JPH0422483A - Apparatus for evaporative concentration treatment of waste photographic processing solution - Google Patents

Apparatus for evaporative concentration treatment of waste photographic processing solution

Info

Publication number
JPH0422483A
JPH0422483A JP12723790A JP12723790A JPH0422483A JP H0422483 A JPH0422483 A JP H0422483A JP 12723790 A JP12723790 A JP 12723790A JP 12723790 A JP12723790 A JP 12723790A JP H0422483 A JPH0422483 A JP H0422483A
Authority
JP
Japan
Prior art keywords
waste liquid
photographic processing
filter
heating
processing 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
JP12723790A
Other languages
Japanese (ja)
Other versions
JP3111256B2 (en
Inventor
Masayuki Kurematsu
雅行 榑松
Nobutaka Goshima
伸隆 五嶋
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.)
Konica Minolta Inc
Original Assignee
Konica Minolta Inc
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 Konica Minolta Inc filed Critical Konica Minolta Inc
Priority to JP02127237A priority Critical patent/JP3111256B2/en
Publication of JPH0422483A publication Critical patent/JPH0422483A/en
Application granted granted Critical
Publication of JP3111256B2 publication Critical patent/JP3111256B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Landscapes

  • Photographic Processing Devices Using Wet Methods (AREA)
  • Heat Treatment Of Water, Waste Water Or Sewage (AREA)
  • Vaporization, Distillation, Condensation, Sublimation, And Cold Traps (AREA)

Abstract

PURPOSE:To achieve the miniaturization and cost reduction of the title apparatus with good heat efficiency by providing a filter having a large number of through-holes with a diameter of 0.5mum-2mm to a route supplying a waste photographic processing solution. CONSTITUTION:When a valve 20 is opened, a waste solution is sucked up from a container 19 under reduced pressure to be sprinkled from the nozzle 21 provided to the upper part in a culumn 9 through a filter unit 26. The waste solution enters a hollow container from the inlet 31 thereof, but a cylindrical porous filter 29 is mounted on a bottom part and a lid 28 at both ends thereof in close contact therewith, and the waste solution is passed through the through-holes having a diameter of 0.5mum-2mm of the filter 29 to be discharged from the upper part of an inner cylinder 27 through an outlet 30. The solid in the solution remains between the filter 29 and the outer cylinder of the filter unit 26 and, therefore, the contaminated filter 29 is removed at the time of replacement by opening the lid 28.

Description

【発明の詳細な説明】 〔産業上の利用分野〕 この発明は、写真用自動現像機による写真感光材料の現
像処理に伴い発生する廃液(以下、写真処理廃液ないし
廃液と略称)を蒸発処理する処理装置に係り、特に、自
動現像機内若しくは自動現像機の近傍に配置して処理す
るのに適した写真処理廃液の処理装置に関する。
[Detailed Description of the Invention] [Industrial Application Field] The present invention is a method for evaporating waste liquid (hereinafter referred to as photographic processing waste liquid or waste liquid) generated during the processing of photographic light-sensitive materials using an automatic photographic processor. The present invention relates to a processing device, and particularly to a processing device for photographic processing waste liquid suitable for processing by being disposed in or near an automatic processor.

〔従来の技術〕[Conventional technology]

一般に、ハロゲン化銀感光材料の写真処理は、発色現像
、漂白定着(又は漂白、定着)、水洗又は安定化処理の
順に行なわれている。
Generally, photographic processing of silver halide light-sensitive materials is carried out in the order of color development, bleach-fixing (or bleaching and fixing), and water washing or stabilization processing.

そして、多量の感光材料を処理する写真処理においては
、処理によって消費された成分を補充し一方、処理によ
って処理液中に溶出或は蒸発によって濃化する成分(例
えば現像液における臭化物イオン、定着液における銀錯
塩のような)を除去して処理成分を一定に保つことによ
って処理液の性能を一定に維持する手段が採られており
、補充のために補充液が処理液に補充され、写真処理に
おける濃厚化成分の除去のために処理液の一部が廃棄さ
れている。
In photographic processing in which a large amount of light-sensitive material is processed, components consumed during processing are replenished, while components that are eluted into the processing solution or concentrated by evaporation during processing (for example, bromide ions in the developer, bromide ions in the fixer), etc. A method is used to maintain the performance of the processing solution at a constant level by removing substances such as silver complex salts (such as silver complex salts) and keeping the processing components constant. A portion of the processing solution is discarded to remove concentrated components.

近年、補充液は水洗の補充液である水洗水を含めて公害
上や経済的理由から補充の量を大幅に減少させたシステ
ムに変わりつつあるが、写真処理廃液は自動現像機の処
理槽から廃液管によって導かれ、水洗水の廃液や自動現
像機の冷却水等で希釈されて下水道等に廃棄されている
In recent years, systems have been changing to systems in which the amount of replenishment fluid, including washing water, which is used as a replenishment fluid for washing, has been significantly reduced due to pollution and economic reasons, but photographic processing waste fluid is removed from the processing tank of automatic processors. It is led through a waste liquid pipe, diluted with waste liquid from washing water, cooling water from automatic processing machines, etc., and then disposed of in a sewer or the like.

