JPH0248089A - Waste liquid processing device and automatic photograph developing machine using this device - Google Patents

Waste liquid processing device and automatic photograph developing machine using this device

Info

Publication number
JPH0248089A
JPH0248089A JP19445788A JP19445788A JPH0248089A JP H0248089 A JPH0248089 A JP H0248089A JP 19445788 A JP19445788 A JP 19445788A JP 19445788 A JP19445788 A JP 19445788A JP H0248089 A JPH0248089 A JP H0248089A
Authority
JP
Japan
Prior art keywords
waste liquid
liquid
tank
processing
ice
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
JP19445788A
Other languages
Japanese (ja)
Inventor
Takao Ogawa
尊夫 小川
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.)
Ogawa Kankyo Kenkyusho KK
Original Assignee
Ogawa Kankyo Kenkyusho KK
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 Ogawa Kankyo Kenkyusho KK filed Critical Ogawa Kankyo Kenkyusho KK
Priority to JP19445788A priority Critical patent/JPH0248089A/en
Publication of JPH0248089A publication Critical patent/JPH0248089A/en
Pending legal-status Critical Current

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  • Photographic Processing Devices Using Wet Methods (AREA)
  • Photographic Developing Apparatuses (AREA)
  • Physical Water Treatments (AREA)

Abstract

PURPOSE:To allow the reutilization of processing water and to facilitate processing of a residual waste liquid by obtaining the processing water for dissolution of ice contg. less contaminants and the thick waste liquid of the contaminants in the state in which the ice deposited by cooling the waste liquid generated by a development processing machine to the freezing point or below and the waste liquid coexist. CONSTITUTION:The cooled waste liquid freezes by a small amt. each on the surface of a drum, parts from the liquid surface and is scraped by a scraper 13. The scraped liquid enters a processing water tank 14. A heater 15 in the lower part of the scraper 13 and the tank 14 thaws partly or fully the ice. The waste liquid of a waste liquid receiving tank 12 is then removed into a thick liquid tank 17 at the point of the time when the waste liquid in an original liquid tank 8 runs out for the purpose of a batch processing. The liquid is transferred into a processing water stock tank 28 if the water quality of the liquid stored in the tank 14 is adequate for releasing or recycling. The liquid is transferred to the tank 8 and the similar operation is repeated when said quality is insufficient. The liquid in the tank 27 is transferred to a thick liquid stock tank 19 when the quality of the water stored in this tank attains the sufficient concn. The liquid is transferred into the tank 8 and the similar operation is repeated at the point of the time when the tank 17 is filled with the liquid if said quality is insufficient.

Description

【発明の詳細な説明】 本発明は銀塩写真処理廃液を良好に処理する装置に関す
る。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to an apparatus for effectively treating silver salt photographic processing waste liquid.

