JPH06130570A - Method for purifying waste photographic developer - Google Patents

Method for purifying waste photographic developer

Info

Publication number
JPH06130570A
JPH06130570A JP4315486A JP31548692A JPH06130570A JP H06130570 A JPH06130570 A JP H06130570A JP 4315486 A JP4315486 A JP 4315486A JP 31548692 A JP31548692 A JP 31548692A JP H06130570 A JPH06130570 A JP H06130570A
Authority
JP
Japan
Prior art keywords
solution
processing
waste liquid
developer
ppm
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
JP4315486A
Other languages
Japanese (ja)
Inventor
Takao Katsuragi
隆夫 桂木
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.)
Individual
Original Assignee
Individual
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 Individual filed Critical Individual
Priority to JP4315486A priority Critical patent/JPH06130570A/en
Publication of JPH06130570A publication Critical patent/JPH06130570A/en
Pending legal-status Critical Current

Links

Abstract

PURPOSE:To easily purify a waste developer to the quality fulfilling the waste water quality standard by flocculating and removing the contaminant with various chemicals and electrolytically oxidizing/reducing the treated water. CONSTITUTION:This treating device consists of one reaction tank 1, one sludge filtering tank 2 and one treated water tank 3. One to three kinds among a melamine-formalin resin colloid, aq. aluminum sulfate, aq. aluminum polychloride, aq. ferric polysulfate, aq. sodium hydroxide, fine-powder activated carbon suspension, anionic high molecular flocculant and nonionic high molecular flocculant are selected in accordance with the kind of developer and treating stage and used in specified amts. The primarily, secondarily and tertiarily treated developer and the developer not treated with liq. chemicals are electrolytically oxidized/reduced.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は写真フィルム類の現像液
の浄化処理に関するものである。現在の写真現像液は数
種類に分類されるが、そのいずれも薬品および金属類が
多様かつ濃厚に含有されているため、それらの浄化処理
は甚だ困難であるとされ、現在は特殊産業廃棄物として
国際的取り決めにもとづいて海洋投棄が行われているも
のである。しかしながら、1995年以降この海洋投棄
は禁止となるために、それを無公害化するための処理方
法の開発は早急の課題となっている。現在我が国におけ
る現像廃液の発生場所は市井の写真現像業者、病院レン
トゲン現像現場、オフセット印刷現像現場等数万カ所に
およぶと推計されており、これらの場所で発生する現像
廃液はすべて産業廃棄物業者にわたされ、海洋投棄処分
されているのが現状である。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a cleaning treatment of a developing solution for photographic films. Currently, photographic developers are classified into several types, but all of them contain various chemicals and metals in a rich and concentrated manner, and it is said that their purification processing is extremely difficult, and now they are treated as special industrial waste. Ocean dumping is carried out based on international agreements. However, since 1995, this ocean dumping has been banned, so the development of a treatment method for making it pollution-free is an urgent issue. It is estimated that there are tens of thousands of places where development waste liquids are generated in Japan, such as photo development companies in Ichii, hospital X-ray development sites, offset printing development sites, etc., and all development waste liquids generated in these places are industrial waste companies. The current situation is that they have been dumped and dumped at sea.

【0002】[0002]

【従来の技術】従来、この廃液の処理方法として、廃液
中の銀の抽出を行う技術があったが、今は経済的理由で
ほとんど行われていない。また、近年廃液を蒸留濃縮し
た後、乾燥焼却する方法が試みられているが、いまだ、
ほとんど実用化されていないのが実状である。このよう
にいまだ見るべき浄化処理手段の開発が遅れている理由
は、これらの現像液はすべて多様な薬品類と金属類を多
量に含有するきわめて複雑な内容のものであるために、
きわめて特殊な産業廃液として従来の廃水処理技術のら
ち外に置かれていたことによるものである。
2. Description of the Related Art Conventionally, as a method for treating this waste liquid, there has been a technique for extracting silver in the waste liquid, but at present, it is hardly used for economic reasons. In addition, a method of distilling and concentrating the waste liquid and then incineration by drying has been attempted in recent years, but still,
The reality is that it has hardly been put to practical use. The reason why the development of the purification treatment means to be seen is still delayed is that all of these developers have extremely complicated contents containing a large amount of various chemicals and metals.
This is because it was placed outside the conventional wastewater treatment technology as a very special industrial waste liquid.