しかしながら、近年の公害規制の強化により、水洗水や
冷却水の下水道や河川への廃棄は可能であるが、これら
以外の写真処理液[例えば、現像液、定着液、発色現像
液、漂白定着液(又は漂白液、定着液)、安定液等]の
廃棄は、実質的に不可能となっている。このため、各写
真処理業者は廃液を専門の廃液処理業者に回収料金を払
って回収してもらったり公害処理設備を設置したりして
いる。しかしながら、廃液処理業者に委託する方法は、
廃液を貯留しておくのにかなりの;(ベースが必要とな
るし、またコスト的にも極めて高価であり、さらに公害
処理設備は初期投資(イニシャルコスト)が極めて大き
く、整備するのにかなり広大な場所を必要とする等の欠
点を有している。
However, due to stricter pollution regulations in recent years, it is possible to dispose of washing water and cooling water into sewers or rivers, but other photographic processing solutions [e.g. developer, fixer, color developer, bleach-fixer] (or bleaching solution, fixing solution), stabilizing solution, etc.] has become virtually impossible to dispose of. For this reason, each photo processing company pays a collection fee to a specialized waste liquid processing company to collect the waste liquid, or installs pollution treatment equipment. However, the method of outsourcing to a waste liquid treatment company is
It takes a considerable amount of space to store the waste liquid (a base is required, and it is also extremely expensive), and the initial investment (initial cost) for pollution treatment equipment is extremely large, and it takes quite a large area to set up. It has disadvantages such as requiring a large space.

従って、一般には廃液回収業者によって回収され、二次
及び三次処理され無害化されているが、回収費の高騰に
より廃液引き取り価格は年々高くなるばかりでなく、ミ
ニラボ等では回収効率は悪いため、なかなか回収に来て
もらうことができず、廃液が店に充満する等の問題を生
じている。
Therefore, waste liquid is generally collected by waste liquid collection companies and rendered harmless through secondary and tertiary processing, but not only is the price of waste liquid collection rising year by year due to rising collection costs, but collection efficiency is low in minilabs, etc., so it is difficult to do so. No one can come to collect the liquid, causing problems such as waste liquid filling the store.

これらの問題を解決するために写真処理廃液の処理をミ
ニラボ等でも容易に行えることを目的として、写真処理
廃液を加熱して水分を蒸発乾固ないし固化することが研
究されており、例えば、実開昭60−70841号等に
示されている。ところで、発明者等の研究では写真処理
廃液を蒸発処理した場合、亜硫酸ガス、硫化水素、アン
モニアガス等の有害ないし極めて悪臭性のガスが発生す
る。これは写真処理液の定着液や漂白定着液としてよく
用いられるチオ硫酸アンモニウムや亜硫酸塩(アンモニ
ウム塩、ナトリウム塩又はカリウム塩)が高温のため分
解することによって発生することがわかった。更に蒸発
処理時には写真処理廃液中の水分等が蒸気となって気体
化することにより体積が膨張し、蒸発釜中の圧力が増大
する。このためこの圧力によって蒸発処理装置から前記
有害ないし悪臭性のガスが装置外部へもれ出してしまい
、作業環境上極めて好ましくないことが起る。
In order to solve these problems, research has been conducted to heat the photographic processing waste liquid to evaporate the water to dryness or solidify it, with the aim of making it easier to process the photographic processing waste liquid even in minilabs. It is shown in JP-A No. 60-70841 and the like. By the way, the inventors' research has shown that when photographic processing waste liquid is evaporated, harmful or extremely malodorous gases such as sulfur dioxide gas, hydrogen sulfide, and ammonia gas are generated. It has been found that this is caused by the decomposition of ammonium thiosulfate and sulfites (ammonium salt, sodium salt, or potassium salt), which are commonly used as fixing solutions and bleach-fixing solutions in photographic processing solutions, due to high temperatures. Further, during the evaporation process, moisture and the like in the photographic processing waste liquid becomes vapor and gasifies, thereby expanding the volume and increasing the pressure in the evaporation pot. Therefore, due to this pressure, the harmful or malodorous gas leaks out of the evaporation treatment apparatus to the outside of the apparatus, resulting in an extremely unfavorable working environment.

そこで、これらを解決するために実開昭60−7084
1号には蒸発処理装置の排気管部に活性炭等の排ガス処
理部を設ける方法が開示されている。しかし、この方法
は写真処理廃液中の多量の水分による水蒸気により、排
ガス処理部で結露又は凝結し、ガス吸収処理剤を水分が
覆い、ガス吸収能力を瞬時に失わせてしまう重大な欠点
を有しており、未だ実用には供し得ないものであった。
Therefore, in order to solve these problems,
No. 1 discloses a method of providing an exhaust gas treatment section such as activated carbon in the exhaust pipe section of an evaporation treatment device. However, this method has the serious drawback that water vapor from a large amount of water in the photographic processing waste liquid condenses or condenses in the exhaust gas treatment section, covering the gas absorption processing agent and causing it to instantly lose its gas absorption ability. However, it has not yet been put to practical use.

〔発明が解決しようとする課題〕[Problem to be solved by the invention]

これらの問題点を解決するために、この発明者等は写真
処理廃液を蒸発処理するに際し、蒸発によって生じる蒸
気を凝縮させ、さらに凝縮によって生じる凝縮液を処理
するとともに非凝縮成分についても処理して外部へ放出
する写真処理廃液の濃縮処理装置について先に提案した
In order to solve these problems, the present inventors condensed the vapor produced by evaporation when processing waste photographic processing liquid by evaporation, and further treated the condensate produced by condensation and also treated non-condensed components. We have previously proposed a device for concentrating photographic processing waste liquid that is discharged to the outside.