/ 近年銀塩写真の現像処理時間は短くなり30分以内の処
理が可能となっている。またユーザーの撮影済みフィル
ムをDPE取り次ぎ店に出してからプリントを手にする
までの所用時間の大半はDPE取り次ぎ店とラボと称す
る現像処理を行う所の往復時間となる。このためこれを
スピードアップする必要から小型で、自動制御による取
扱の容易な自動現像機が開発され集配時間が短縮できる
よう各所に事務所の片隅に設置する感覚で自動現像機(
以下ミニラボと称する)が設置できるようになった。と
ころが一般にこのような場所には廃水処理設備はないた
め、ミニラボからは廃水が発生しないよう設計されてお
り、疲労した現像液や定着液、水洗液は廃液タンクに貯
めて処理業者が定期的に収集するシステムを採用してい
る。ところが交通混雑の部会では収集に時間がかかり意
外と大変であり、また逆に過疎地区では収集効率が悪く
、ややもすると不法に廃棄されたりして河ノ海水の汚染
汚濁の原因になりかねない。このためミニラボ側では廃
液の発生量の少ない機械の開発が1つのテーマであり、
現状では写真の品質に影響することもあっである程度の
量以下にはなかなか少なくできないのが現状である。一
般的なミニラボ(時間33 mmロールフィルム30本
処理)で廃液の発生量は7日当りおよそ現像廃液が3リ
ツトル、漂白定着廃液が2リツトル、水洗液が10リツ
トル、合計/Jリットル程度である。
/ In recent years, the processing time for silver halide photography has become shorter and can now be processed within 30 minutes. Furthermore, most of the time required from the time a user sends the photographed film to the DPE agency until the user receives the print is the round trip time between the DPE agency and the development processing facility called a laboratory. For this reason, it was necessary to speed up this process, so a small automatic developing machine that was automatically controlled and easy to handle was developed.
(hereinafter referred to as a mini lab) can now be installed. However, since there is generally no wastewater treatment equipment in such locations, minilabs are designed so that no wastewater is generated, and exhausted developer, fixer, and washing solutions are stored in waste tanks and treated periodically by a processing company. We have adopted a system to collect information. However, collection takes time and is surprisingly difficult in congested areas, and conversely, collection efficiency is poor in depopulated areas, leading to illegal disposal and the potential for contamination of the Kawano Seawater. For this reason, one of the themes on the minilab side is the development of machines that generate less waste liquid.
Currently, it is difficult to reduce the amount below a certain level because it may affect the quality of the photo. In a typical minilab (processing 30 rolls of 33 mm roll film per hour), the amount of waste liquid generated is approximately 3 liters of developing waste liquid, 2 liters of bleach-fixing waste liquid, and 10 liters of washing liquid per 7 days, totaling about 1 J liter.

本発明はこれらミニラボから発生する廃液の量を少なく
し、廃液の収集を軽減しコストダウンにつなげる廃液処
理をおこなうことができる。
The present invention can reduce the amount of waste liquid generated from these minilabs, reduce the collection of waste liquid, and perform waste liquid treatment that leads to cost reduction.

第1表は代表的な写真処理薬品の成分を示すものである
。一般に写真の処理廃液は汚濁度が高く、BOD(生物
化学的酸素要求量)やC0D(化学的酸素要求量)は敵
方PPMもあり、これを活性汚泥法のような一般的な廃
水処理で浄化することは非常におおきな設備を必要とし
また生物分解できない成分も多く、ミニラボに併設する
ことは現実的でない。また活性炭を使用するにしても吸
着容量の制約から多量の活性炭を必要とし、交換の頻度
およびコストで同じく現実的でない。オゾンのような酸
化剤を使用することも検討されてきたが写真処理薬品に
はオゾンで分解できない成分が多く不十分である。分離
膜で処理する方法もあるが写真処理薬品は多量の無機塩
を含むと同時に有機物の分子量も数10から7000程
度まで分布しこれらを効率よく分離する膜は現状では見
あたらない。廃液を焼却する方法はCOD成分を分解す
ることはできるが薬品中のイオウ成分のため多量の亜硫
酸ガスや鉄分や塩類のダストが発生しこれの処理を要す
るなど少量の廃液を処理するにもかなり大変な設備とな
りミニラボに併設することは現実的でない。廃液を蒸発
または蒸留する方法は留出液に薬液成分が留出しCOD
除去率はせいぜいjO%程度と悪く且つ成分が熱により
分解し悪臭ガスが発生しかえってこれを除くために大変
な処理が必要となり実用化できていない。このように写
真処理廃液は種々の検討がなされてきているが、いまだ
に簡便な処理方式は見いだせず、この結果ミニラボにお
い又は処理業者が廃液を収集する方式を採用している。
Table 1 shows the ingredients of typical photographic processing chemicals. In general, the treated wastewater shown in the photo has a high degree of pollution, and BOD (biochemical oxygen demand) and C0D (chemical oxygen demand) have PPM on the other hand, and this can be solved by general wastewater treatment such as the activated sludge method. Purification requires extremely large equipment, and many components cannot be biodegraded, making it impractical to install them in a minilab. Furthermore, even if activated carbon is used, a large amount of activated carbon is required due to adsorption capacity limitations, and it is also impractical due to the frequency and cost of replacement. The use of oxidizing agents such as ozone has been considered, but this is insufficient because many photographic processing chemicals have components that cannot be decomposed by ozone. Although there is a method of processing using a separation membrane, photographic processing chemicals contain a large amount of inorganic salts, and at the same time, the molecular weight of organic substances ranges from several tens to about 7,000, and there is currently no membrane that can efficiently separate these substances. Although the method of incinerating waste liquid can decompose COD components, the sulfur components in the chemicals generate a large amount of sulfur dioxide gas, iron, and salt dust, which must be disposed of, making it difficult to treat small amounts of waste liquid. It would be a complicated piece of equipment, and it would be impractical to install it alongside a minilab. The method of evaporating or distilling the waste liquid is that the chemical components are distilled out in the distillate and the COD
The removal rate is poor, at most about jO%, and the components decompose due to heat, producing foul-smelling gases, which require extensive treatment to remove, and have not been put to practical use. As described above, various studies have been conducted on photographic processing waste liquid, but a simple treatment method has not yet been found, and as a result, methods have been adopted in which the waste liquid is collected in minilabs or by processing companies.

