stage, but because this has extremely high solubility, it does not precipitate at the same time as the iron. This is because it takes advantage of the property that it can be effectively separated. It is well known to those skilled in the art that metals dissolved in water are easily precipitated as hydroxides by making the pH pH 8 to 9 alkaline, but when forming a chelate with citric acid, It has been said that almost no precipitation occurs at this level of alkalinity, and that it is extremely difficult to recover only the complexed metal.

発明者らは廃水中の鉄とクエン酸のキレートがpHが1
0あたりから分解が認められpH12程度のところでほ
とんど全量の分解が起り、鉄分のほぼ完全な回収が出来
ることを確認した。従ってpHを高くする程純度の高い
クエン酸の回収が可能となり、回収したクエン酸の用途
により回収条件を設定する必要がある。
The inventors discovered that the chelate of iron and citric acid in wastewater has a pH of 1.
Decomposition was observed from around 0, and almost all decomposition occurred at around pH 12, confirming that almost complete iron content could be recovered. Therefore, the higher the pH, the more purified citric acid can be recovered, and it is necessary to set the recovery conditions depending on the use of the recovered citric acid.

一方p■が高くなるほど廃液中に残存する鉄分の量が少
なくなるが工業的には廃液中に許容される鉄分量(現行
の排出基準10 ppm ) k満足する値で十分であ
り、その点からはpH11,5以上が必要とされること
を認めた。
On the other hand, as p becomes higher, the amount of iron remaining in the waste liquid decreases, but from an industrial perspective, a value that satisfies the permissible amount of iron in the waste liquid (current emission standard 10 ppm) k is sufficient, and from that point of view, recognized that a pH of 11.5 or higher is required.

上述のようにpiを高くする程金属分の回収率は高くは
なるが、過剰の添加は最終の廃液の処理負荷が大きくな
ると共に第1図に示すように添加量の増加に対する金属
除去効率の上昇が頭うちとなり経済的にあまり好ましく
ない。この為上限、はpH約13−・程度で十分である
As mentioned above, the higher the pi, the higher the recovery rate of metals, but excessive addition increases the processing load of the final waste liquid, and as shown in Figure 1, the metal removal efficiency decreases as the amount of addition increases. The rise has reached a plateau, which is not very favorable economically. For this reason, an upper limit of about pH 13-. is sufficient.

ちなみに廃液はpHを12程度まで上げれは殆んどの量
の鉄クエン酸キレートが分解され、金属分が水酸化物と
して沈澱し、廃水中に残存する鉄分を1.5 ppm程
度までに減少することができる。更にpHを13程度に
まで上げれば鉄のクエン酸キレートはほぼ完全に分解さ
れ残存する鉄分が痕跡量にまで減少せしめられクエン酸
カルシウムの回収率もほぼ上限に近いところまで向上で
きる。
By the way, if the pH of the wastewater is raised to about 12, most of the iron citrate chelate will be decomposed and the metal will precipitate as hydroxide, reducing the iron content remaining in the wastewater to about 1.5 ppm. I can do it. Furthermore, if the pH is raised to about 13, the iron citric acid chelate is almost completely decomposed, the remaining iron content is reduced to a trace amount, and the recovery rate of calcium citrate can be improved to almost the upper limit.

このようにして回収された金属分は廃液が石油工業、石
油化学工業、一般化学工業における装置の洗浄に使用し
たものである場合には、はとんどが鉄分である、ゲータ
イiの水酸化物とした後空気中約600℃の酸化により
ベンガラとしての再利用が可能である。
If the waste liquid recovered in this way is used for cleaning equipment in the petroleum industry, petrochemical industry, or general chemical industry, the metal content recovered in this way is mostly iron, and the hydroxide of Geitai i. After it is made into a material, it can be oxidized in air at about 600°C to be reused as red red iron.

一方クエン酸分の面からみると、金属を回収した後カル
シウム塩として回収する本発明の方法では、piが10
以上であれば回収率がほとんど一定となることを知見し
ている。従つて金属分の回収の面からの要求に基いてp
Hを設定しておけば、クエン酸回収上からも十分満足し
得る結果が得られる。回収されたクエン酸カルシウムは
、従来広く工業的に行われている方法によりクエン酸に
転換し得る。
On the other hand, in terms of the citric acid content, in the method of the present invention in which the metal is recovered as a calcium salt, pi is 10
It is known that the recovery rate is almost constant if it is above. Therefore, based on the requirements from the point of view of metal recovery, p
If H is set, a sufficiently satisfactory result can be obtained in terms of citric acid recovery. The recovered calcium citrate can be converted to citric acid by a conventionally widely used industrial method.