しかしながら、この提案によれば、次のような問題点が
あることを見いだした。すなわち、蒸発濃縮を行なうに
あたり、蒸発濃縮カラムに注入された写真処理廃液中に
固形物(ゴミなど)があると、加熱時に突沸を起こし、
これによって飛散したスランジ等が蒸気の経路に入り蒸
留液中に混入するから時にはこの蒸留液が廃液と変わら
ない公害負荷をもつものになってしまう。
However, according to this proposal, the following problems were found. In other words, when performing evaporative concentration, if there is solid matter (such as dust) in the photographic processing waste liquid injected into the evaporative concentration column, it will cause bumping during heating.
As a result, scattered sludge and the like enter the steam path and are mixed into the distilled liquid, which sometimes ends up having the same pollution load as waste liquid.

この突沸を防止するためには、供給する写真廃液に混入
している固形物を取り除くことが必要である。
In order to prevent this bumping, it is necessary to remove solids mixed in the supplied photographic waste liquid.

特に土泥突沸は、蒸発濃縮を減圧下で行なうときに発生
し易く、上記対策は不可欠となる。
In particular, mud bumping is likely to occur when evaporative concentration is performed under reduced pressure, and the above measures are essential.

なお、減圧下で蒸発濃縮を行なう理由は、減圧下では水
の沸点が下がることを利用し、水分の蒸発を低温で行な
うためであり、この低温とは100°C以下、好ましく
は10°Cから80°Cの範囲であって、この温度では
、写真処理廃液の分解が起らず従って有責ガス等の発生
を抑制する効果のある範囲である。
The reason for performing evaporative concentration under reduced pressure is to take advantage of the fact that the boiling point of water decreases under reduced pressure, and to evaporate water at a low temperature, and this low temperature is 100°C or less, preferably 10°C. to 80° C. At this temperature, decomposition of the photographic processing waste liquid does not occur, and therefore, it is effective in suppressing the generation of responsible gases and the like.

この発明は、供給写真処理廃液の供給経路で固形物を除
去する手段をもった写真処理廃液の蒸発濃縮処理装置を
提供することを目的とするものである。
SUMMARY OF THE INVENTION An object of the present invention is to provide an apparatus for evaporating and concentrating photographic processing waste liquid, which has a means for removing solid matter from the supply path of the photographic processing waste liquid.

〔課題を解決するための手段〕[Means to solve the problem]

その目的は、次の(1)、(2)、(3)、(4)の手
段のいずれか1項によって達成される。
The purpose is achieved by any one of the following means (1), (2), (3), and (4).

(1)写真処理廃液を受け入れ、加熱手段をもって加熱
蒸発を行なう加熱部と、上記発生した蒸気を冷却手段を
もって冷却凝縮する凝縮部と、上記加熱部に写真処理廃
液を供給する手段とを有する写真処理廃液の蒸発濃縮処
理装置に於て、写真処理廃液を供給する経路に、穴径が
2mm以下、0,5ミクロン以上の多数の貫通穴を有す
るフ・1ルターを設けたことを特徴とする写真処理廃液
の蒸発濃縮処理装置。
(1) A photograph having a heating section that receives photographic processing waste liquid and performs heat evaporation using a heating means, a condensing section that cools and condenses the generated vapor using a cooling means, and a means for supplying the photographic processing waste liquid to the heating section. In the evaporation concentration processing device for processing waste liquid, a filter having a large number of through holes with hole diameters of 2 mm or less and 0.5 microns or more is provided in the path for supplying the photographic processing waste liquid. Evaporative concentration treatment equipment for photographic processing waste liquid.

(2)上記加熱手段がヒートポンプの加熱部である上記
(1)項記載の写真処理廃液の蒸発濃縮処理装置。
(2) The apparatus for evaporating and concentrating photographic processing waste liquid according to item (1) above, wherein the heating means is a heating section of a heat pump.

(3)上記加熱手段による加熱蒸発濃縮を減圧下で行な
い、2 kcaff/cm2・h「以下で蒸気が加熱部
から出ていく経路に障害物を設けたことを特徴とする上
記(1)項記載の写真処理廃液の蒸発濃縮処理装置。
(3) The above-mentioned item (1), characterized in that the heating evaporation concentration by the heating means is performed under reduced pressure, and an obstacle is provided in the path where the steam exits from the heating section. The evaporative concentration processing apparatus for photographic processing waste liquid described above.

(4)上記加熱手段がヒートポンプの加熱部である上記
(3)項記載の写真処理廃液の蒸発濃縮処理装置。
(4) The apparatus for evaporating and concentrating photographic processing waste liquid according to item (3) above, wherein the heating means is a heating section of a heat pump.

