JPS5855542A - Treatment of photographic waste liquid - Google Patents

Treatment of photographic waste liquid

Info

Publication number
JPS5855542A
JPS5855542A JP15415181A JP15415181A JPS5855542A JP S5855542 A JPS5855542 A JP S5855542A JP 15415181 A JP15415181 A JP 15415181A JP 15415181 A JP15415181 A JP 15415181A JP S5855542 A JPS5855542 A JP S5855542A
Authority
JP
Japan
Prior art keywords
silver
waste liquid
chelating agent
carrier
photographic waste
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
JP15415181A
Other languages
Japanese (ja)
Other versions
JPS6367529B2 (en
Inventor
Hisashi Tanaka
久 田中
Masahiko Chiguma
正彦 千熊
Morio Nakayama
守雄 中山
Nobuo Sanmi
三位 信夫
Katsumi Imada
勝美 今田
Takashi Yamamoto
隆司 山本
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.)
Daiichi Pharmaceutical Co Ltd
Original Assignee
Daiichi Pharmaceutical 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 Daiichi Pharmaceutical Co Ltd filed Critical Daiichi Pharmaceutical Co Ltd
Priority to JP15415181A priority Critical patent/JPS5855542A/en
Publication of JPS5855542A publication Critical patent/JPS5855542A/en
Publication of JPS6367529B2 publication Critical patent/JPS6367529B2/ja
Granted legal-status Critical Current

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  • Silver Salt Photography Or Processing Solution Therefor (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)
  • Manufacture And Refinement Of Metals (AREA)

Abstract

PURPOSE:To easily recover silver from photographic waste liquid and to enable to reuse said waste liquid, by treating the photographic waste liquid with anion exchange resin supporting a certain kind of a sulfur-contg. chelating agent. CONSTITUTION:Silver is wrested and recovered from the extremely stable complex salt of silver thiosulfate contained in photographic waste liquid, by treating the waste liquid with anion exchange resin supporting a sulfur-contg. chelating agent represented by the general formula (in the formula, each of X and Y independently means a sulfonic, carboxylic or hydroxylic group, or one of them is hydrogen atom while the other means a sulfonic, carboxylic or hydroxylic group). Silver adsorbed on the carrier of the sulfur-contg. chelating agent is easily eluted by an eluate such as thiourea, and the carrier can be repeatedly reused. The use amount of the carrier as the sulfur-contg. chelating agent is the same mol as or more than an amount of silver in the photographic waste liquid.

Description

【発明の詳細な説明】 本発明は含硫キレート化剤担持アニオン交換樹脂(以下
「担持体」と称す。)による写真廃液の処理法に関する
。即ち、疲労した写真用定着液、同漂白定着液あるいは
漂白、漂白定着操作後の水洗水などの廃液を本担持体で
処理して。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for treating photographic waste liquid using an anion exchange resin supporting a sulfur-containing chelating agent (hereinafter referred to as "support"). That is, waste liquids such as tired photographic fixers, bleach-fixers, or washing water after bleaching and bleach-fixing operations are treated with the present carrier.

該廃液中の銀の回収を、更には該廃液の再利用を目的と
した写真廃液の処理方法に関する0周知のごとく、写真
業界においては膨大な量の銀が使用されている。しかし
ながら銀資源の枯渇あるいは銀価格の高騰などの面から
t写真廃液中の銀の回収再利用が強く要望されている現
状である。また、水質汚染の防止写真処理に用いられた
薬品類の有効活用、水資源の確保などの面から廃液の循
環再利用も重要視されているO 現在、写真廃液から銀を回収する方法としては、硫化水
素法、電解法、イオン交換樹脂法あるいは置換法(イオ
ン化傾向を利用する方法で。
As is well known, a huge amount of silver is used in the photographic industry, as is well known regarding the processing method of photographic waste liquid for the purpose of recovering the silver in the waste liquid and furthermore, reusing the waste liquid. However, due to the depletion of silver resources and the rising price of silver, there is a strong demand for the recovery and reuse of silver in photographic waste liquids. In addition, the circulation and reuse of waste liquids is also considered important from the viewpoint of preventing water pollution, making effective use of chemicals used in photographic processing, and securing water resources.Currently, there are no methods for recovering silver from photographic waste liquids. , hydrogen sulfide method, electrolytic method, ion exchange resin method, or substitution method (a method that utilizes ionization tendency).