本発明者はこれらの事実をふまえ検討した結果、下記の
処理方式が簡便で実現可能な方法であることを見いだし
た。
As a result of consideration based on these facts, the present inventor found that the following processing method is a simple and feasible method.

即ち写真処理廃液をO′C以下に冷却することにより廃
液から氷を析出させ、廃液と析出させた水を共存させる
状態で、廃液から氷を取り出すと汚濁物の少ない氷と汚
濁物の濃縮された廃液に効率よく分離できることを見い
だした。一般に温度による溶解度の差により液体から固
体を析出させ精製物を得る手段は晶析操作としてよく使
われる手段であるがこれは少量の溶質成分の精製を目的
とするものであり、本発明の母液そのものの精製とは全
く異なる。母液そのものの精製の例として海水から淡水
の製造があるがこれは塩化ナトIJウムのような無機塩
の分離という単純な系であり本発明のような廃液の処理
とは異なる。即ち廃液は種々の無機塩や錯塩や有機物を
含む理論では全く推定できない複雑な糸であり、一般に
は生物処理や活性炭処理などの他の廃液処理法と比較し
有利とはいえず廃液処理装置として使用されることばは
! とんどない。ところが実験の結果写真処理廃液の処理と
しては非常によい分離効率があることを見いだし、且つ
前述のように他の廃液処理法にみられる除去不可成分や
分解物による1次汚染の不都合もなく実用に値する方法
であることを見いだした。この操作により得られた廃液
と氷を溶かした処理水についてそれぞれ同様の操作を複
数回くりかえすことで、十分汚濁物を濃縮した少量の廃
液と河川や下水道に放流可能なまでに精製された処理水
または写真現像機の水洗水として再利用できるまでに精
製された処理水を得ることができ、その結果処理業者に
渡す廃液の量を大幅に削減できるようになった。
That is, ice is precipitated from the waste liquid by cooling the photographic processing waste liquid to below O'C, and when ice is taken out from the waste liquid in a state where the waste liquid and the precipitated water coexist, ice with less contaminants and concentrated contaminants are obtained. It was discovered that the waste liquid can be efficiently separated. Generally, the method of obtaining a purified product by precipitating a solid from a liquid due to the difference in solubility due to temperature is a method often used as a crystallization operation, but this method is aimed at purifying a small amount of solute component, and the mother liquor of the present invention It is completely different from refining itself. An example of purifying the mother liquor itself is the production of fresh water from seawater, but this is a simple system of separating inorganic salts such as sodium chloride, and is different from the treatment of waste liquid as in the present invention. In other words, waste liquid is a complex thread containing various inorganic salts, complex salts, and organic substances that cannot be estimated at all by theory, and is generally not advantageous compared to other waste liquid treatment methods such as biological treatment and activated carbon treatment, so it is not recommended as a waste liquid treatment device. The words used! There's no way. However, as a result of experiments, we found that it has very good separation efficiency for processing waste liquid from photographic processing, and as mentioned above, it can be put to practical use without the problems of primary contamination caused by unremovable components and decomposed products that occur in other waste liquid treatment methods. I found it to be a worthy method. By repeating the same operation several times for the waste liquid obtained by this operation and the treated water obtained by melting the ice, a small amount of waste liquid with sufficiently concentrated pollutants and treated water purified to the extent that it can be discharged into rivers and sewers are obtained. Alternatively, it is possible to obtain treated water that has been purified to the point that it can be reused as washing water for photographic processing machines, and as a result, it has become possible to significantly reduce the amount of waste liquid sent to processing companies.

