JPH02149396A - Apparatus for treating waste liquid of photographic processing - Google Patents
Apparatus for treating waste liquid of photographic processingInfo
- Publication number
- JPH02149396A JPH02149396A JP63303801A JP30380188A JPH02149396A JP H02149396 A JPH02149396 A JP H02149396A JP 63303801 A JP63303801 A JP 63303801A JP 30380188 A JP30380188 A JP 30380188A JP H02149396 A JPH02149396 A JP H02149396A
- Authority
- JP
- Japan
- Prior art keywords
- waste liquid
- concentrate
- photographic processing
- processing waste
- liquid
- 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
Links
- 239000007788 liquid Substances 0.000 title claims abstract description 94
- 238000012545 processing Methods 0.000 title claims abstract description 88
- 239000002699 waste material Substances 0.000 title claims abstract description 72
- 239000012141 concentrate Substances 0.000 claims abstract description 70
- 238000001704 evaporation Methods 0.000 claims abstract description 23
- 230000008020 evaporation Effects 0.000 claims abstract description 20
- 238000010438 heat treatment Methods 0.000 claims abstract description 18
- 238000000354 decomposition reaction Methods 0.000 abstract description 7
- 238000013021 overheating Methods 0.000 abstract description 6
- 230000003467 diminishing effect Effects 0.000 abstract 1
- 238000004519 manufacturing process Methods 0.000 abstract 1
- 238000007790 scraping Methods 0.000 description 15
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 15
- 235000019645 odor Nutrition 0.000 description 9
- 238000000034 method Methods 0.000 description 7
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 6
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 description 6
- 238000001514 detection method Methods 0.000 description 6
- 229910000037 hydrogen sulfide Inorganic materials 0.000 description 6
- 239000000463 material Substances 0.000 description 6
- 238000005406 washing Methods 0.000 description 6
- 238000007664 blowing Methods 0.000 description 3
- 238000011161 development Methods 0.000 description 3
- 238000010586 diagram Methods 0.000 description 3
- 239000002245 particle Substances 0.000 description 3
- RAHZWNYVWXNFOC-UHFFFAOYSA-N Sulphur dioxide Chemical compound O=S=O RAHZWNYVWXNFOC-UHFFFAOYSA-N 0.000 description 2
- 238000004061 bleaching Methods 0.000 description 2
- 239000004020 conductor Substances 0.000 description 2
- 239000000498 cooling water Substances 0.000 description 2
- 239000012153 distilled water Substances 0.000 description 2
- 239000012530 fluid Substances 0.000 description 2
- 239000007789 gas Substances 0.000 description 2
- 238000002156 mixing Methods 0.000 description 2
- 230000000630 rising effect Effects 0.000 description 2
- 150000003839 salts Chemical class 0.000 description 2
- 238000000926 separation method Methods 0.000 description 2
- 229910052709 silver Inorganic materials 0.000 description 2
- 239000004332 silver Substances 0.000 description 2
- 230000003746 surface roughness Effects 0.000 description 2
- 150000004764 thiosulfuric acid derivatives Chemical class 0.000 description 2
- CPELXLSAUQHCOX-UHFFFAOYSA-M Bromide Chemical compound [Br-] CPELXLSAUQHCOX-UHFFFAOYSA-M 0.000 description 1
- BQCADISMDOOEFD-UHFFFAOYSA-N Silver Chemical compound [Ag] BQCADISMDOOEFD-UHFFFAOYSA-N 0.000 description 1
- LSNNMFCWUKXFEE-UHFFFAOYSA-N Sulfurous acid Chemical compound OS(O)=O LSNNMFCWUKXFEE-UHFFFAOYSA-N 0.000 description 1
- 239000004809 Teflon Substances 0.000 description 1
- 229920006362 Teflon® Polymers 0.000 description 1
- 150000003863 ammonium salts Chemical class 0.000 description 1
- 230000033228 biological regulation Effects 0.000 description 1
- 230000006837 decompression Effects 0.000 description 1
- 238000004821 distillation Methods 0.000 description 1
- 238000001035 drying Methods 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 238000010828 elution Methods 0.000 description 1
- 210000002615 epidermis Anatomy 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 239000000284 extract Substances 0.000 description 1
- 238000000605 extraction Methods 0.000 description 1
- 238000011049 filling Methods 0.000 description 1
- 230000005484 gravity Effects 0.000 description 1
- 235000003642 hunger Nutrition 0.000 description 1
- 238000012423 maintenance Methods 0.000 description 1
- 229910001120 nichrome Inorganic materials 0.000 description 1
- 150000007524 organic acids Chemical class 0.000 description 1
- 238000012946 outsourcing Methods 0.000 description 1
- 239000010453 quartz Substances 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N silicon dioxide Inorganic materials O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 1
- -1 silver halide Chemical class 0.000 description 1
- 230000006641 stabilisation Effects 0.000 description 1
- 238000011105 stabilization Methods 0.000 description 1
- 239000003381 stabilizer Substances 0.000 description 1
- 230000037351 starvation Effects 0.000 description 1
- LSNNMFCWUKXFEE-UHFFFAOYSA-L sulfite Chemical class [O-]S([O-])=O LSNNMFCWUKXFEE-UHFFFAOYSA-L 0.000 description 1
- 150000003464 sulfur compounds Chemical class 0.000 description 1
- 230000008719 thickening Effects 0.000 description 1
- DHCDFWKWKRSZHF-UHFFFAOYSA-L thiosulfate(2-) Chemical compound [O-]S([S-])(=O)=O DHCDFWKWKRSZHF-UHFFFAOYSA-L 0.000 description 1
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
Landscapes
- Photographic Processing Devices Using Wet Methods (AREA)
Abstract
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]
一般に、ハロゲン化銀写真感光材料の写真処理は、黒白
感光材料の場合には現像、定着、水洗等、カラー感光材
料の場合には発色現像、漂白定着(又は漂白、定着)、
水洗、安定化等の機能の1つ又は2つ以上を有する処理
液を用いた工程を組合せて行なわれている。[Prior Art] In general, photographic processing of silver halide photographic materials includes development, fixing, washing, etc. in the case of black and white materials, and color development, bleach-fixing (or bleaching, fixing) in the case of color photographic materials. ,
A combination of processes using a treatment liquid having one or more functions such as water washing and stabilization is carried out.