【0003】[0003]

【発明が解決しようとする課題】本発明が解決しようと
する課題は2点に集約される。 (1) 現像廃液の水質を河川放流基準を満たす水質ま
でに浄化処理すること。 (2) 処理方法が比較的容易で特別な技術者を必要と
せず、特に危険な薬品類を用いない処理方法であるこ
と。
The problems to be solved by the present invention are summarized in two points. (1) Purify the waste effluent so that it meets the river discharge standards. (2) The treatment method is relatively easy, requires no special technician, and does not use particularly dangerous chemicals.

【0004】[0004]

【課題を解決するための手段】[Means for Solving the Problems]

(1) 使用する薬品の種類が下記の通りである。 メラミンフォルマリン樹脂コロイド 硫酸アルミニウム溶液 ポリ塩化アルミニウム溶液 ポリ硫酸第2鉄溶液 燐酸2ナトリウム、燐酸ナトリウム溶液 水酸化ナトリウム溶液 微粉末活性炭懸濁液 アニオン系高分子凝集剤 ノニオン系高分子凝集剤 以上9種類の薬品類は対象となる現像液の種類と各処理
段階によって、そのうちの1種類ないし3種類を選択使
用するものである。 (2) 薬品の使用量は一定ではないが、各薬品ともお
およそ従来の廃水処理技術の使用水準の数10倍ないし
数100倍にのぼる高水準をその使用量とするものであ
る。 (3) 処理は各廃液とも第1処理、第2処理の段階に
分けて段階順に行い、必要な場合、さらに第3処理を行
う。 (4) 上記の各段階処理はすべて同一装置内で行うも
のである。
(1) The types of chemicals used are as follows. Melamine formalin resin colloid Aluminum sulfate solution Poly aluminum chloride solution Poly ferric sulfate solution Disodium phosphate, sodium phosphate solution Sodium hydroxide solution Fine powder activated carbon suspension Anion polymer flocculant Nonion polymer flocculant 9 types above The chemicals are selected from one to three types depending on the type of developing solution and each processing step. (2) Although the amount of chemicals used is not constant, the amount of chemicals used is approximately 10 to 100 times higher than the level of conventional wastewater treatment technology. (3) The treatment is performed for each of the waste liquids in the order of the first treatment and the second treatment, and the third treatment is further performed if necessary. (4) All of the above-mentioned steps are performed in the same device.

【0005】[0005]

【作用】本処理方法の内容とする作用は次の2つであ
る。1つは上記各種薬液の作用によって行うきわめて強
い汚染物質の凝集除去作用であり、今1つは活性炭との
併用によって行う吸着除去作用である。
The function of the present processing method is the following two functions. One is the action of removing and removing extremely strong contaminants by the action of the above-mentioned various chemicals, and the other is the action of removing by adsorption in combination with activated carbon.

【0006】[0006]

【実施例】【Example】

(1) 第1次処理工程の1例 (イ)原水(濃厚黒赤濁液)100lに対し 添加量 メラミン樹脂コロイド液(10%)10l 高分子凝集剤(アニオン)(0.1%) 5l (ロ)1次処理水(薄茶色透明) (2) 第2次処理工程の1例 (イ)1次処理水(茶色弱濁)100lに対し 添加量 ポリ塩化アルミニウム(10%) 3l 燐酸2ナトリウム(10%) 4l 高分子凝集剤(0.1%) 2l 微粉末活性炭(20%) 25l (ロ)2次処理水(淡黄色透明) (3)第3次処理工程の1例 (イ)2次処理水(黄緑色)100lに対し 添加量 硫酸アルミニウム(10%) 2l 燐酸2ナトリウム(10%) 3l 微粉末活性炭(20%) 20l (ロ)3次処理水(無色透明) (1) One example of the first treatment process (a) Addition amount to 100 liters of raw water (concentrated black turbid liquid) Melamine resin colloidal solution (10%) 10 liters Polymer flocculant (anion) (0.1%) 5 liters (B) Primary treated water (transparent to light brown) (2) Example of secondary treatment process (a) Addition amount to 100 l of primary treated water (brown turbidity) Polyaluminum chloride (10%) 3 l Phosphoric acid 2 Sodium (10%) 4l Polymeric flocculant (0.1%) 2l Fine powder activated carbon (20%) 25l (b) Secondary treated water (transparent pale yellow) (3) One example of the third treatment step (a) ) Addition amount to 100l of secondary treated water (yellow green) Aluminum sulfate (10%) 2l Disodium phosphate (10%) 3l Fine powder activated carbon (20%) 20l (b) Third treated water (colorless transparent)

