JPS6111193A - Treatment of waste liquid of chemical cleaning - Google Patents

Treatment of waste liquid of chemical cleaning

Info

Publication number
JPS6111193A
JPS6111193A JP13362384A JP13362384A JPS6111193A JP S6111193 A JPS6111193 A JP S6111193A JP 13362384 A JP13362384 A JP 13362384A JP 13362384 A JP13362384 A JP 13362384A JP S6111193 A JPS6111193 A JP S6111193A
Authority
JP
Japan
Prior art keywords
waste liquid
hydroxide
liquid
chemical cleaning
calcium
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
Application number
JP13362384A
Other languages
Japanese (ja)
Inventor
Yukio Hayashi
林 行男
Yoshio Kudo
工藤 良夫
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.)
Mitsubishi Heavy Industries Ltd
Original Assignee
Mitsubishi Heavy Industries 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 Mitsubishi Heavy Industries Ltd filed Critical Mitsubishi Heavy Industries Ltd
Priority to JP13362384A priority Critical patent/JPS6111193A/en
Publication of JPS6111193A publication Critical patent/JPS6111193A/en
Pending legal-status Critical Current

Links

Abstract

PURPOSE:To permit the easy treatment by adding an alkali agent to waste liquid to form the precipitate of hydroxide of heavy metal, etc. and blowing air to the liquid to oxidize the liquid then adding active carbon thereto. CONSTITUTION:A calcium compd. such as calcium hydroxide is added to the waste liquid under stirring to adjust the pH to >=7 and to precipitate phosphoric acid and heavy metal ions in the form of calcium phosphate and the hydroxide of heavy metal. The formed ferrows hydroxide is oxidized to ferric hydroxide by blowing air and thereafter sodium peroxide is added to the waste liquid at the equiv. of COD in said liquid or above under blowing of air together with >=0.05 kg active carbon for each 1m<3> of the waste liquid to oxidize and decompose the COD component.

Description

【発明の詳細な説明】 (産業上の利用分野) 本発明は、塩酸洗浄液及びりん酸系の防錆液を含む化学
洗浄廃液を処理する方法に関する。
DETAILED DESCRIPTION OF THE INVENTION (Industrial Application Field) The present invention relates to a method for treating chemical cleaning waste liquid containing a hydrochloric acid cleaning liquid and a phosphoric acid-based rust preventive liquid.

(従来の技術) 従来、火力プラント、化学プラント等のボイラ、熱交換
器等の金属表面に付着、堆積した鉄を主成分とする酸化
物スケールあるいは稼動ボイラの如く銅分を含む酸化物
スケールを除去してプラント類の安全運転、保全管理を
目的として化学洗浄が行われている。化学洗浄組成の一
例として塩酸に酸腐食抑制剤(インヒビター)あるいは
銅分を含むスケールに対しては塩酸にインヒビターと銅
分を溶解封鎖するチオ尿素が添加されておシ、また酸洗
浄後の金属表面1一時的に防錆する防錆処理において、
それら化学洗浄後の廃液の組成と性状の一例を示せば第
1表の如くである。また、排水基準値は地域自治体との
公害防止協定などで決められており、その例を示せば第
2表の如くである。
(Prior art) In the past, oxide scale mainly composed of iron that adhered or accumulated on the metal surfaces of boilers, heat exchangers, etc. in thermal power plants, chemical plants, etc., or oxide scale containing copper content such as in operating boilers, etc. Chemical cleaning is carried out to remove these substances and ensure the safe operation and maintenance of plants. As an example of a chemical cleaning composition, an acid corrosion inhibitor (inhibitor) is added to hydrochloric acid, or for scale containing copper, thiourea is added to hydrochloric acid to dissolve and sequester the inhibitor and copper. Surface 1 In the rust prevention treatment that temporarily prevents rust,
An example of the composition and properties of the waste liquid after chemical cleaning is shown in Table 1. In addition, wastewater standard values are determined by pollution prevention agreements with local governments, and examples are shown in Table 2.