この発明に於て、ヒートポンプの加熱部とは、冷媒ガス
をコンプレッサーを含む管体で連結した閉ループに封じ
こめ、上記コンプレッサーで圧縮して昇温した上記冷媒
ガスを上記管体の一方に放出し、この管壁を境として被
加熱体を接触させ、被加熱体を加熱することによって、
上記昇温した冷媒ガスの熱を放出する構成のものを示す
In this invention, the heating section of the heat pump confines refrigerant gas in a closed loop connected by pipes including a compressor, and releases the refrigerant gas, which has been compressed and heated by the compressor, into one of the pipes. By bringing the object to be heated into contact with this tube wall as a boundary and heating the object,
A configuration is shown in which the heat of the heated refrigerant gas is released.

ヒートポンプの冷却部とは、上記ヒートポンプの冷媒が
、上記閉ループに於て、コンプレッサーの吸引側では温
度低下するから、この温度低下した冷媒ガスに、上記管
体の管壁を境として被冷却体(この場合は水蒸気)を接
触させ、被冷却体を冷却する構成のものを示す。
The cooling section of a heat pump is the refrigerant of the heat pump whose temperature decreases on the suction side of the compressor in the closed loop, and the cooled object ( In this case, it shows a configuration in which the object to be cooled is cooled by contacting it with water vapor.

上記ヒートポンプの加熱部及び、ヒートポンプの冷却部
はいずれも、その熱伝達表面積を大きくし、伝熱効率を
向上するために、パイプで螺旋状に形成するものである
Both the heating section of the heat pump and the cooling section of the heat pump are spirally formed with pipes in order to increase the heat transfer surface area and improve heat transfer efficiency.

次に全体を減圧する減圧手段を使用する理由は、減圧下
で加熱することで廃液中の水分の蒸発温度を低下させる
ためであり、この蒸発温度を低下させる理由は、廃液の
加熱を90°C以下に抑えることにより、廃液に含まれ
るチオ硫酸アンモニウムや亜硫酸塩等が分解することな
くして、水分のみを効率よく蒸発させる効果を着目した
からである。
Next, the reason why a depressurizing means is used to reduce the pressure of the entire waste liquid is to lower the evaporation temperature of water in the waste liquid by heating it under reduced pressure. This is because we focused on the effect of efficiently evaporating only water by keeping the temperature below C, without decomposing ammonium thiosulfate, sulfite, etc. contained in the waste liquid.

ヒートポンプの加熱部を濃縮液中から液面上に及び/ま
たは液面上から濃縮液中に連続して設ける理由は、この
構成にすることによって、写真処理廃液の、加熱による
突沸を制御し、蒸発効率を上昇させる効果を発見したか
らである。
The reason why the heating part of the heat pump is continuously provided from the concentrated liquid to above the liquid level and/or from above the liquid level into the concentrated liquid is that by using this configuration, bumping of the photographic processing waste liquid due to heating can be controlled, This is because they discovered the effect of increasing evaporation efficiency.

発明者の観察では上記液面上の加熱で蒸気移動が加速さ
れている現象が明かに見られ、この効果が濃縮液中から
の蒸発効率を向上しているものと思われる。
The inventor's observation clearly shows a phenomenon in which the vapor transfer is accelerated by the heating above the liquid surface, and it is thought that this effect improves the evaporation efficiency from the concentrated liquid.

実験による比較では、この発明の構成のものは、25%
程度だけ、液中のみ加熱のものに比べて、蒸発水量が多
い結果を得ている。
In an experimental comparison, the configuration of this invention has a 25%
The result was that the amount of evaporated water was slightly larger than that of the one in which only the liquid was heated.

更に、上記写真処理廃液の加熱部と、蒸気凝縮部を連通
状態とし、全体を減圧した理由は、減圧による蒸発速度
向上と凝縮部までの経路短縮による装置の小型化、低コ
スト化を計ったものである。
Furthermore, the heating section for the photographic processing waste liquid and the steam condensing section were connected to reduce the overall pressure.The reason for this was to improve the evaporation rate by reducing the pressure and shorten the route to the condensing section, thereby reducing the size and cost of the device. It is something.

更に写真処理廃液を供給する経路に、固形物を除去する
フィルターを設けたから、加熱にあたり、突沸を防止で
きるものである。
Furthermore, since a filter for removing solid matter is provided in the path for supplying the photographic processing waste liquid, bumping can be prevented during heating.

〔実施例〕〔Example〕

次に、この発明の実施例を図をもって説明する。 Next, embodiments of the present invention will be described with reference to the drawings.

第1図は、実施例の全体構成を説明する断面図である。FIG. 1 is a sectional view illustrating the overall configuration of the embodiment.

水循環ポンプ14を始動すると、容器16からくみ上げ
られた水は、エジェクター15から、勢いよく下方へ吹
き出される。このときエジェクター15でT字状に連結
された気路23は負圧となるから、バルブ18を開くと
、蒸気凝縮部8及びこれに連通ずる蒸発濃縮カラム(以
下単にカラノ、ということがある)9の気室から、空気
が吸い出され、これら、蒸気凝縮部8及び該カラム9は
減圧される。
When the water circulation pump 14 is started, the water pumped up from the container 16 is vigorously blown downward from the ejector 15. At this time, the air passage 23 connected in a T-shape by the ejector 15 becomes under negative pressure, so when the valve 18 is opened, the vapor condensing section 8 and the evaporation concentration column (hereinafter sometimes simply referred to as "Carano") connected thereto are connected to the vapor condensing section 8. Air is sucked out from the air chamber 9, and these, the vapor condensing section 8 and the column 9 are depressurized.