写真現像機で使用される薬品の代表例として第1表に一
般的なカラー写真の現像液と定着液の組成を示す。写真
現像機からは、現像廃液、定着廃液、水洗廃液等の廃液
が発生するが、その中でも水洗廃液が一番多く発生する
ので、カラー写真の該水洗廃液についてその分離効率を
測定したところ、第2表のような結果を得た。これとの
比較の− 乙 ために単蒸留における分離効率を第3表に示す。
As representative examples of chemicals used in photographic developing machines, Table 1 shows the compositions of common color photographic developers and fixers. Photographic developing machines generate waste liquids such as developing waste liquid, fixing waste liquid, washing waste liquid, etc. Among them, washing waste liquid is generated the most, so when we measured the separation efficiency of the washing waste liquid for color photography, we found that The results shown in Table 2 were obtained. For comparison with this, the separation efficiency in simple distillation is shown in Table 3.

これによると、廃液が共存する状態で氷を析出取り出す
場合は、その分離効率が単蒸留の場合と比較し約3倍と
なり有効な結果を得た。また第≠表は白黒写真廃液の場
合のデーターを示し、この場合も十分実用に値する結果
を得た。このことは印刷用の写真廃液やレントゲンの処
理廃液にも適用できることを示している。
According to this, when ice is precipitated and removed in the presence of waste liquid, the separation efficiency is approximately three times that of simple distillation, and an effective result was obtained. Further, Table ≠ shows data for the case of black and white photographic waste liquid, and in this case too, results worthy of practical use were obtained. This indicates that it can also be applied to photographic waste liquid for printing and waste liquid from X-ray processing.

以下図面に従って本発明を説明する。The present invention will be explained below with reference to the drawings.

第1図は本発明の実施例を示す図であり(1)はミニラ
ボである。ミニラボからは現像廃液(2)、漂白定着廃
液(3)、水洗廃液(4)が発生し、これらは各タンク
(5) (6) (7)に入れられる。多量に発生する
水洗廃液(4)は−旦原液タンク(8)に移す。原液タ
ンク(8)からポンプ(9)により廃液受は容器と冷却
ドラムと掻き落しスクレーパーとその他付属品からなる
機械(以下このユニットを冷凍分離機と称す)aCtに
おくられ冷却ドラムαυの下にある廃液受は容器(2)
に入る。該冷却ドラムは廃液受は容器の中の廃液に一部
没入しており矢印の方向にゆっくり回転している。該冷
却ドラムの表面は内部から冷媒等により0℃以下に冷却
されている。冷却方法は不凍液や冷媒ガスを使用して間
接的に冷却したり、ペルチェ効果による直接冷却などが
ある。冷却された廃液はすこしづづドラム表面に氷結し
成長しながら液面からはなれていき、掻き落しスクレー
バーα■により掻き落とされ処理水タンク(14)には
いる。
FIG. 1 is a diagram showing an embodiment of the present invention, and (1) is a minilab. A developing waste solution (2), a bleach-fixing waste solution (3), and a washing waste solution (4) are generated from the minilab, and these are placed in each tank (5), (6), and (7). A large amount of washing waste liquid (4) is transferred to the raw liquid tank (8). The waste liquid receiver is sent from the raw liquid tank (8) by the pump (9) to a machine (hereinafter referred to as a refrigeration separator) consisting of a container, a cooling drum, a scraper, and other accessories (this unit is referred to as a refrigeration separator), and is placed under the cooling drum αυ. A certain waste liquid receiver is a container (2)
to go into. The waste liquid receiver of the cooling drum is partially immersed in the waste liquid in the container and rotates slowly in the direction of the arrow. The surface of the cooling drum is internally cooled to below 0° C. by a refrigerant or the like. Cooling methods include indirect cooling using antifreeze or refrigerant gas, and direct cooling using the Peltier effect. The cooled waste liquid gradually freezes on the drum surface, grows and separates from the liquid surface, is scraped off by the scraper α■, and enters the treated water tank (14).