第1表から判るように銅分を含有しないスケールの化学
洗浄廃液あるいは銅分を含有するスケールの化学洗浄廃
液の何れにも有害成分である遊離酸、 COD、鉄、銅
(銅分を含有するスケールの化学洗浄廃液のみ)及びり
ん酸塩などが多量溶解されているので、このような化学
洗浄廃液は公害上そのママ放流することは絶対に許され
ない。
As can be seen from Table 1, both the chemical cleaning waste for scale that does not contain copper and the chemical cleaning waste for scale that contains copper contain harmful components such as free acid, COD, iron, and copper (containing copper). Since a large amount of chemical scale cleaning waste liquid (only chemical scale cleaning waste liquid) and phosphates are dissolved, it is absolutely unacceptable to discharge such chemical cleaning waste liquid in its entirety due to pollution concerns.

一方、放流水質は第2表に例示されるように各地域自治
体との公害防止協定などで決められた規制値まで浄化処
理することが必要である。
On the other hand, as shown in Table 2, it is necessary to purify the quality of the discharged water to the regulatory values determined by pollution prevention agreements with local governments.

従来はこのような化学洗浄廃液の処理工程において。Conventionally, in the treatment process of such chemical cleaning waste liquid.

(1)水酸化ナトリウムあるいは水酸化カルシウムなど
のアルカリ剤を加えてPH11以上に調整し重金属を沈
殿生成する。
(1) Add an alkaline agent such as sodium hydroxide or calcium hydroxide to adjust the pH to 11 or higher to precipitate heavy metals.

(2)  エアレーションしながら凝集剤を添加し沈殿
物を沈降させた後、その上澄液を別の貯槽にポンプ移送
する。
(2) After adding a flocculant and settling the precipitate while aerating, the supernatant liquid is pumped to another storage tank.

(3) A I COD除去:エアレーションしながら
過酸化水素kcODに対し当量以上添 加してC0Dk 1100pp程度まで処理する。
(3) A I COD removal: While aerating, hydrogen peroxide is added in an amount equivalent to or more relative to kcOD, and treatment is carried out to a CODk level of approximately 1100 pp.

(4)A 2 COD除去:エアレーションしながら過
硫酸塩を添加してCODを10ppm 程度まで処理する。
(4) A 2 COD removal: Add persulfate while aerating to treat COD to about 10 ppm.

(5)PH再調整:塩酸等の酸で中和したのち放流する
(5) PH readjustment: Discharge after neutralizing with acid such as hydrochloric acid.

(発明が解決しようとする問題点) 上述した処理方法によればCODは確かに排水規準値内
まで低下できるが9次のような問題点がある。
(Problems to be Solved by the Invention) According to the treatment method described above, the COD can certainly be lowered to within the wastewater standard value, but there are the following problems.

(1)廃液処理工程が非常に繁雑でちシ、処理に長時間
を要しコスト高となる。
(1) The waste liquid treatment process is very complicated and takes a long time to process, resulting in high costs.

(2)化学洗浄廃液量は多い時で800〜1bM@Q1
m’にもなるため廃液貯槽が1基しかないプラントの場
合は仮設の廃液貯槽が必要となシ、コスト高の一因とな
る。
(2) The amount of chemical cleaning waste liquid is 800 to 1 bM @Q1
m', so in the case of a plant with only one waste liquid storage tank, a temporary waste liquid storage tank is required, which is a cause of high costs.

(3)  沈殿生成物を分離した上澄液において屋1゜
A2のCOD除去剤を添加処理すると廃液中の銅封鎖剤
であるチオ尿素[(NH2)2 CS、lが酸化分解さ
れて硫黄Sを析出して白濁するため。
(3) When a COD remover of 1°A2 is added to the supernatant liquid from which the precipitated product has been separated, thiourea [(NH2)2CS, 1, which is a copper sequestering agent in the waste liquid, is oxidized and decomposed to form sulfur S. Precipitates out and becomes cloudy.