アルミニウムや鉄などが使われる。)などが知られてい
る。しかしながら、これらの方法は衛生面、設備面1回
収率あるいは回収銀の品質などの面から問題があり、写
真業界では新規回収方法の開発が要望されている現状で
ある。
Aluminum and iron are used. ) etc. are known. However, these methods have problems in terms of hygiene, equipment, recovery rate, and quality of recovered silver, and there is a current demand in the photographic industry for the development of new recovery methods.

写真廃液中における銀は9次の反応式で示すごとく、大
部分が4オ硫酸錯イオンの形で存在する。
Silver in photographic waste liquid is mostly present in the form of tetraosulfate complex ions, as shown by the 9th order reaction formula.

従って写真廃液からの銀の回収が従来円滑に行なわれな
い最も大きな理由は、高濃度の銀が極めて安定な上記錯
イオンの形で存在することに加えて高濃度のハイポ等と
共存するためといわれている。
Therefore, the biggest reason why recovery of silver from photographic waste liquid has not been carried out smoothly in the past is that in addition to the existence of highly concentrated silver in the form of the above-mentioned extremely stable complex ions, it also coexists with high concentrations of hypo, etc. It is said.

そこで本発明者らは極めて安定度の高い銀チオ硫酸錯塩
(イオン)より銀を奪い取る能力を有しかつ写真廃液中
に存在する銀(イオン)以外のその他高濃度成分により
影響を受けない安定な官能基を有する担体を用いた該廃
液処理方法を鋭意検討した結果、ある種の含硫キレート
化剤を担持せしめたアニオン交換樹脂即ち担持体が銀イ
オンならびに銀チオ硫酸錯イオン中の銀に対して優れた
選択的吸着性能を発揮すること、更には上記担持体処理
により銀のみが効率よく回収除去された該廃液は再使用
可能であるという利点を知見し本発明を完成した◎本発
明に係わる担持体の構成々分の−っである含硫キレート
化剤とは次の一般式(A)及び(B)を有するものであ
る。
Therefore, the present inventors developed a stable silver thiosulfate complex (ion) that has the ability to remove silver from extremely stable silver thiosulfate complexes (ions) and is not affected by other highly concentrated components other than silver (ions) present in photographic waste liquid. As a result of intensive investigation into a wastewater treatment method using a carrier having a functional group, we found that an anion exchange resin, that is, a carrier carrying a certain kind of sulfur-containing chelating agent, is effective against silver ions and silver in silver thiosulfate complex ions. The present invention was completed based on the discovery that the waste liquid exhibits excellent selective adsorption performance through the above-mentioned carrier treatment, and that the waste liquid from which only silver is efficiently recovered and removed through the above-mentioned support treatment can be reused. The sulfur-containing chelating agent, which is a component of the related carrier, has the following general formulas (A) and (B).

式中、XおよびYは、各々独立してスルホン酸基、カル
ボキシル基あるいは水酸基を意味するか又はいずれか一
方が水素原子であって他方がスルホン酸基、力、、ルボ
キシル基あるいは水酸基であることを意味する。
In the formula, X and Y each independently represent a sulfonic acid group, a carboxyl group, or a hydroxyl group, or one of them is a hydrogen atom and the other is a sulfonic acid group, a carboxyl group, or a hydroxyl group. means.

尚1式(A)および(B)の化合物は分析試薬としてよ
く知られている式(A)または(B)中XおよびYが共
に水素原子であるジチゾンまたはアゾチオビリンから容
易に合成されるものであり、それらの代表例としてはジ
チゾンスルホン111 (式(A)中XおよびYがスル
ホン酸基を示す。〕(以下「DzS」と称す05)、ア
ゾチオビリンスルホン酸〔式(B)中XおよびYがスル
ホン酸基を示す。〕(以下「ATPS」と称す。)など
が挙げられる。
The compounds of formulas (A) and (B) are easily synthesized from dithizone or azothiovirine, in which X and Y in formula (A) or (B) are both hydrogen atoms, which are well known as analytical reagents. Typical examples thereof include dithizone sulfone 111 (X and Y in formula (A) represent a sulfonic acid group) (hereinafter referred to as "DzS" 05), azothiopyrine sulfonic acid [X in formula (B)] and Y represents a sulfonic acid group.] (hereinafter referred to as "ATPS").