掻き落しスクレーパーα1の下部及び処理水タンクα→
の下部にはヒーターαυが設置してあり、氷を一部また
は全部を解氷する。この図の例はバッチ処理のため原液
タンクの廃液がなくなった時点で廃液受は容器(ロ)の
廃液をバルブ(ト)をあけ濃縮、液タンク←ηへ抜く。
Lower part of scraper α1 and treated water tank α→
A heater αυ is installed at the bottom of the ice cube to melt some or all of the ice. In the example shown in this figure, when the waste liquid in the stock solution tank is used up due to batch processing, the waste liquid receiver opens the valve (g) to concentrate the waste liquid in the container (b) and drains it to the liquid tank ←η.

処理水タンク←Φに貯った液の水質が放流可能または再
利用可能な場合はこれを処理水ストックタンクα樽へ移
液する。不十分な場合は処理水タンクの水を原液タンク
(8)に移し同様の操作を繰り返す。一方濃縮液タンク
に貯った液の水質が十分濃縮された濃度になった場合は
濃縮液ストックタンクσ9に移液する。不十分な場合は
濃縮液タンクに液がいっばいになった時点で原液タンク
(8)に移し、同様の操作を繰り返す。氷結して精製す
るときに一番分離効率をさげるのは氷に付着する廃液な
のでエアーナイフ翰により空気を吹き付けて付着廃液を
除去すると有効である。
If the quality of the liquid stored in the treated water tank ←Φ is such that it can be discharged or reused, it is transferred to the treated water stock tank α barrel. If it is insufficient, transfer the water from the treated water tank to the stock solution tank (8) and repeat the same operation. On the other hand, when the water quality of the liquid stored in the concentrate tank reaches a sufficiently concentrated concentration, the liquid is transferred to the concentrate stock tank σ9. If it is insufficient, once the concentrated liquid tank is full of liquid, transfer it to the stock liquid tank (8) and repeat the same operation. When freezing and purifying ice, what reduces the separation efficiency the most is the waste liquid that adheres to the ice, so it is effective to remove the adhering waste liquid by blowing air with an air knife.

第、2図は冷凍分離機を複数個シリーズに接続し、水洗
廃液を連続的に処理し、得られた処理水を水洗水として
再利用する例を示す図である。(1)から(7)までは
第1図と同じであるが、水洗廃液(4)はポンプ(ハ)
で3段目冷凍分離機(ハ)の廃液受は容器に供給される
。図の翰から勾までは1段目から5段目の冷凍分離機を
示す。一つ一つの冷凍分離機は第1図で説明した構造か
らなり(ホ)から(ハ)までの冷凍分離機は第1図の処
理水タンクのかわりに次段の冷凍分離機が接続され、第
1図の濃縮液タンクαηのかわりに前段の冷凍分離機が
接続されている。
FIG. 2 is a diagram showing an example in which a plurality of refrigeration separators are connected in series to continuously treat washing waste liquid, and the obtained treated water is reused as washing water. (1) to (7) are the same as in Figure 1, but washing waste liquid (4) is pumped (c).
The waste liquid receiver of the third stage refrigerating separator (c) is supplied to the container. The diagram from top to bottom shows the first to fifth stages of refrigerating separators. Each refrigerating separator has the structure explained in Fig. 1, and the refrigerating separators (e) to (c) are connected to the next stage refrigerating separator instead of the treated water tank shown in Fig. 1. In place of the concentrate tank αη in FIG. 1, a freezing separator in the previous stage is connected.