放流に際し問題が残る。Problems remain when releasing water.

第1表 第2表 海、域に排出される排水の基準値例(各地の例
から抜粋) また、 CODの除去については、上記方法以外に廃液
全アルカリ剤でアルカリ性にしたのち。
Table 1 Table 2 Examples of standard values for wastewater discharged into the sea and other areas (excerpts from examples from various regions) In addition to the methods mentioned above, COD can also be removed by making all wastewater alkaline with an alkaline agent.

次亜塩素酸ナトリウム、さらし粉あるいは過酸化水素等
の酸化剤を添加してCOI酸化分解する方法もあるが9
本発明者等の実験によれば倒れの酸化剤も酸化力が弱く
第2表の排水基準値を大きく越えており、満足すべき結
果は得られなかった。
There is also a method of oxidizing and decomposing COI by adding an oxidizing agent such as sodium hypochlorite, bleaching powder, or hydrogen peroxide.9
According to the experiments conducted by the present inventors, the oxidizing agent of the present invention also had a weak oxidizing power and far exceeded the wastewater standard value shown in Table 2, and no satisfactory results were obtained.

本発明は、上記の問題点を解消するため、廃液中の重金
属、9ん酸塩、 CODなどの有害物質を第2表の排水
基準値内まで除去し、かつ無色透明の処理水を比較的簡
単に得ることができる化学洗浄廃液の処理方法を提供す
ることを目的とする。
In order to solve the above-mentioned problems, the present invention removes harmful substances such as heavy metals, 9-phosphates, and COD from wastewater to within the wastewater standard values shown in Table 2, and produces relatively clear and colorless treated water. The object of the present invention is to provide a method for treating chemical cleaning waste liquid that can be easily obtained.

(問題点を解決するための手段) 本発明は、塩酸洗浄液及びりん酸系の防錆液を含む化学
洗浄廃液を処理するにあたシ、上記廃液に水酸化カルシ
ウム酸化カルシウムあるいは塩化カルシウム等のカルシ
ウム化合物及び水酸化ナトリウムあるいは水酸化カリウ
ム等のアルカリ剤を添加してPH7以上に調整してアル
カリ廃液とし、この廃液中の重金属及びりん酸塩を重金
属水酸化物及びりん酸カルシウムとして沈殿生成させ、
生成した水酸化第一鉄を空気吹き込みによって水酸化第
二鉄に酸化したのち。
(Means for Solving the Problems) The present invention provides a method for treating chemical cleaning waste liquid containing a hydrochloric acid cleaning liquid and a phosphoric acid-based rust preventive liquid, by adding calcium hydroxide, calcium oxide, calcium chloride, etc. to the waste liquid. A calcium compound and an alkaline agent such as sodium hydroxide or potassium hydroxide are added to adjust the pH to 7 or higher to obtain an alkaline waste liquid, and the heavy metals and phosphates in this waste liquid are precipitated as heavy metal hydroxide and calcium phosphate. ,
After the generated ferrous hydroxide is oxidized to ferric hydroxide by air blowing.

上記廃液中のCODに対して過酸化ナトリウムを当量以
上及び粒状の活性炭を廃液in’に対し0.05Kg以
上併用添加してCOD成分を酸化分解する化学洗浄廃液
の処理方法である。
This is a method for treating chemical cleaning waste liquid in which the COD component is oxidized and decomposed by adding at least an equivalent amount of sodium peroxide to the COD in the waste liquid and 0.05 kg or more of granular activated carbon to the waste liquid in'.