他方の構成々分のアニオン交換樹脂については、特に制
限はなく、市販@塩基性タイプのいずれもが使用できる
が、前記式(A)または(B)中XおよびYの種類に対
応させて用いるのが好ましい。例えば、Xがスルホン酸
基の場合、キレート化剤(A)または伸)の担持量を多
くする目的で強塩基性アニオン交換樹脂が適当である。
The anion exchange resin for the other component is not particularly limited, and any commercially available basic type can be used, but it is used in accordance with the types of X and Y in the above formula (A) or (B). is preferable. For example, when X is a sulfonic acid group, a strongly basic anion exchange resin is suitable for increasing the amount of the chelating agent (A) or chelating agent (A) supported.

キレート化剤(A)または(B)のアニオン交換樹脂へ
の担持は水溶液中にて次のよ−うな簡便な操作で達成で
きる。例えば、樹脂11当りキレート、化剤0.2〜2
mmolを水にとかし、樹脂と振りまぜると試薬の色が
消えた点で吸着担持を終了−する。この時点で、濾取す
れば本発明に供する担持体が調製できる。
Supporting the chelating agent (A) or (B) on the anion exchange resin can be achieved in an aqueous solution by the following simple operation. For example, chelate, curing agent 0.2 to 2 per 11 resin.
When mmol is dissolved in water and mixed with resin, the adsorption and loading is completed when the color of the reagent disappears. At this point, the carrier used in the present invention can be prepared by filtering it.

このようにして調製された相持体は、多量のキレート化
剤が樹脂にイオン交換反応と物理的吸着により担持され
ていることに起因し、安定性や吸着容量などの面で優れ
たものである。
The phase support prepared in this way has excellent stability and adsorption capacity due to the fact that a large amount of the chelating agent is supported on the resin through ion exchange reaction and physical adsorption. .

このようにして調製された担持体の写真廃液中の銀吸着
性能について1代表的なりzS及びATPS 担持アン
バーライト00400の銀チオ硫酸錯イオン溶液におけ
る銀吸着実験を行なった結果2本担持体は銀チオ硫酸錯
イオンに対して優れた銀奪取吸着性能を発揮することを
確認した。
Regarding the silver adsorption performance of the support prepared in this manner in photographic waste liquid, we conducted a silver adsorption experiment in a silver thiosulfate complex ion solution using representative Amberlite 00400 supported on ZS and ATPS. It was confirmed that it exhibited excellent silver scavenging and adsorption performance for thiosulfate complex ions.

本発明を行なうには、疲労の進んだ写真廃液例えば定着
液、漂白定着液の廃液や定着、漂白定着操作後の水洗水
など−i−ネ担持体で処理すればよい@その処理法とし
ては、バッチ法、カラム法が挙げられる。バッチ法の場
合、攪拌もしくは振盪を行ないつ\、@着を行なうのが
好ましし)。
To carry out the present invention, photographic waste liquids with advanced fatigue, such as waste liquids of fixers, bleach-fixers, and washing water after fixing and bleach-fixing operations, can be treated with a -i-ne carrier. , batch method, and column method. In the case of a batch method, it is preferable to carry out the mixing while stirring or shaking).

本担持体の使用量は担持キレ。−ト化剤の種類によって
興なるが、処理廃液に含まれる銀量と同モル乃至それ以
上のキレート化剤を必要とし。
The amount of this carrier used is just enough to support it. - Although it depends on the type of chelating agent, it is necessary to use the same molar amount of chelating agent as the amount of silver contained in the treatment waste liquid or more.

その量が担持された担持体量が必要である。また1g&
着の際温度やpHについては特に配慮を必要とせず広い
範囲で適用可能である。
The amount of support loaded with that amount is required. Also 1g&
No particular consideration is required regarding the temperature or pH during the application, and it can be applied over a wide range.