例えばクエン酸カルシウムに理論量の硫酸を加えてクエ
ン酸を遊離し、不純物を活性炭等により吸着除去した後
、濃縮してクエン酸の結晶として回収する。
For example, a theoretical amount of sulfuric acid is added to calcium citrate to liberate citric acid, impurities are adsorbed and removed using activated carbon, etc., and then concentrated and recovered as citric acid crystals.

本発明の処理に使用する苛性ソーダ水溶液の濃度は特に
制限的ではないが、pH調整という目的から約10%水
溶液が最も望ましく゛。
Although the concentration of the caustic soda aqueous solution used in the treatment of the present invention is not particularly limited, an approximately 10% aqueous solution is most desirable for the purpose of pH adjustment.

また可溶性ガルシウム化合物としては、Cac4.Ca
 (NOx )2等の容易に溶液中でCaイオンを生ず
るものであれば特に制限はない。
Moreover, as a soluble galcium compound, Cac4. Ca
There is no particular restriction as long as it can easily generate Ca ions in solution, such as (NOx)2.

このようにして金属分、クエン酸分を回収した後の上澄
液は廃棄処分することになるが、この中には主として腐
蝕防止剤、界面活性剤等からなるCOD成分が500〜
1.000ppm程度残存しているため、例えば晒粉の
ような酸化剤で処理することにより20 ppm以下の
含量とし、河川等に放流することができる。
The supernatant after recovering metals and citric acid in this way is disposed of, but this contains COD components of 500 to 500%, mainly consisting of corrosion inhibitors, surfactants, etc.
Since about 1.000 ppm remains, the content can be reduced to 20 ppm or less by treatment with an oxidizing agent such as bleaching powder, and then discharged into rivers and the like.

次に実施例により本発明の方法を更に詳細に説明する。Next, the method of the present invention will be explained in more detail with reference to Examples.

実施例 石油精製装置を酸洗した下記成分の廃液に10%のNa
OH水溶液を下記第1表に示す夫々の量添加し、鉄分を
沈澱回収した後、CaCt2を添加しクエン酸分をクエ
ン酸カルシウムとして沈澱回収した。結果を第1表に示
す。
Example 10% Na was added to the waste liquid of the following components obtained by pickling the oil refinery equipment.
OH aqueous solutions were added in the respective amounts shown in Table 1 below, and the iron content was precipitated and recovered, then CaCt2 was added and the citric acid content was precipitated and recovered as calcium citrate. The results are shown in Table 1.

同第1表に示したクエン酸回収率は、第2段の処理によ
って回収したクエン酸分の原液中のクエン酸分に対する
パーセントを示す。
The citric acid recovery rate shown in Table 1 indicates the percentage of citric acid recovered by the second stage treatment to the citric acid in the stock solution.

原液性状 *1 鉄分含量  1.450 ppm *2 クエン酸分   1.76チ pH8,74 外  観  黄褐色 第  1  表Stock liquid properties *1 Iron content 1.450 ppm *2 Citric acid content: 1.76 chi pH8,74 Appearance Yellowish brown Table 1

【図面の簡単な説明】[Brief explanation of drawings]