次にバルブ20を開くと上記減圧によって、廃液は容器
19から吸い上げられて、フィルターユニット26を経
てカラム9内の上部に設けられたノズル21からカラム
9内に散布する。モしてカラム9内に廃液がたまり液面
Aに至ると液面センサー22が検知して、バルブ20を
閉じさせ注液が止まる。バルブ20は電磁弁を用いても
よい。
Next, when the valve 20 is opened, the waste liquid is sucked up from the container 19 by the reduced pressure, passes through the filter unit 26, and is sprayed into the column 9 from the nozzle 21 provided at the upper part of the column 9. When the waste liquid accumulates in the column 9 and reaches the liquid level A, the liquid level sensor 22 detects this, closes the valve 20, and stops liquid injection. The valve 20 may be a solenoid valve.

次にフィルターユニット26について説明する。Next, the filter unit 26 will be explained.

中空容器の入口31から廃液が入ってゆくが、円筒状の
多孔質のフィルター29が、底部とツク28にその両端
を密着して取り付けられ、この孔(直径2mm以下0.
5ミクロン以上の貫通穴)を通して該液が通り、内筒2
7の上部から出口30を通って該液が排出される構造で
、液中の固形物はフィルター29とフィルターユニット
26の外筒との間に残留するから、7タ28を開けて汚
れたフィルター29の交換を行なうときに取り除かれる
Waste liquid enters from the inlet 31 of the hollow container, and a cylindrical porous filter 29 is attached to the bottom and both ends of the tube 28 in close contact with each other.
The liquid passes through the inner cylinder 2 (through hole of 5 microns or more)
The structure is such that the liquid is discharged from the upper part of the filter 7 through the outlet 30, and solid matter in the liquid remains between the filter 29 and the outer cylinder of the filter unit 26, so open the filter 28 and remove the dirty filter. It is removed when performing the 29 exchange.

この例では、円筒状のフィルターを使用したが、これに
限定するものではなく、平板状のフィルターを境として
、液流を行なうこともできるし、単に直管の途中にフィ
ルターをつめ込んでもよい。
In this example, a cylindrical filter was used, but the invention is not limited to this; the liquid can flow using a flat filter as a boundary, or the filter may simply be packed in the middle of a straight pipe. .

突沸は特に写真廃液供給時に激しいことを発明者は注目
し、供給廃液に突沸のもとになる固形物が混入しないよ
うにした。
The inventor noticed that bumping was especially severe when supplying photographic waste liquid, and tried to prevent solid matter that would cause bumping from being mixed into the supplied waste liquid.

フィルターの穴径の好ましい範囲は0.5ミクロンから
1 mm、さらに好ましくは1ミクロンから0.5mm
である。
The preferred range of the hole diameter of the filter is 0.5 micron to 1 mm, more preferably 1 micron to 0.5 mm.
It is.

次に、ヒートポンプ1を詳しく説明する。ヒートポンプ
1は、コンプレッサー2き、空冷凝!11器3と、ファ
ンモーター5により駆動されるプロペラファン4と、加
熱部6と、冷却コイル13と、冷却部7とこれらを連結
するバイブと、この系内に注入した冷媒とよりなる。
Next, the heat pump 1 will be explained in detail. Heat pump 1 uses compressor 2 and air-cooled condensation! 11 unit 3, a propeller fan 4 driven by a fan motor 5, a heating section 6, a cooling coil 13, a cooling section 7, a vibrator connecting these, and a refrigerant injected into this system.

コンプレッサー2により圧縮された冷媒は高温となって
空冷凝縮器3に向けて吹き出される。ここで、ファンモ
ーター5で駆動されたプロペラファン4で強制空冷を行
なう。これはヒートポンプの暴走を防止し、かつ、加熱
部6の温度を制御し、高温によるガス発生を防止するた
めに行なわれる。
The refrigerant compressed by the compressor 2 reaches a high temperature and is blown out toward the air-cooled condenser 3. Here, forced air cooling is performed using a propeller fan 4 driven by a fan motor 5. This is done in order to prevent the heat pump from running out of control, control the temperature of the heating section 6, and prevent gas generation due to high temperatures.

次に上記強制空冷によって適温になった冷媒は加熱部6
に入る。加熱部6はカラム9に注入した廃液の液面A以
下の部分に連続して液面上にも配設し、それぞれ液面A
以下の部分では廃液を加熱し、液面上の部分では、発生
した蒸気を加熱する。
Next, the refrigerant that has reached an appropriate temperature due to the forced air cooling is heated to a heating section 6.
to go into. The heating unit 6 is also disposed continuously above the liquid level of the waste liquid injected into the column 9 below the liquid level A.
The part below heats the waste liquid, and the part above the liquid surface heats the generated steam.

そして加熱s6を通過した冷媒はドライヤー11゜キャ
ピラリーチューブ10を通って冷却コイル13に入って
、容器16に注入された水を冷却したのち、冷却部7に
入る。ここで、カラム9から蒸発してきた蒸気を冷却し
てのち、上記冷媒はコンプレッサー2に戻り1サイクル
を完了し、このザイクルを繰り返し行なう。
The refrigerant that has passed through the heating s6 passes through the dryer 11 and the capillary tube 10, enters the cooling coil 13, cools the water injected into the container 16, and then enters the cooling section 7. After cooling the vapor evaporated from the column 9, the refrigerant returns to the compressor 2 to complete one cycle, and this cycle is repeated.