ただし前段の冷凍分離機とは液の混合や逆流を防ぐため
若干のレベル差をつけたU字連結管(ハ)により接続さ
れている。水洗廃液は3段目冷凍分離機(ハ)の冷却ド
ラム表面に氷結しドラムの回転により液から取り出され
スクレーバーにより掻き落とさ一 れ一部または全部溶解され7段目冷凍分離機(ハ)の廃
液受は容器に入る。ここで再び廃液受は容器中の廃液と
新たな固液平衡状態における氷を≠段目の冷却ドラム表
面に析出され同様の操作でオ段目冷凍分離機(ハ)には
いる。j段目冷凍分離機(ハ)から同様の操作で排出さ
れる氷または水は3段目が最終段のため処理水タンク兼
分配タンク(ロ)に入る。
However, it is connected to the previous stage refrigeration separator by a U-shaped connecting pipe (c) with a slight level difference to prevent liquid mixing and backflow. The washing waste liquid freezes on the surface of the cooling drum of the third-stage freezing separator (c), is removed from the liquid by the rotation of the drum, is scraped off by a scraper, and is partially or completely dissolved, and then the waste liquid is sent to the seventh-stage freezing separator (c). The uke goes into the container. Here, the waste liquid receiver again deposits the waste liquid in the container and ice in a new solid-liquid equilibrium state on the surface of the ≠th stage cooling drum, and enters the 0th stage freezing separator (c) in the same manner. Ice or water discharged from the j-stage frozen separator (c) in a similar operation enters the treated water tank/distribution tank (b) since the third stage is the final stage.

(ロ)のタンクでは溶解用ヒーター□□□により氷は完
全にとかされ一部はポンプ(3I)により水洗水として
温度調節用ヒーター(33)により温度調節されて写真
現像機へ供給される。また一部は連結管(ホ)により!
段目冷凍分離機(ハ)へ戻される。この戻す液量と水洗
水として系外へとりだす液量の比は蒸留操作における還
流比にあたるもので連続操作において各段の廃液受は容
器中の廃液濃度を一定に保ち、精製度や濃縮度をきめる
要素となるものである。
In the tank (b), the ice is completely melted by the melting heater □□□, and a portion is supplied to the photographic developing machine as washing water by the pump (3I), the temperature of which is controlled by the temperature control heater (33). Also, some of it is due to the connecting pipe (E)!
It is returned to the stage refrigeration separator (c). The ratio of the amount of liquid returned to the outside of the system as washing water corresponds to the reflux ratio in distillation operation.In continuous operation, the waste liquid receiver at each stage keeps the concentration of waste liquid in the container constant, and the degree of purification and concentration is controlled. This is a deciding factor.

方濃縮される液は2段目冷凍分離機(イ)、1段目冷凍
分離機(イ)へと濃縮され最後は濃縮液タンク(ハ)へ
入る。
The concentrated liquid is concentrated in the second stage frozen separator (A), first stage frozen separator (A), and finally enters the concentrated liquid tank (C).

以下実施例を示す。Examples are shown below.

実施例−1 第2図のごとき冷凍分離機を用いて水洗廃液を連続処理
したデータを第5表に示す。
Example 1 Table 5 shows the data obtained by continuously processing washing waste liquid using a refrigeration separator as shown in Fig. 2.

なおここで使用した冷却ドラムの仕様は直径10cm、
長さ/!;cm  表面積0.0’l−7m2冷媒温度
  −g′C 回転速度  /回/3分 還流比   / 装置の段数は5段で水洗廃液は濃縮側から3段目に供給
の操作で 処理量   0.3j  リットル/時間濃縮液   
0.03gリットル/時間濃度C0Dcr  /10.
000ppm処理水    0.31、2  リットル
/時間濃度00Dcr    /jOppm が得られた。
The specifications of the cooling drum used here are 10 cm in diameter.
length/! ; cm Surface area 0.0'l-7m2 Refrigerant temperature -g'C Rotation speed / times / 3 minutes Reflux ratio / The number of stages of the device is 5, and the water washing waste liquid is supplied to the third stage from the concentration side, so the throughput is 0 .3j liter/hour concentrate
0.03g liter/hour concentration C0Dcr/10.
000ppm treated water 0.31.2 liters/hour concentration 00Dcr/jOppm was obtained.