このようにして担持体で処理された写真廃液は、含有銀
のみが高い吸着率で吸着除去されるので、写真処理液と
して再び使用が可能である。
The photographic waste liquid treated with the carrier in this manner can be reused as a photographic processing liquid since only the silver contained therein is adsorbed and removed at a high adsorption rate.

また、疲労の進んだ写真廃液の処理のみならず写真処理
工程中に1本担持体による処理法を装置的工夫などによ
り組み込み、処理液を連続的に循環再生することも可能
である。
Furthermore, in addition to treating exhausted photographic waste liquid, it is also possible to incorporate a treatment method using a single carrier into the photographic processing process by devising equipment, etc., and to continuously circulate and regenerate the processing liquid.

一方1本担持体に吸着された銀は、樹脂−キレート化剤
−銀の形態で存在すると考えられ。
On the other hand, silver adsorbed on one carrier is considered to exist in the form of resin-chelating agent-silver.

適当な溶離剤で処理すれば樹脂とキレート化剤との結合
に影響を与えることなく溶離でき9本担持体は反復再使
用可能である。その溶離剤としては、銀と可溶性化合物
を形成する試薬9例えばチオ尿素などが挙げられる。溶
離方法としては、銀吸着体を集め、溶離剤の0.1〜5
モル水溶液で処理すればよい。
If treated with a suitable eluent, the resin and chelating agent can be eluted without affecting their binding, and the 9-piece carrier can be repeatedly reused. Examples of the eluent include reagents 9 that form soluble compounds with silver, such as thiourea. As for the elution method, collect the silver adsorbent and add 0.1 to 5 ml of the eluent.
It can be treated with a molar aqueous solution.

以下、実施例を挙げて本発明を説明するが。The present invention will be explained below with reference to Examples.

これらは本発明を説明す名ための例示に過ぎず。These are merely examples to illustrate the invention.

ATPSやDzS以外のキレート北側担持アニオン交換
樹脂の使用や本相持体の写真廃液以外における銀の回収
への適用も可能なものである。
It is also possible to use an anion exchange resin carrying a chelate north side other than ATPS or DzS, and to apply the present carrier to recovery of silver from sources other than photographic waste liquid.

実施例1 チオ硫酸ナトリウム・五水塩49.69.亜硫酸ナトリ
ウムLOりを水で1 l(pH7,0)  となし、こ
の溶液中に硝酸銀を銀として10s9加えて銀チオ硫酸
錯イオン溶液を調製した・この銀錯イオン溶液50−の
各々に対してQ、 2 mrrrol/9樹脂のDzS
又はATPSを担持したアンバーライトCG400の各
&100sI9及び5001119を加え、25℃、N
o分間振盪し、上澄液中の銀濃度を原子吸光法で測定し
吸着率を求め、その結果を第1表に示した。
Example 1 Sodium thiosulfate pentahydrate 49.69. A silver thiosulfate complex ion solution was prepared by diluting sodium sulfite LO to 1 liter (pH 7,0) with water and adding 10s9 of silver nitrate as silver to this solution.For each of this silver complex ion solution 50- Q, 2 mrrrol/9 resin DzS
Or add each &100sI9 and 5001119 of Amberlite CG400 carrying ATPS, and heat at 25°C with N
After shaking for 0 minutes, the silver concentration in the supernatant was measured by atomic absorption spectrometry to determine the adsorption rate, and the results are shown in Table 1.

第1表 銀の吸着率 実施例2 銀1)9が吸着されたDzS (0,2s+uaoVg
樹脂)担持7ンバー5イ)Oct400.ff  を0
.8〜1.2モルチオ尿素液500−にて処理し、@着
された銀の溶離実験を行なった。その結果を第■表に示
した如く良好な銀の脱着率を呈した。
Table 1 Silver adsorption rate Example 2 DzS (0,2s+uaoVg) where silver 1)9 was adsorbed
Resin) Support 7 members 5a) Oct400. ff to 0
.. The sample was treated with 8 to 1.2 molar thiourea solution at a concentration of 500 ml, and an elution experiment of the deposited silver was carried out. As the results are shown in Table 1, a good silver desorption rate was exhibited.