この構成の特徴は、減圧手段として水循環ポンプによる
水の吹き出し力を活用し、その水を、ヒートポンプの冷
媒で冷却して使用していること、及び廃液の加熱蒸発を
行なう熱源にヒートポンプの加熱部(凝縮器)を使用し
、がっ、液面下だけでなく、液面上での蒸気加熱をも行
なうことにより、蒸発蒸気の上方への移動を早めて、蒸
発効率を大幅に向上したことである。
The features of this configuration are that the water blowing force of the water circulation pump is used as a pressure reduction means, and the water is cooled with the heat pump's refrigerant. By using a (condenser) to heat steam not only below the liquid level but also above the liquid level, the upward movement of evaporated steam is accelerated and evaporation efficiency is greatly improved. It is.

さらに効率設計として、カラム9を上お減圧したことで
、バルブ20を開けば、廃液を送液ポンプなしで汲み上
げてカラム9内に入れこむ構成としたから効率化及びコ
ンパクト化に効果的である。
Furthermore, as an efficient design, by reducing the pressure in the column 9, by opening the valve 20, the waste liquid is pumped up and put into the column 9 without a liquid pump, which is effective for efficiency and compactness. .

上記の構成で減圧下で加熱蒸発が行なわれると、カラム
9の廃液面からは、廃液が上方へ、勢いよくはね上がる
現象が起るので、これが冷却部7に入りこむのを防止す
るため、ハネ防止板24を設けに 。
When heating evaporation is carried out under reduced pressure with the above configuration, a phenomenon occurs in which the waste liquid violently splashes upward from the waste liquid surface of the column 9. To prevent this from entering the cooling section 7, a splash prevention is performed. Plate 24 is provided.

第2図(a)、(b) 、第3図(a)、(b)、第4
図、第5図にハネ防止板24の実施例を示す。
Figure 2 (a), (b), Figure 3 (a), (b), Figure 4
An embodiment of the splash prevention plate 24 is shown in FIG.

第2図(a)の側断面図及び第2図(b)の上面図で示
す実施例では壁面から突出するはね防止板24が両側か
ら交互に配置されていて、下方がらハネ上がったスラッ
ジは上方へ通り抜けることはできないようにしである。
In the embodiment shown in the side sectional view of FIG. 2(a) and the top view of FIG. 2(b), splash prevention plates 24 protruding from the wall surface are arranged alternately from both sides, and the sludge splashes up from below. so that it cannot pass upwards.

第3図(a)の側断面図及び第3図(b)の上面図で示
す実施例では、はね防止板24が壁面に複数段の穴明き
板24Kを固定する方式のもので、この穴は、上下板で
それぞれ位置をずらしてあり、下から直進するスラッジ
を止める如くしである。
In the embodiment shown in the side sectional view of FIG. 3(a) and the top view of FIG. 3(b), the splash prevention plate 24 is of a type in which a plurality of perforated plates 24K are fixed to the wall surface, These holes are located at different positions on the upper and lower plates to stop sludge flowing straight from below.

第4図の側断面図に示す実施例では壁面からリング状に
受け皿部24bが出ているその上に間隔をおいて傘24
aを設けてありその周辺が、受け皿部24bと重複して
いるから、下からのはね上がりスラッジは、上方に通り
抜けることがなく、傘24aにI;まったスラッジは受
け皿部24bに落下して回収される。第5図の側断面図
に示す実施例は糸くず状の多孔質部材を内部に層状につ
め込んだもので、この場合はスラッジが付着して目づま
りするから適宜取り替えることが必要である。
In the embodiment shown in the side cross-sectional view of FIG.
Since the periphery of the umbrella 24a overlaps with the receiving tray 24b, the sludge splashed up from below does not pass upward, and the sludge that collects on the umbrella 24a falls into the receiving tray 24b and is collected. be done. The embodiment shown in the side cross-sectional view of FIG. 5 is one in which a lint-like porous member is packed inside in layers, and in this case, sludge adheres to the member and causes clogging, so it is necessary to replace it as appropriate.

発生した水蒸気は、冷却部7で冷却凝縮され水滴として
、蒸気凝縮部8の底部8C1:たまるが、減圧手段によ
りバルブ18を通って、容器16に排出される。そして
、容器16にはオーバーフロー口を設け、上記凝縮水で
あふれた水はパイプ36によって凝縮水タンク35へと
流入し回収される。
The generated water vapor is cooled and condensed in the cooling section 7 and collected as water droplets at the bottom 8C1 of the steam condensing section 8, but is discharged into the container 16 through the valve 18 by the pressure reducing means. The container 16 is provided with an overflow port, and the water overflowing with the condensed water flows into the condensed water tank 35 through a pipe 36 and is collected.

このように蒸発濃縮が進み、廃液がスラッジ化すると、
上記のような冷熱サイクルのバランスが急にくずれると
ころがあって、それは、コンプレッサー2の圧縮後の出
口に於ける冷媒温度が100 ’0から120 ’Cに
急変することで検出される。そこで、この温度変化を温
度センサーをもって検出することによって、廃液のスラ
ッジ化検出として、コンプレッサー2を止め、水循環ポ
ンプ14を止める。
As evaporation concentration progresses and the waste liquid becomes sludge,
There is a point where the balance of the cooling/heating cycle as described above suddenly collapses, and this is detected when the refrigerant temperature at the outlet of the compressor 2 after compression suddenly changes from 100'0 to 120'C. Therefore, by detecting this temperature change using a temperature sensor, the compressor 2 is stopped and the water circulation pump 14 is stopped to detect that the waste liquid has turned into sludge.