【0007】[0007]

【発明の効果】【The invention's effect】

(1)濃黒赤色の汚濁現像液を微黄色透明ないし無色透
明の液とし、その水質は各項目毎に基準値以下とするこ
とができる。 (2)その処理水は簡単な構造(図面参照)の処理装置
の中で処理が行われ、所要時間は2段階処理の場合は約
10分、3段階処理の場合約15分で完了する。 (3)原液の流送、薬液類の添加はすべて自動制御によ
って行われ、人手を要する作業はごくわずかである。
(1) The dark black red contaminated developer may be a slightly yellow transparent or colorless transparent liquid, and the water quality may be below the reference value for each item. (2) The treated water is treated in a treatment device having a simple structure (see the drawing), and the required time is about 10 minutes for the two-step treatment and about 15 minutes for the three-step treatment. (3) The flow of the stock solution and the addition of the chemicals are all performed by automatic control, and the work that requires manpower is extremely small.

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

[図1]処理装置の構造図である。 FIG. 1 is a structural diagram of a processing device.

【符号の説明】[Explanation of symbols]

1 反応槽 2 スラッジ槽 3 処
理水槽 4 攪拌機 5 スラッジフィルター 6 流
送ポンプ 7 薬品タンク 8 薬品タンク 9 薬
品タンク 10 薬品タンク 11 薬品タンク 12
架台足場
1 Reaction Tank 2 Sludge Tank 3 Treated Water Tank 4 Stirrer 5 Sludge Filter 6 Flow Pump 7 Chemical Tank 8 Chemical Tank 9 Chemical Tank 10 Chemical Tank 11 Chemical Tank 12
Pedestal scaffolding

─────────────────────────────────────────────────────
─────────────────────────────────────────────────── ───

【手続補正書】[Procedure amendment]

【提出日】平成5年8月16日[Submission date] August 16, 1993

【手続補正1】[Procedure Amendment 1]

【補正対象書類名】明細書[Document name to be amended] Statement

【補正対象項目名】全文[Correction target item name] Full text

【補正方法】変更[Correction method] Change

【補正内容】[Correction content]

【書類名】 明細書[Document name] Statement

【発明の名称】 写真現像廃液の浄化処理方法Title: Method for purifying photographic developer waste liquid

【特許請求の範囲】[Claims]

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は写真フィルム類の現像液
の浄化処理に関するものである。現在の写真現像液は数
種類に分類されるが、そのいずれも薬品および金属類が
多様かつ濃厚に含有されているため、それらの浄化処理
は甚だ困難であるとされ、現在は特殊産業廃棄物として
国際的取り決めにもとづいて海洋投棄が行われているも
のである。しかしながら、1995年以降この海洋投棄
は禁止となるために、それを無公害化するための処理方
法の開発は早急の課題となっている。現在我が国におけ
る現像廃液の発生場所は市井の写真現像業者、病院レン
トゲン現像現場、オフセット印刷現像現場等数万カ所に
およぶと推計されており、これらの場所で発生する現像
廃液はすべて産業廃棄物業者にわたされ、海洋投棄処分
されているのが現状である。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a cleaning treatment of a developing solution for photographic films. Currently, photographic developers are classified into several types, but all of them contain various chemicals and metals in a rich and concentrated manner, and it is said that their purification processing is extremely difficult, and now they are treated as special industrial waste. Ocean dumping is carried out based on international agreements. However, since 1995, this ocean dumping has been banned, so the development of a treatment method for making it pollution-free is an urgent issue. It is estimated that there are tens of thousands of places where development waste liquids are generated in Japan, such as photo development companies in Ichii, hospital X-ray development sites, and offset printing development sites, and all the development waste liquids generated in these places are industrial waste companies. The current situation is that they have been dumped and dumped at sea.