第■表 チオ尿素による銀の脱着 実施例8 チオ硫酸す) 13ウム・五水塩248F、無水亜硫酸
ナトリウム15Fを水に溶解する。この溶液に硝酸銀を
銀として12 Qs9(1,11mmaoz )溶かし
てのち、水で全量1ノとする0このモデル定着廃液を8
等分して次の吸脱着実験8回を行なう。
Table Ⅲ Desorption of silver using thiourea Example 8 Thiosulfate 13um pentahydrate 248F and anhydrous sodium sulfite 15F are dissolved in water. Dissolve 12 Qs9 (1,11 mmaoz) of silver nitrate in this solution, and then add water to make a total volume of 1 mm.
Divide into equal parts and perform the next adsorption/desorption experiment eight times.

即ち、このモデル定着廃液+lをDzS 樹脂充填カラ
ム(DzS (Q、2 mmol/9樹脂)担持アンバ
ーライトCG400,8.59.直径0.8cmのカラ
ム〕に8171/時の流速にて通液した。
That is, this model fixing waste solution +l was passed through a DzS resin-packed column (DzS (Q, 2 mmol/9 resin)-supported Amberlite CG400, 8.59, 0.8 cm diameter column) at a flow rate of 8171/hour. .

また、樹脂に吸着された銀の溶離にはL2モルチオ尿素
を用いた。
Further, L2 mole thiourea was used to elute silver adsorbed on the resin.

銀が溶出された樹脂には、上記モデル定着廃液+lを再
び通液し以下同様に合計8回にわたり吸脱着実験を行な
った。
The model fixing waste solution +l was again passed through the resin from which silver had been eluted, and adsorption and desorption experiments were conducted in the same manner a total of 8 times.

本実験結果を次の第1表に示した。The results of this experiment are shown in Table 1 below.

第1表 モデル定着廃液からの銀の回収〔銀の分析は原
子吸光法により行なった〕実施例4 チオ硫酸アンモニウム100g、エチレンジアミン四酢
酸二ナトリウム49.エチレンジアミン四酢酸鉄II)
錯塩4θg、亜硫酸ナトリウム29、”Iつ化カリウム
1g、チオシアン酸ナトリウム10gおよび20%アン
モニア水10ajを水でlノとする。この漂白定着液に
て現像フィルムの処理を反復打なう。得られた疲労漂白
定着液の銀濃度を原子吸光法で測定すると11.697
1であった。この疲労漂白定着液を。
Table 1 Recovery of silver from model fixing waste solution [Silver analysis was carried out by atomic absorption method] Example 4 Ammonium thiosulfate 100 g, disodium ethylenediaminetetraacetate 49. Iron ethylenediaminetetraacetate II)
4θg of the complex salt, 29g of sodium sulfite, 1g of potassium chloride, 10g of sodium thiocyanate and 10ajj of 20% aqueous ammonia are diluted with water.The developed film is repeatedly treated with this bleach-fix solution. When the silver concentration of the fatigued bleach-fix solution was measured by atomic absorption method, it was 11.697.
It was 1. This fatigue bleach-fix solution.

DzS樹脂充填カラム(D z 8 (0,8mmol
/ g樹脂)担持アンバーライトCG400,189.
直径2CIIのカラム〕に1i/$の流速にて通液した
DzS resin packed column (D z 8 (0,8 mmol
/g Resin) Supported Amberlite CG400,189.
The solution was passed through a column with a diameter of 2 CII at a flow rate of 1 i/$.

その結果、漏出点は75−であり、漏出点までの処理液
中の銀濃度は0.24/l以下であった。
As a result, the leakage point was 75-, and the silver concentration in the treatment liquid up to the leakage point was 0.24/l or less.

一方9本処理液の漂白定着力をテストフィルムにて評価
したところ、第N表の如く本来の漂白定着力を回復する
ことが認められた。
On the other hand, when the bleach-fixing power of the nine treatment solutions was evaluated using test films, it was found that the original bleach-fixing power was recovered as shown in Table N.

第N表 漂白定着液の再生 テストフィルム:7ジ微粒子フィルムに一定の露光を与
えたのち、コダックD−7!(1:4液)にて現像(2
0℃、7分)、水洗、乾燥した悪化In−L78±0.
02の74にムを0.5譚角に切ったもの。
Table N Bleach-fix regeneration test film: After constant exposure to 7-di fine grain film, Kodak D-7! Developed with (1:4 liquid) (2
0° C., 7 minutes), washed with water, and dried degraded In-L78±0.
02's 74 MU cut into 0.5 tan squares.