このとき、容器16が大気圧に開口しているため、容器
16内の水が上記凝縮部8の減圧状態により、気路23
を通って吸い込まれてしまうがら、これを防止するため
に、バルブ18を三方弁として、上記停止時には気路2
3側を閉じて、大気に通じる開口を開く如くしている。
At this time, since the container 16 is open to atmospheric pressure, the water in the container 16 is reduced to the air passage 23 due to the reduced pressure in the condensing section 8.
In order to prevent this, the valve 18 is designed as a three-way valve, and the air passage 2 is closed at the time of the stop.
The third side is closed, leaving an opening to the atmosphere.

但し三方弁でなくても、気路23に大気に通じる開口を
開閉する電磁弁等を設けて、これを開口し、上記停止と
同時に大気圧でバランスさせてもよい。
However, instead of a three-way valve, an electromagnetic valve or the like for opening and closing an opening communicating with the atmosphere may be provided in the air passage 23, and this may be opened and balanced at atmospheric pressure at the same time as the above-mentioned stop.

しかるのち、カラム9の下部のバルブ25を開いて、ス
ラッジを排出する。ここで回収されたスラッジは銀を高
濃度で含むから、有価資源として密封容器にいれ、別途
銀回収を行なった上で適当な所へ廃棄する。
Thereafter, the valve 25 at the bottom of the column 9 is opened to discharge the sludge. The sludge collected here contains a high concentration of silver, so it is stored in a sealed container as a valuable resource, and the silver is collected separately before being disposed of at an appropriate location.

なお、この装置による濃縮度は、総合廃液で18〜20
倍まで濃縮でき、スラッジ化率は外見上98%である。
In addition, the concentration level with this device is 18 to 20 in total waste liquid.
It can be concentrated up to twice as much, and the sludge conversion rate is apparently 98%.

〔発明の効果〕〔Effect of the invention〕

このように構成したから、写真処理廃液の蒸発濃縮処理
装置を熱効率よく、小型で低コスト化することができる
ものである。
With this configuration, the apparatus for evaporating and concentrating photographic processing waste liquid can be made more thermally efficient, smaller, and lower in cost.

【図面の簡単な説明】 第1図は本発明の1実施例の断面図。 第2図(a)、第3図(a)、第4図、第5図はハネ防
止板24の各実施例の側断面図。 第2図(b)、第3図(b)はそれぞれ第2図(a)及
び第3図(a)に示す実施例の上面図。 1・・・ヒートポンプ  2・・・コンプレッサー3・
・・空冷凝縮器   4・・・プロペラファン5・・・
ファンヒーター 6・・・加熱部(凝縮器)7・・・冷
却部(蒸発器) 8・・・蒸気凝縮部9・・・蒸発濃縮
カラム(カラム) 10・・・キャビタリーチューブ 11・・・ドライヤー   13・・・冷却コイル14
・・・水循環ポンプ  15・・・エジェクター16・
・・容器      17・・減圧手段18・・バルブ
     19・・・容器20・・バルブ21・・・ノ
ズル 22・・・液面センサー  23・・・気路24・・・
ハネ防止板25・・・バルブ26・・・フィルターユニ
ット 27・・・内筒      28・・・フタ29・・・
フィルター   30・・出口31・・・入口
BRIEF DESCRIPTION OF THE DRAWINGS FIG. 1 is a sectional view of one embodiment of the present invention. FIG. 2(a), FIG. 3(a), FIG. 4, and FIG. 5 are side sectional views of each embodiment of the splash prevention plate 24. FIG. 2(b) and FIG. 3(b) are top views of the embodiment shown in FIG. 2(a) and FIG. 3(a), respectively. 1...Heat pump 2...Compressor 3.
...Air-cooled condenser 4...Propeller fan 5...
Fan heater 6... Heating section (condenser) 7... Cooling section (evaporator) 8... Vapor condensing section 9... Evaporation concentration column (column) 10... Cavitary tube 11... Dryer 13...Cooling coil 14
...Water circulation pump 15...Ejector 16.
... Container 17 ... Pressure reducing means 18 ... Valve 19 ... Container 20 ... Valve 21 ... Nozzle 22 ... Liquid level sensor 23 ... Air path 24 ...
Splash prevention plate 25... Valve 26... Filter unit 27... Inner cylinder 28... Lid 29...
Filter 30... Outlet 31... Inlet

Claims (4)