【0002】[0002]

【従来の技術】従来、この廃液の処理方法として、廃液
中の銀の抽出を行う技術があったが、今は経済的理由で
ほとんど行われていない。また、近年廃液を蒸留濃縮し
た後、乾燥焼却する方法が試みられているが、いまだ、
ほとんど実用化されていないのが実状である。このよう
にいまだ見るべき浄化処理手段の開発が遅れている理由
は、これらの現像液はすべて多様な薬品類と金属類を多
量に含有するきわめて複雑な内容のものであるために、
きわめて特殊な産業廃液として従来の廃水処理技術のら
ち外に置かれていたことによるものである。
2. Description of the Related Art Conventionally, as a method for treating this waste liquid, there has been a technique for extracting silver in the waste liquid, but at present, it is hardly used for economic reasons. In addition, a method of distilling and concentrating the waste liquid and then incineration by drying has been attempted in recent years, but still,
The reality is that it has hardly been put to practical use. The reason why the development of the purification treatment means to be seen is still delayed is that all of these developers have extremely complicated contents containing a large amount of various chemicals and metals.
This is because it was placed outside the conventional wastewater treatment technology as a very special industrial waste liquid.

【0003】[0003]

【発明が解決しようとする課題】本発明が解決しようと
する課題は2点に集約される。 (1) 現像廃液の水質を河川放流基準を満たす水質ま
でに浄化処理すること。 (2) 処理方法が比較的容易で特別な技術者を必要と
せず、特に危険な薬品類を用いない処理方法であるこ
と。
The problems to be solved by the present invention are summarized in two points. (1) Purify the waste effluent so that it meets the river discharge standards. (2) The treatment method is relatively easy, requires no special technician, and does not use particularly dangerous chemicals.

【0004】[0004]

【課題を解決するための手段】 (1) 使用する薬品の種類が下記の通りである。 メラミンフォルマリン樹脂コロイド 硫酸アルミニウム溶液 ポリ塩化アルミニウム溶液 ポリ硫酸第2鉄溶液 燐酸2ナトリウム、燐酸ナトリウム溶液 水酸化ナトリウム溶液 微粉末活性炭懸濁液 アニオン系高分子凝集剤 ノニオン系高分子凝集剤 以上9種類の薬品類は対象となる現像液の種類と各処理
段階によって、そのうちの1種類ないし3種類を選択使
用するものである。 (2) 処理は各廃液とも第1次処理、第2次処理の段
階に分けて段階順に行い、必要な場合、さらに第3次処
理を行う。 (3) 第1次処理後または第2次・第3次処理後の現
像液およびこれらの薬液処理を行わない現像液に対し、
その液の電気分解を行うことによって処理液の酸化・還
元処理を行う。この処理に要する電力量ないし作用時間
は処理水の汚染の程度によって定める。 (4) 上記の各段階処理は特別の場合を除きすべて同
一装置内で行うものである。
[Means for Solving the Problems] (1) The types of chemicals used are as follows. Melamine formalin resin colloid Aluminum sulfate solution Poly aluminum chloride solution Poly ferric sulfate solution Disodium phosphate, sodium phosphate solution Sodium hydroxide solution Fine powder activated carbon suspension Anion polymer flocculant Nonion polymer flocculant 9 types above The chemicals are selected from one to three types depending on the type of developing solution and each processing step. (2) Treatment of each waste liquid is performed in the order of the primary treatment and the secondary treatment, and if necessary, the tertiary treatment is further performed. (3) For the developer after the first treatment or after the second and third treatments and the developer not subjected to the chemical treatment,
The solution is electrolyzed to oxidize / reduce the processing solution. The amount of electricity and the operating time required for this treatment are determined by the degree of contamination of the treated water. (4) The above-mentioned steps are all performed in the same apparatus except for special cases.