本発明はこのように廃液を処理することができ、その処
理水を河川や下水道に放流したり写真現像機の水洗水と
して再利用することができるので残留分の廃液が少なく
なりその収集や系外での廃液処理が楽にできる。ただし
規制値によっては汚濁負荷が本発明による処理で十分低
くなってから最終処理として活性炭使用することが有効
な場合もあるが本発明の主旨を逸脱するものではない。
The present invention can treat waste liquid in this way, and the treated water can be discharged into rivers or sewers or reused as washing water for photographic processing machines, so the residual waste liquid is reduced, making it easier to collect and systemize. Easily dispose of waste liquid outside. However, depending on regulatory values, it may be effective to use activated carbon as a final treatment after the pollution load has been sufficiently reduced by the treatment according to the present invention, but this does not depart from the spirit of the present invention.

まだ該処理水は低湿で処理をおこなっているため熱によ
る内容成分の分解による質の変化や藻や微生物の発生に
よる汚染がないため写真現像機の良質の水洗水として使
用でき水洗水のクローズ化が容易となる。さらにこの場
合は排水規制値のごとく低濃度まで処理する必要がない
ため、より簡便となる利点がある。また他の処理法にみ
られる成分の分解による悪臭や生物処理にともなう汚泥
具がなく処理できることも写真自動現像機が他の作業や
人の常時いる専用でない空間に置かれるケースが多いこ
とを考えると見逃せない大きな利点である0 第1表 現像液処方 lリットルあたり 漂白定着液  lリットルあたり 第2表 水洗廃液の分離効率:水洗廃液のC0Dcr =1、2
000ppm−/3− lグ= ≠
Since the treated water is still processed at low humidity, there is no change in quality due to decomposition of the contents due to heat, and there is no contamination due to the growth of algae or microorganisms, so it can be used as high-quality rinsing water for photo processing machines, and the rinsing water can be closed. becomes easier. Furthermore, in this case, it is not necessary to treat the wastewater to a low concentration as required by wastewater regulation values, so there is an advantage that it is simpler. Additionally, the process can be done without the foul odors caused by the decomposition of components or the sludge equipment associated with biological processing, which is seen in other processing methods.Considering that automatic photo processing machines are often placed in spaces not exclusively used for other tasks or where people are constantly present. This is a big advantage that cannot be overlooked. 1st expression solution formulation Bleach-fix solution per liter 2nd surface per liter Washing waste liquid separation efficiency: C0Dcr of washing waste liquid = 1, 2
000ppm-/3-lg=≠

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

図面は本発明の実施例を示し、第1図はバッチ処理にお
ける概略図、第2図は連続処理における概略図である。 (1)は写真自動現像機、(2)は現像廃液、(3)は
定着廃液、(4)は水洗廃液、(5)は現像廃液タンク
、(6)は定着廃液タンク、(7)は水洗廃液タンク、
(8)は原液タンク、(9)はポンプ、aQは冷凍分離
機、aηは冷却ドラム、(ロ)は廃液受は容器、aつは
掻き落しスクレハー、(ロ)は処理水タンク、aのはヒ
ーター、(2)はパルプ、Qηは濃縮液タンク、α8)
は処理水ストックタンク、0すは濃縮液ストックタンク
、(イ)はエアーナイフ、(ハ)はポンプ、(イ)は/
段目冷凍分離機、■はコ段目冷凍分離機、(ハ)は3段
目冷凍分離機、(ハ)は≠段目冷凍分離機、0ejはj
段目冷凍分離機、(財)は処理水タンク兼分配タンク、
(ハ)は濃縮液タンク、翰はU字連結管、翰は溶解用ヒ
ーター、 (31)はポンプ、0つはパイプ、c33)
は温度調節用ヒーターである。
The drawings show embodiments of the present invention; FIG. 1 is a schematic diagram of batch processing, and FIG. 2 is a schematic diagram of continuous processing. (1) is an automatic photo processor, (2) is a developer waste, (3) is a fixer waste, (4) is a washing waste, (5) is a developer waste tank, (6) is a fixer waste tank, and (7) is a waste fixer. Washing waste tank,
(8) is the raw solution tank, (9) is the pump, aQ is the frozen separator, aη is the cooling drum, (b) is the waste liquid receiver is the container, a is the scraping scraper, (b) is the treated water tank, is the heater, (2) is the pulp, Qη is the concentrate tank, α8)
0 is treated water stock tank, 0 is concentrated liquid stock tank, (a) is air knife, (c) is pump, (a) is /
Stage frozen separator, ■ is the first stage frozen separator, (c) is the third stage frozen separator, (c) is ≠ stage frozen separator, 0ej is j
Stage refrigeration separator, (Foundation) is treated water tank and distribution tank,
(c) is the concentrate tank, the handle is the U-shaped connecting pipe, the handle is the melting heater, (31) is the pump, 0 is the pipe, c33)
is a temperature control heater.