漂白定着力の評価:テストフィルムを10分間水で膨潤
させ、濾紙で水を切ったのち、25℃に保った漂白定着
液に浸し、無色透明になるまテ(7)時間をストップウ
ォッチで測定する。
Evaluation of bleach-fixing power: Swell the test film with water for 10 minutes, drain the water with a filter paper, then soak it in a bleach-fix solution kept at 25°C, and measure the time it takes to become colorless and transparent (7) using a stopwatch. do.

Claims (1)

【特許請求の範囲】 写真廃液を、一般式 (式中、XおよびYは、各々独立してスルホン酸基、カ
ルボキシル基あるいは水酸基を意味するか又はいずれか
一方が水素原子であって他方がスルホン酸基、カルボキ
シル基あるいは水酸基であることを意味する。)で表わ
される含硫キレート化剤を担持するアニオン交換樹脂で
処理することを特徴とする写真廃液中の銀の回収方法。
[Scope of Claims] Photographic waste liquid is prepared by the general formula (wherein, 1. A method for recovering silver from photographic waste, the method comprising treating it with an anion exchange resin carrying a sulfur-containing chelating agent (meaning an acid group, a carboxyl group or a hydroxyl group).
JP15415181A 1981-09-29 1981-09-29 Treatment of photographic waste liquid Granted JPS5855542A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP15415181A JPS5855542A (en) 1981-09-29 1981-09-29 Treatment of photographic waste liquid

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP15415181A JPS5855542A (en) 1981-09-29 1981-09-29 Treatment of photographic waste liquid

Publications (2)

Publication Number Publication Date
JPS5855542A true JPS5855542A (en) 1983-04-01
JPS6367529B2 JPS6367529B2 (en) 1988-12-26

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Family Applications (1)

Application Number Title Priority Date Filing Date
JP15415181A Granted JPS5855542A (en) 1981-09-29 1981-09-29 Treatment of photographic waste liquid

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Country Link
JP (1) JPS5855542A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS63118025A (en) * 1986-11-06 1988-05-23 Nippon Mining Co Ltd Method for removing or recovering silver
FR2764908A1 (en) * 1997-06-19 1998-12-24 Gerard Gasser PROCESS FOR SEPARATING METAL IONS ABSORBED ON A RESIN AND PROCESS AND PLANT FOR THE TREATMENT AND RECYCLING OF PHOTOGRAPHIC EFFLUENTS
EP2508864A3 (en) * 2011-04-04 2016-06-01 ARKRAY, Inc. Method for recovering metal and kit for recovery of metal for use in the same

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP5889059B2 (en) 2011-04-04 2016-03-22 アークレイ株式会社 Metal recovery method
JP5899085B2 (en) 2011-09-22 2016-04-06 アークレイ株式会社 Heavy metal recovery method and heavy metal recovery reagent used therefor

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS63118025A (en) * 1986-11-06 1988-05-23 Nippon Mining Co Ltd Method for removing or recovering silver
JPH0331772B2 (en) * 1986-11-06 1991-05-08 Nippon Mining Co
FR2764908A1 (en) * 1997-06-19 1998-12-24 Gerard Gasser PROCESS FOR SEPARATING METAL IONS ABSORBED ON A RESIN AND PROCESS AND PLANT FOR THE TREATMENT AND RECYCLING OF PHOTOGRAPHIC EFFLUENTS
WO1998059081A1 (en) * 1997-06-19 1998-12-30 Gasser Gerard Separating metal ions absorbed on a resin and installation for recycling photographic effluents including an exchanger and an electrolysis vessel
US6387243B1 (en) 1997-06-19 2002-05-14 Gerard Gasser Separation of metal ions absorbed on a resin and installation for recycling photographic effluents including an exchanger and an electrolytic vessel
EP2508864A3 (en) * 2011-04-04 2016-06-01 ARKRAY, Inc. Method for recovering metal and kit for recovery of metal for use in the same

Also Published As

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