【0005】[0005]

【作用】本処理方法の内容とする作用は主として次の2
つである。1つは上記各種薬液の作用によって行う汚染
物質の凝集除去作用であり、今1つは処理水の電気分解
による酸化・還元作用である。
[Function] The function of the present processing method is mainly described in the following 2
Is one. One is an action of aggregating and removing contaminants performed by the action of the above-mentioned various chemical solutions, and the other is an action of oxidation / reduction by electrolysis of treated water.

【0006】[0006]

【実施例】 (1) 第1次処理工程の1例 (イ)原水(濃厚黒赤濁液)100gに対し 添加量 メラミン樹脂コロイド液(10%)10l 高分子凝集剤(アニオン)(0.1%) 5l (ロ)1次処理水(薄茶色透明) (2) 第2次処理工程の1例 (イ)1次処理水(茶色弱濁)100gに対し 添加量 ポリ塩化アルミニウム(10%) 3l 燐酸2ナトリウム(10%) 4l 高分子凝集剤(0.1%) 2l 微粉末活性炭 10l (ロ)2次処理水(淡黄色透明) (3)電気分解処理工程の1例 (イ)2次処理水に対し、反応槽の底辺に設けた電極
(陽極板0.2dm25枚、陰極板0.25dm26
枚)に電圧20V、電流30A程度の直流電流を通じる
ことによって、その電気分解を行い、初期の目標の値に
低下するまで継続する。(一般に30分〜2時間であ
る) (ロ)3次処理水(無色透明)
Examples (1) One example of the first treatment step (a) Addition amount to 100 g of raw water (thick black turbid liquid) Melamine resin colloid liquid (10%) 10 l Polymer flocculant (anion) (0. 1%) 5l (b) Primary treated water (light brown transparent) (2) Example of secondary treatment process (a) Addition amount to 100 g of primary treated water (brown slightly turbid) Polyaluminum chloride (10% ) 3l Disodium phosphate (10%) 4l Polymer flocculant (0.1%) 2l Fine powder activated carbon 10l (b) Secondary treated water (pale yellow transparent) (3) One example of electrolysis treatment step (a) Electrodes (0.2 dm25 anode plate, 0.25 dm26 cathode plate) provided at the bottom of the reaction tank for the secondary treated water.
By passing a direct current with a voltage of about 20 V and a current of about 30 A to each sheet, the electrolysis is performed and the electrolysis is continued until the initial target value is reached. (Generally 30 minutes to 2 hours) (b) Third-order treated water (colorless and transparent)

【0007】[0007]

【発明の効果】 (1)処理水の水質を基準値以下とすることができる。 (2)その処理は簡単な構造(図面参照)の処理装置の
中で処理が行われ、所要時間は2段階処理の場合は約1
0分、電気分解処理の場合約2時間程度である。 (3)原液の流送、薬液類の添加はすべて自動制御によ
って行われ、人手を要する作業はごくわずかである。
EFFECTS OF THE INVENTION (1) The quality of treated water can be kept below a reference value. (2) The processing is performed in a processing device having a simple structure (see the drawing), and the required time is about 1 in the case of two-step processing.
0 minutes, about 2 hours in the case of electrolysis. (3) The flow of the stock solution and the addition of the chemicals are all performed by automatic control, and the work that requires manpower is extremely small.

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

【図1】処理装置の構造図である。FIG. 1 is a structural diagram of a processing device.