Claims (1)

【特許請求の範囲】 1、写真自動現像処理機において、発生する廃液を冷媒
等により0℃以下に冷却する手段と、冷却により析出す
る氷と廃液が共存する状態においてその氷を該廃液から
取り出す手段を備え、写真処理廃液の固液共存状態にお
ける廃液中の汚濁物濃度とそこから析出される氷中の汚
濁物濃度の差を利用して、汚濁物の少ない氷をとかした
処理水と汚濁物の濃縮された廃液を得ることを特徴とす
る廃液処理装置。 2、請求項1記載の廃液処理装置から発生する処理水を
用いて写真自動現像処理機における水洗水として再循環
させる機構を備えたことを特徴とする写真自動現像処理
機。
[Claims] 1. In an automatic photographic processing machine, a means for cooling the generated waste liquid to below 0°C using a refrigerant, and removing the ice from the waste liquid in a state where the waste liquid coexists with ice that precipitates due to cooling. By using the difference between the contaminant concentration in the photographic processing waste liquid in a solid-liquid coexistence state and the contaminant concentration in the ice precipitated from the waste liquid, it is possible to compare the treated water with melted ice containing less contaminants and the contaminant. A waste liquid treatment device characterized in that it obtains a concentrated waste liquid. 2. An automatic photographic processing machine comprising a mechanism for recirculating the treated water generated from the waste liquid processing apparatus according to claim 1 as washing water in the automatic photographic processing machine.
JP19445788A 1988-08-05 1988-08-05 Waste liquid processing device and automatic photograph developing machine using this device Pending JPH0248089A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP19445788A JPH0248089A (en) 1988-08-05 1988-08-05 Waste liquid processing device and automatic photograph developing machine using this device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP19445788A JPH0248089A (en) 1988-08-05 1988-08-05 Waste liquid processing device and automatic photograph developing machine using this device

Publications (1)

Publication Number Publication Date
JPH0248089A true JPH0248089A (en) 1990-02-16

Family

ID=16324885

Family Applications (1)

Application Number Title Priority Date Filing Date
JP19445788A Pending JPH0248089A (en) 1988-08-05 1988-08-05 Waste liquid processing device and automatic photograph developing machine using this device

Country Status (1)

Country Link
JP (1) JPH0248089A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
RU2616081C1 (en) * 2016-06-07 2017-04-12 Федеральное государственное бюджетное образовательное учреждение высшего образования "Тихоокеанский государственный университет" Water purifier for producing melted drinking water
RU2625110C1 (en) * 2016-06-15 2017-07-11 Федеральное государственное бюджетное образовательное учреждение высшего образования "Тихоокеанский государственный университет" Method of main water cleaning
RU2645544C1 (en) * 2016-12-08 2018-02-21 Федеральное государственное бюджетное образовательное учреждение высшего образования "Тихоокеанский государственный университет" Device for producing thawed drinking water

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5944883A (en) * 1982-09-08 1984-03-13 Hitachi Ltd Three-axis rectangular type laser oscillation device

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5944883A (en) * 1982-09-08 1984-03-13 Hitachi Ltd Three-axis rectangular type laser oscillation device

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
RU2616081C1 (en) * 2016-06-07 2017-04-12 Федеральное государственное бюджетное образовательное учреждение высшего образования "Тихоокеанский государственный университет" Water purifier for producing melted drinking water
RU2625110C1 (en) * 2016-06-15 2017-07-11 Федеральное государственное бюджетное образовательное учреждение высшего образования "Тихоокеанский государственный университет" Method of main water cleaning
RU2645544C1 (en) * 2016-12-08 2018-02-21 Федеральное государственное бюджетное образовательное учреждение высшего образования "Тихоокеанский государственный университет" Device for producing thawed drinking water

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