第1図は廃液に10 NaOH添加量に対する金属除去
効率の変化を示したものである。 手続補正書 昭和56年10月20日 特許庁長官島田春樹 彎 】事件の表示昭和56年 特許願第154229号2、
発明の名称 化学洗浄廃液の処理方法 3 補正をする者 事件との関係 特許出願人 1″r 神奈川県横浜市鶴見区鶴見中央二丁目12番1
号”   (328)千代田化工建設株式会社(名称) 4代理人 5、補正の対象  (1)明細書の「発明の詳細な説明
」の欄(1)明細書第1頁第18行目の 「化学洗浄液」を 「化学洗浄廃液」と訂正する。 (2)同上第2頁第2行目の 「化学洗浄液」を 「化学洗浄廃液」と訂正する。 (3)同上第5頁第14行目の 「鉄分である。」を 「鉄分であり、これを」と訂正する。 (4)同上筒8頁ニス・ら2行目の 「1ONaOHJを [10%Na0HJと訂正する。
FIG. 1 shows the change in metal removal efficiency with respect to the amount of 10 NaOH added to the waste liquid. Procedural amendment October 20, 1980 Haruki Shimada, Commissioner of the Japan Patent Office] Indication of the case 1981 Patent Application No. 154229 2,
Name of the invention Method for treating chemical cleaning waste liquid 3 Relationship with the case of the person making the amendment Patent applicant 1″r 2-12-1 Tsurumi Chuo, Tsurumi-ku, Yokohama, Kanagawa Prefecture
(328) Chiyoda Corporation (Name) 4 Agent 5, Subject of amendment (1) "Detailed description of the invention" column of the specification (1) "In the 18th line of page 1 of the specification""Chemical cleaning liquid" is corrected to "Chemical cleaning waste liquid." (2) "Chemical cleaning liquid" in the second line of page 2 of the above is corrected to "chemical cleaning waste liquid." (3) In the 14th line of page 5 of the same document, "It's iron." is corrected to "It's iron." (4) In the second line of Nis et al., page 8 of the same cylinder, "1ONaOHJ is corrected to [10%Na0HJ.

Claims (1)

【特許請求の範囲】 1、鉄とクエン酸とのキレートを含6化学洗浄廃液を苛
性ソーダでpgを11.5以上に調整し、鉄分を水酸化
物として沈澱せしめこれを回収した後、更に可溶性カル
シウム化合物を添加しクエン酸分をクエン酸カルシウム
として沈澱回収することを特徴とする化学洗浄廃液の処
理方法。 2、苛性ソーダによるpn調整を11.5〜13に調整
する特許請求の範囲第1項の方法。 3、 可溶性カルシウム化合物としてCaC4、Ca 
(No、)2を使用する特許請求の範囲第1、または2
項の方法。
[Claims] 1. A chemical cleaning waste solution containing a chelate of iron and citric acid is adjusted to a pg of 11.5 or more with caustic soda, and the iron content is precipitated as a hydroxide. After recovering this, further soluble A method for treating chemical cleaning waste liquid, characterized by adding a calcium compound and recovering the citric acid content by precipitation as calcium citrate. 2. The method according to claim 1, in which pn adjustment by caustic soda is adjusted to 11.5 to 13. 3. CaC4, Ca as soluble calcium compounds
Claim 1 or 2 using (No.)2
Section method.
JP13422981A 1981-08-28 1981-08-28 Processing method for chemical cleaning waste liquid Expired JPS60119B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP13422981A JPS60119B2 (en) 1981-08-28 1981-08-28 Processing method for chemical cleaning waste liquid

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP13422981A JPS60119B2 (en) 1981-08-28 1981-08-28 Processing method for chemical cleaning waste liquid

Publications (2)

Publication Number Publication Date
JPS5836695A true JPS5836695A (en) 1983-03-03
JPS60119B2 JPS60119B2 (en) 1985-01-05

Family

ID=15123439

Family Applications (1)

Application Number Title Priority Date Filing Date
JP13422981A Expired JPS60119B2 (en) 1981-08-28 1981-08-28 Processing method for chemical cleaning waste liquid

Country Status (1)

Country Link
JP (1) JPS60119B2 (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH07367U (en) * 1991-03-25 1995-01-06 健一 川井田 Eye drop container with mirror
JP2000210681A (en) * 1999-01-21 2000-08-02 United States Enrichment Corp Method of removing metal from cleaning liquid
CN102390877A (en) * 2011-08-04 2012-03-28 中粮生物化学(安徽)股份有限公司 Treatment method of calcium hydrogen citrate washes and preparation method of citric acid

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US10546488B2 (en) 2017-06-21 2020-01-28 International Business Machines Corporation Management of mobile objects

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH07367U (en) * 1991-03-25 1995-01-06 健一 川井田 Eye drop container with mirror
JP2000210681A (en) * 1999-01-21 2000-08-02 United States Enrichment Corp Method of removing metal from cleaning liquid
CN102390877A (en) * 2011-08-04 2012-03-28 中粮生物化学(安徽)股份有限公司 Treatment method of calcium hydrogen citrate washes and preparation method of citric acid

Also Published As

Publication number Publication date
JPS60119B2 (en) 1985-01-05

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