【符号の説明】 1 反応槽 2 スラッジ槽 3 処
理水槽 4 攪拌機 5 スラッジフィルター 6 流
送ポンプ 7 薬品タンク 8 薬品タンク 9 薬
品タンク 10 薬品タンク 11 薬品タンク 12
架台足場
[Explanation of symbols] 1 reaction tank 2 sludge tank 3 treated water tank 4 stirrer 5 sludge filter 6 flow pump 7 chemical tank 8 chemical tank 9 chemical tank 10 chemical tank 11 chemical tank 12
Pedestal scaffolding

【手続補正2】[Procedure Amendment 2]

【補正対象書類名】図面[Document name to be corrected] Drawing

【補正対象項目名】全図[Correction target item name] All drawings

【補正方法】変更[Correction method] Change

【補正内容】[Correction content]

【図1】 [Figure 1]

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.5 識別記号 庁内整理番号 FI 技術表示箇所 C02F 9/00 ZAB 7446−4D ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 5 Identification code Office reference number FI technical display location C02F 9/00 ZAB 7446-4D

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 写真現像廃液に対し、メラミンフォル
マリン樹脂コロイド、ポリ塩化アルミニウム液、硫
酸アルミニウム液、ポリ疏酸第2鉄液 燐酸ナトリ
ウム液 水酸化ナトリウム液 活性炭微粉末 ア
ニオン系高分子凝集剤 ノニオン系高分子凝集剤のう
ち1種類ないし3種類を添加し、かつ、その添加量を対
象処理水の水量に対し、おおよその場合純分比 50
ppm以上、 の場合は純分比 1000ppm
以上、 の場合は純分比500ppm以上、の場
合は純分比 10,000ppm以上、 の場合は
純分比 20ppm以上の比率で添加することによって
凝集作用を行うことを特徴とする現像廃液処理方法
1. A melamine formalin resin colloid, a polyaluminum chloride solution, an aluminum sulfate solution, a polyferric acid ferric acid solution, a sodium phosphate solution, a sodium hydroxide solution, an activated carbon fine powder, an anionic polymer flocculant, and nonion for the photographic development waste solution. One to three types of macromolecular flocculants are added, and the amount of addition is approximately 50% of the water content of the target treated water.
In case of ppm or more, the pure content ratio is 1000ppm
As described above, in the case of, a pure content ratio of 500 ppm or more, in the case of, a pure content ratio of 10,000 ppm or more, and in the case of a pure content ratio of 20 ppm or more, a coagulation action is carried out, and a developing waste liquid treatment method is characterized.
【請求項2】 廃液の処理を第1処理段階、第2処理段
階ないし第3処理段階の順序で行い、各処理段階とも同
一装置の中で行う写真現像廃液の処理方法
2. A method of processing a photographic waste liquid, wherein the waste liquid is processed in the order of a first processing step, a second processing step to a third processing step, and each processing step is carried out in the same apparatus.
【請求項3】 1個の反応槽、1個のスラッジ▲ろ▼過
槽および1個の処理水槽をもって構成され、この順序で
処理水が循環されることを特徴とする写真現像廃液処理
装置の構造
3. A photographic waste liquid processing apparatus comprising one reaction tank, one sludge filtration tank and one processing water tank, wherein the processing water is circulated in this order. Construction
JP4315486A 1992-10-14 1992-10-14 Method for purifying waste photographic developer Pending JPH06130570A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP4315486A JPH06130570A (en) 1992-10-14 1992-10-14 Method for purifying waste photographic developer

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP4315486A JPH06130570A (en) 1992-10-14 1992-10-14 Method for purifying waste photographic developer

Publications (1)

Publication Number Publication Date
JPH06130570A true JPH06130570A (en) 1994-05-13

Family

ID=18065951

Family Applications (1)

Application Number Title Priority Date Filing Date
JP4315486A Pending JPH06130570A (en) 1992-10-14 1992-10-14 Method for purifying waste photographic developer

Country Status (1)

Country Link
JP (1) JPH06130570A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105600901A (en) * 2015-12-18 2016-05-25 天津大学 Preparation method of ammonium chloride-modified melamine resin decolorant
CN106698748A (en) * 2016-12-26 2017-05-24 骆昌盛 Preparation, device and treatment method for treating CTP developing effluent

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105600901A (en) * 2015-12-18 2016-05-25 天津大学 Preparation method of ammonium chloride-modified melamine resin decolorant
CN106698748A (en) * 2016-12-26 2017-05-24 骆昌盛 Preparation, device and treatment method for treating CTP developing effluent

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