(作用) 第1表に示した組成及び性状の化学洗浄廃液を対象とし
て説明する。先ず廃液を空気吹き込みによって強制的に
攪拌しながら水酸化カルシウム、酸化カルシウム、ある
いは塩化カルシウムなどのカルシウム化合物を廃液中の
シん酸イオン(PO4)に対し1当量以上添加し、さら
に水酸化ナトリウムあるいは水酸化カリウムなどのアル
カリ剤を添加してPH7以上に調整してシん酸及び重金
属イオンをりん酸カルシウム及び重金属の水酸化物とし
て沈殿生成させ、生成した水酸化第一鉄を空気吹き込み
によって水酸化第二鉄に酸化したのち空気吹き込みを続
けながら過酸化す) IJウムを廃液中のCODに対し
当量以上及び粒状の活性炭を廃液1rr?に対し0.0
5 K9以上併用添加してCOD成分を酸化分解する。
(Function) The following description deals with chemical cleaning waste liquid having the composition and properties shown in Table 1. First, a calcium compound such as calcium hydroxide, calcium oxide, or calcium chloride is added in an amount of 1 equivalent or more based on phosphate ion (PO4) in the waste liquid while forcibly stirring the waste liquid by blowing air, and then sodium hydroxide or Add an alkaline agent such as potassium hydroxide to adjust the pH to 7 or higher to precipitate cynic acid and heavy metal ions as calcium phosphate and heavy metal hydroxide, and then hydrate the ferrous hydroxide by blowing air. After oxidizing to ferric oxide, peroxidize while continuing to blow air) Add IJum in an amount equivalent to or more than the COD in the waste liquid and granular activated carbon to 1rr of the waste liquid. 0.0 against
5 K9 or higher is added in combination to oxidize and decompose COD components.

次いで空気吹き込みを止め、セラ) IJングによシ上
澄液と沈殿物に完全分離したのち、上澄液は塩酸または
硫酸などで中和しながらポンプを使用してそのまま排出
放流し、沈殿物は遠心分離機あるいはプレスフィルター
機によシ脱水し。
Then, the air blowing is stopped, and the supernatant liquid is completely separated into the precipitate using IJ.The supernatant liquid is neutralized with hydrochloric acid or sulfuric acid, etc., and discharged as it is using a pump, and the precipitate is removed. is dehydrated using a centrifuge or press filter machine.

固形物として処理する。なお上記廃液処理において上澄
液と沈殿物を分離する場合に沈殿物の凝集沈降を促進す
るために高分子凝集剤を添加してもよい。
Treat as a solid. In addition, when separating a supernatant liquid and a precipitate in the above-mentioned waste liquid treatment, a polymer flocculant may be added to promote coagulation and sedimentation of the precipitate.

第1表に示す化学洗浄廃液に水酸化カルシウム、酸化カ
ルシウム、塩化カルシウムなどのカルシウム化合物及び
水酸化す) IJウム、水酸化カリウムなどのアルカリ
剤を併用添加して廃液中に溶解しているりん酸塩及び鉄
、銅などの重金属がほぼ完全に除去できるのは、りん酸
カルシウム(Ca5(PO4)zl及び鉄、銅の水酸化
物CFe(OH)z 、 Cu(OH)z )の沈殿を
生成するからである。次に沈殿生成した水酸化第一鉄C
F e(OH)z’)を空気吹き込みによって、下記(
1)式の化学反応に示すように水酸化第二鉄CFe(O
H)3)に酸化するのは、廃液中の溶解鉄を減少させる
のと。
Calcium compounds such as calcium hydroxide, calcium oxide, and calcium chloride, as well as alkaline agents such as potassium hydroxide and calcium hydroxide, are added to the chemical cleaning waste liquid shown in Table 1 to prevent phosphorus from being dissolved in the waste liquid. Salts and heavy metals such as iron and copper can be almost completely removed by precipitation of calcium phosphate (Ca5(PO4)zl and iron and copper hydroxides CFe(OH)z, Cu(OH)z). This is because it generates. Next, ferrous hydroxide C precipitated
F e(OH)z') by blowing air into the following (
1) As shown in the chemical reaction of formula, ferric hydroxide CFe(O
H) Oxidation to 3) reduces dissolved iron in waste liquid.

後で添加する過酸化ナトリウムの水酸化第一鉄による消
費を防止するためである。
This is to prevent sodium peroxide, which will be added later, from being consumed by ferrous hydroxide.