【特許請求の範囲】[Claims] (1)写真処理廃液を受け入れ、加熱手段をもって加熱
蒸発を行なう加熱部と、上記発生した蒸気を冷却手段を
もって冷却凝縮する凝縮部と、上記加熱部に写真処理廃
液を供給する手段とを有する写真処理廃液の蒸発濃縮処
理装置に於て、写真処理廃液を供給する経路に、穴径が
2mm以下、0.5ミクロン以上の多数の貫通穴を有す
るフィルターを設けたことを特徴とする写真処理廃液の
蒸発濃縮処理装置。
(1) A photograph having a heating section that receives photographic processing waste liquid and performs heat evaporation using a heating means, a condensing section that cools and condenses the generated vapor using a cooling means, and a means for supplying the photographic processing waste liquid to the heating section. A photographic processing waste liquid characterized in that, in an evaporation concentration processing apparatus for processing waste liquid, a filter having a large number of through holes with hole diameters of 2 mm or less and 0.5 microns or more is provided in the path for supplying the photographic processing waste liquid. evaporation concentration processing equipment.
(2)上記加熱手段がヒートポンプの加熱部である請求
項1記載の写真処理廃液の蒸発濃縮処理装置。
(2) The apparatus for evaporating and concentrating photographic processing waste liquid according to claim 1, wherein the heating means is a heating section of a heat pump.
(3)上記加熱手段による加熱蒸発濃縮を減圧下で行な
い、2kcal/cm^2・hr以下で蒸気が加熱部か
ら出ていく経路に障害物を設けたことを特徴とする請求
項1記載の写真処理廃液の蒸発濃縮処理装置。
(3) The heating evaporation concentration by the heating means is performed under reduced pressure, and an obstacle is provided in a path through which the steam exits from the heating section at a rate of 2 kcal/cm^2.hr or less. Evaporative concentration treatment equipment for photographic processing waste liquid.
(4)上記加熱手段がヒートポンプの加熱部である請求
項3記載の写真処理廃液の蒸発濃縮処理装置。
(4) The apparatus for evaporating and concentrating photographic processing waste liquid according to claim 3, wherein the heating means is a heating section of a heat pump.
JP02127237A 1990-05-17 1990-05-17 Evaporation concentration processing equipment for photographic processing waste liquid Expired - Fee Related JP3111256B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP02127237A JP3111256B2 (en) 1990-05-17 1990-05-17 Evaporation concentration processing equipment for photographic processing waste liquid

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP02127237A JP3111256B2 (en) 1990-05-17 1990-05-17 Evaporation concentration processing equipment for photographic processing waste liquid

Publications (2)

Publication Number Publication Date
JPH0422483A true JPH0422483A (en) 1992-01-27
JP3111256B2 JP3111256B2 (en) 2000-11-20

Family

ID=14955107

Family Applications (1)

Application Number Title Priority Date Filing Date
JP02127237A Expired - Fee Related JP3111256B2 (en) 1990-05-17 1990-05-17 Evaporation concentration processing equipment for photographic processing waste liquid

Country Status (1)

Country Link
JP (1) JP3111256B2 (en)

Also Published As

Publication number Publication date
JP3111256B2 (en) 2000-11-20

Similar Documents

Publication Publication Date Title
EP0457303B1 (en) Apparatus for concentrating waste liquor from photographic process
AU603400B2 (en) Method of treating photographic process waste liquor through concentration by evaporation and apparatus therefor
JPH0422483A (en) Apparatus for evaporative concentration treatment of waste photographic processing solution
JPS63151301A (en) Apparatus for evaporation and concentration treatment of waste photographic treatment liquid
JPH0418976A (en) Evaporating and thickening device for waste photographic processing liquid
JPH0427483A (en) Vaporization-condensation treating apparatus for photograph waste solution
JPH0427484A (en) Method for reducing waste of processing solution for silver halide photosensitive material
JPH0422480A (en) Apparatus for evaporative concentration treatment of waste photographic processing solution
JPH03238079A (en) Vacuum evaporative concentrating device for photographic processing liquid waste
JPH0422484A (en) Evaporative concentration treatment system for waste photographic processing solution
JPH03267189A (en) Evaporation concentrating device for waste photographic processing liquid
EP0292282B1 (en) Method of treating photographic process waste liquor through concentration by evaporation
JPH0422481A (en) Apparatus for evaporative concentration treatment of waste photographic processing solution
JP2952506B2 (en) Evaporation and concentration equipment for photographic processing waste liquid
JPH03293081A (en) Vaporizing and concentrating equipment for photographic processing waste liquid
JPH03258386A (en) Device for evaporating and concentrating waste photographic processing solution under reduced pressure
JPH03288587A (en) Apparatus for vacuum evaporative concentration of waste photographic processing solution
JPH03131381A (en) Photographic developer wastewater treatment apparatus
JPH04341303A (en) Evaporation concentration device of aqueous solution
JPH0422482A (en) Apparatus for evaporative concentration treatment of waste photographic processing solution
JPH03262584A (en) Apparatus for evaporating and concentrating waste liquid of photographic processing
JPH03266840A (en) Automatic developing device for photographic sensitive material
JPH03242281A (en) Vacuum evaporating and concentrating device for waste photographic processing liquid
JPH03293083A (en) Method and equipment for vaporizing and concentrating photographic processing waste liquid
JPH05184801A (en) Evaporating concentrator for water solution

Legal Events

Date Code Title Description
S531 Written request for registration of change of domicile

Free format text: JAPANESE INTERMEDIATE CODE: R313531

S533 Written request for registration of change of name

Free format text: JAPANESE INTERMEDIATE CODE: R313533

R350 Written notification of registration of transfer

Free format text: JAPANESE INTERMEDIATE CODE: R350

LAPS Cancellation because of no payment of annual fees