2Fe(OH)z+1/202+H2O−+2Fe(O
H)3   (1)また廃液中のCOD負荷成分である
チオ尿素及びインヒビター(有機アミン系)の酸化分解
でチオ尿素を例にとると下記(2)式の化学反応による
ためと考えられる。インヒビターはその化学式が明確で
ないのでCOD低下に関する酸化分解反応も明らかでな
い。
2Fe(OH)z+1/202+H2O-+2Fe(O
H)3 (1) In addition, it is thought that this is due to the chemical reaction of the following formula (2), taking thiourea as an example, due to the oxidative decomposition of thiourea, which is a COD loading component in the waste liquid, and the inhibitor (organic amine type). Since the chemical formula of the inhibitor is not clear, the oxidative decomposition reaction associated with COD reduction is also unclear.

(NH2)2C8+7NazOz+4H20−+Na2
SO4+12NaOH+ N2 +C02(2) 過酸化す) IJウムのみによる(2)式の酸化反応は
長時間を要する欠点があるが9粒状の活性炭を併用添加
することにより (2)式の酸化分解反応上効果的に促
進することを実験により確かめた。
(NH2)2C8+7NazOz+4H20-+Na2
SO4 + 12NaOH + N2 +C02 (2) (peroxidation) The oxidation reaction of formula (2) using only IJ has the drawback of requiring a long time, but by adding 9 grains of activated carbon together, the oxidative decomposition reaction of formula (2) is effective. It has been confirmed through experiments that it promotes

活性炭の併用による酸化分解の相乗効果は触媒作用によ
るためと考えられる。
The synergistic effect of oxidative decomposition due to the combined use of activated carbon is thought to be due to the catalytic action.

(発明の効果) 本発明は上記のように水酸化カルシウム及び水酸化ナト
リウムなどのアルカリ剤を添加して重金属、りん酸塩の
沈殿物を生成させたアルカリ廃液に過酸化ナトリウムと
粒状活性炭を併用添加することにより、COD成分の酸
化分解を効果的に促進できる利点があシ、シかも、排水
基準値を十分に満足するので処理済みの液は排出するに
際し、希釈及びPH調整の必要もなくそのまま放流する
ことができる。
(Effects of the Invention) As described above, the present invention uses a combination of sodium peroxide and granular activated carbon to the alkaline waste liquid that has been produced by adding alkaline agents such as calcium hydroxide and sodium hydroxide to generate precipitates of heavy metals and phosphates. Adding it may have the advantage of effectively promoting the oxidative decomposition of COD components, but it also satisfies the wastewater standard values, so there is no need to dilute or adjust the pH of the treated liquid when discharging it. It can be released as is.

本発明は、火力プラント、化学プラント等のボイラ、熱
交換器その他の金属製品の塩酸洗浄液及び防錆液を含む
化学洗浄廃液の処理等に利用できるものである。
INDUSTRIAL APPLICATION This invention can be utilized for the treatment of the chemical cleaning waste liquid containing the hydrochloric acid cleaning liquid and rust prevention liquid of the boiler of thermal power plants, chemical plants, etc., heat exchangers, and other metal products.

(実施例) 第1表に示した組成及び性状の化学洗浄廃液を対象とし
て行なったもので、これら廃液1tに水酸化カルシウム
を廃液中のりん酸イオンに対し11当量添加し、さらに
40%水酸化ナトリウム溶液を加えてPHを7以上にな
るように調整し、りん酸カルシウム、水酸化第−鉄及び
水酸化銅の沈殿ケ生成させた。
(Example) This was carried out using chemical cleaning waste liquids having the composition and properties shown in Table 1. To 1 ton of these waste liquids, calcium hydroxide was added in an amount of 11 equivalents to the phosphate ions in the waste liquid, and 40% water was added. A sodium oxide solution was added to adjust the pH to 7 or higher to form precipitates of calcium phosphate, ferrous hydroxide, and copper hydroxide.

次に空気吹き込みによって沈殿物とともに液を強制攪拌
して水酸化第一鉄を水酸化第二鉄に十分酸化したのち、
廃液中のCODに対し添加する過酸化ナトリウムの当量
比及び粒状活性炭の併用添加量を種々かえて添加し、空
気吹き込みによって強制的に2時間攪拌したのち、空気
吹き込みを止めて沈殿物を沈降させ、その上澄液を硫酸
液で中和した処理水のCOD、溶解鉄、銅。
Next, the liquid is forcibly stirred together with the precipitate by blowing air to sufficiently oxidize the ferrous hydroxide to ferric hydroxide.
The equivalent ratio of sodium peroxide added to the COD in the waste liquid and the amount of granular activated carbon added were varied, and the mixture was forcibly stirred for 2 hours by air blowing, and then the air blowing was stopped to allow the precipitate to settle. , COD, dissolved iron, and copper of treated water whose supernatant was neutralized with sulfuric acid solution.

シん酸イオン及びSS(固形浮遊物)を測定し。Measure phosphate ions and SS (solid suspended solids).

第3表の如き結果を得た。第3表において、試験番号1
〜8までの第1ブロツクは第1表に示す銅分を含有しな
いスケールの化学洗浄混合廃液、試験番号9〜16の第
2ブロツクは第1表に示す銅分を含有するスケールの化
学洗浄混合廃液である。また試験番号1.9は上記各ブ
ロックの無処理の化学洗浄廃液で、第1表の混合廃液4
の性状を参考までに示すものである。
The results shown in Table 3 were obtained. In Table 3, test number 1
The first block up to 8 is a chemical cleaning mixed waste solution of scale that does not contain copper as shown in Table 1, and the second block of test numbers 9 to 16 is a chemical cleaning mixture of scale containing copper as shown in Table 1. It is waste liquid. In addition, test number 1.9 is the untreated chemical cleaning waste liquid from each block above, and is the mixed waste liquid 4 in Table 1.
The properties are shown for reference.

なお、塩酸洗浄液のインヒビターには、ヒビロンA−1
00(アミン系酸洗用防食剤、杉村化学工業株式会社製
、商品名)を用いているが。
In addition, the inhibitor of hydrochloric acid cleaning solution is Hibilon A-1.
00 (amine-based pickling anticorrosive agent, manufactured by Sugimura Chemical Industry Co., Ltd., trade name) is used.

他社製品を使用した場合でも第3表と同等の結果が得ら
れ、脱脂剤には、プライサーフA215C(ポリエチレ
ンクリコールエーテル、第−工業製薬株式会社製、商品
名)を用いているが、他社製品を使用した場゛合でも第
3表と同等の結果が得られた。
Results similar to those in Table 3 were obtained even when other companies' products were used, and the degreaser used was Plysurf A215C (polyethylene glycol ether, manufactured by Dai-Kogyo Seiyaku Co., Ltd., trade name); Results equivalent to those in Table 3 were obtained even when the product was used.

試験結果の第3表より下記のことが判明した。From Table 3 of the test results, the following was found.

(1)試験番号2〜8の・化学洗浄廃液及び試験番号1
0〜16の化学洗浄廃液の倒れも廃液中のりん酸イオン
に対し水酸化カルシウムを当量以上添加し、さらに水酸
化ナトリウム溶液を添加してPH7以上に調整し、また
廃液中のCODに対し過酸化ナトリウムを当量と粒状の
活性炭を廃液IRに対し005胸以上併用添加すること
によシ、処理水のCOD、溶解鉄、銅。
(1) Chemical cleaning waste liquid of test numbers 2 to 8 and test number 1
For the collapse of chemical cleaning waste liquids of 0 to 16, calcium hydroxide is added in an amount equivalent to or more than the phosphate ions in the waste liquid, and sodium hydroxide solution is further added to adjust the pH to 7 or higher, and the COD in the waste liquid is adjusted to pH 7 or higher. By adding an equivalent amount of sodium oxide and granular activated carbon to the waste liquid IR, the COD, dissolved iron, and copper of the treated water can be reduced.

りん酸イオン、SSの何れも第2表の排水基準値を十分
に満足するので処理済みの液は排出に際し希釈及びPH
調整の必要もなくそのまま海域に放流することができる
ものである。
Both phosphate ions and SS fully satisfy the wastewater standard values in Table 2, so the treated liquid must be diluted and pH adjusted before discharging.
It can be released into the ocean as is without the need for adjustment.

風下奈白Kazeta Nahaku

Claims (1)

【特許請求の範囲】[Claims] 塩酸洗浄液及びりん酸系の防錆液を含む化学洗浄廃液を
処理するにあたり、上記廃液にカルシウム化合物及びア
ルカリ剤を添加してPH7以上に調整し、廃液中の重金
属及びりん酸塩を重金属水酸化物及びりん酸カルシウム
として沈殿生成させ、生成した水酸化第一鉄を空気吹き
込みによって水酸化第二鉄に酸化したのち、廃液中のC
ODに対して過酸化ナトリウムを当量以上及び粒状の活
性炭を廃液1m^3に対し0.05Kg以上添加してC
ODを酸化分解することを特徴とする化学洗浄廃液の処
理方法。
When treating chemical cleaning waste liquid containing hydrochloric acid cleaning liquid and phosphoric acid-based rust preventive liquid, calcium compounds and alkaline agents are added to the waste liquid to adjust the pH to 7 or higher, and heavy metals and phosphates in the waste liquid are removed by heavy metal hydroxide. C in the waste liquid is precipitated as carbon and calcium phosphate, and the generated ferrous hydroxide is oxidized to ferric hydroxide by air blowing.
C
A method for treating chemical cleaning waste liquid characterized by oxidizing and decomposing OD.
JP13362384A 1984-06-28 1984-06-28 Treatment of waste liquid of chemical cleaning Pending JPS6111193A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP13362384A JPS6111193A (en) 1984-06-28 1984-06-28 Treatment of waste liquid of chemical cleaning

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP13362384A JPS6111193A (en) 1984-06-28 1984-06-28 Treatment of waste liquid of chemical cleaning

Publications (1)

Publication Number Publication Date
JPS6111193A true JPS6111193A (en) 1986-01-18

Family

ID=15109143

Family Applications (1)

Application Number Title Priority Date Filing Date
JP13362384A Pending JPS6111193A (en) 1984-06-28 1984-06-28 Treatment of waste liquid of chemical cleaning

Country Status (1)

Country Link
JP (1) JPS6111193A (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2002036500A3 (en) * 2000-11-02 2003-02-20 Kruger Inc I Method and apparatus for treatment of water and wastewater
CN105293808A (en) * 2015-12-03 2016-02-03 湖北平安电工股份有限公司 Method for extracting n-butyl alcohol in concentrated acid wastewater
CN106186601A (en) * 2016-07-26 2016-12-07 四川高绿平环境科技有限公司 A kind of processing method of mud
CN108558035A (en) * 2018-03-30 2018-09-21 河南金盾环保设备安装工程有限公司 A kind of heavy metal-polluted water treatment agent and preparation method thereof

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2002036500A3 (en) * 2000-11-02 2003-02-20 Kruger Inc I Method and apparatus for treatment of water and wastewater
KR100851456B1 (en) * 2000-11-02 2008-08-08 오떼베 에스아 Method and apparatus for treatment of water
CN105293808A (en) * 2015-12-03 2016-02-03 湖北平安电工股份有限公司 Method for extracting n-butyl alcohol in concentrated acid wastewater
CN106186601A (en) * 2016-07-26 2016-12-07 四川高绿平环境科技有限公司 A kind of processing method of mud
CN106186601B (en) * 2016-07-26 2019-02-26 四川高绿平环境科技有限公司 A kind of processing method of sludge
CN108558035A (en) * 2018-03-30 2018-09-21 河南金盾环保设备安装工程有限公司 A kind of heavy metal-polluted water treatment agent and preparation method thereof

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