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い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、定着液に招ける銀
錯塩のような)を除去して処理液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部が廃棄
されている。In photographic processing in which a large amount of light-sensitive material is processed, the components consumed during processing are replenished, while the components that are concentrated by elution or evaporation into the processing solution (
For example, methods are used to maintain the performance of the processing solution at a constant level by removing bromide ions in the developer solution and silver complex salts introduced into the fixer solution to keep the processing solution components constant. A replenisher is added to the processing solution, and a portion of the processing solution is discarded to remove thickening components in photographic processing.
近年、補充液は水洗の補充液である水洗水な含めて公害
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
像機の冷却水等で稀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. It is led through a waste liquid pipe, diluted with waste liquid from washing water, cooling water from automatic processors, 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)、安定液算コの
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
、廃液を貯溜しておくのにかなりのスペースが必要とな
るし、またコスト的にも極めて高価である。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。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。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] It has become virtually impossible to dispose of stable liquids (or bleaching solutions, fixing solutions) and stabilizers. 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 requires a considerable amount of space to store the waste liquid, and is also extremely expensive. Furthermore, pollution treatment equipment has drawbacks such as extremely large initial investment (initial cost) and the need for a fairly large space for maintenance. Therefore, waste liquid is generally collected by a waste liquid collection company 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.
It is difficult to get people to come and 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な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1id−70841号
等に示されている。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. This is shown in Utility Model Application Publication No. 1ID-70841.
[発明が解決しようとする課題]
ところで、このように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。これは写真処理廃液
に含有される定着液や漂白定着液としてよく用いられる
特有のイオウ系化合物、例えばチオ硫酸塩や亜硫酸塩の
分解によるものである。[Problems to be Solved by the Invention] By the way, when photographic processing waste liquid is evaporated in this manner, harmful or extremely malodorous gases such as sulfur dioxide gas, hydrogen sulfide, and ammonia gas are generated. This is due to the decomposition of specific sulfur compounds, such as thiosulfate and sulfite, which are often used in fixers and bleach-fixers contained in photographic processing waste solutions.
このため、臭気成分を除去すべく種々の研究、実験を行
なったところ、加熱手段の加熱で写真処理廃液を蒸発濃
縮し、所定量蓄積すると取り出して廃棄しており、この
蓄積された濃縮物が加熱され続けると、濃縮物が過熱分
解して、硫化水素、アンモニアガス等が発生する一原因
となっていることが判明した。For this reason, various studies and experiments have been conducted to remove odor components, and it has been found that photographic processing waste liquid is evaporated and concentrated by heating with a heating means, and when a predetermined amount has accumulated, it is taken out and disposed of. It has been found that continued heating causes the concentrate to overheat and decompose, causing hydrogen sulfide, ammonia gas, etc. to be generated.
従って、濃縮物が過熱分解して、硫化水素、アンモニア
ガス等が発生する前に、連続的に濃縮物を取り出す必要
があり、例えば写真処理廃液の循環系にフィルタを備え
、このフィルタによってろ通して濃縮物を取り出すこと
が行なわれるが、この場合目詰まりを起しやすく、運転
に支障をきたすおそれがある等の問題があり、実用的で
ない。Therefore, it is necessary to take out the concentrate continuously before it decomposes overheating and generates hydrogen sulfide, ammonia gas, etc. For example, a filter is provided in the circulation system for photographic processing waste liquid, and the filter is passed through the filter. However, in this case, there are problems such as clogging, which may impede operation, and is not practical.
この発明はかかる点に鑑みなされたもので、濃縮物を取
り出しながら連続処理が可能で、濃縮物の過熱分解を防
止し、悪臭の発生を軽減することができる写真処理廃液
の処理装置を提供することを目的としている。The present invention has been made in view of the above, and provides a processing device for photographic processing waste liquid that is capable of continuous processing while taking out the concentrate, prevents overheating decomposition of the concentrate, and reduces the occurrence of bad odors. The purpose is to
[課題を解決するための手段〕
前記課題を解決するために、この発明は写真処理廃液を
、加熱手段で加熱して蒸発濃縮せしめる写真処理廃液の
処理装置において、写真処理廃液を蒸発により濃縮した
液中に生じる濃縮物を、濃縮液中より直接連続的に取り
出す手段とを備えることを特徴としている。[Means for Solving the Problems] In order to solve the above-mentioned problems, the present invention provides a processing apparatus for photographic processing waste liquids that evaporates and concentrates photographic processing waste liquids by heating the photographic processing waste liquids with a heating means. It is characterized by comprising means for directly and continuously taking out the concentrate produced in the liquid from the concentrate.
また、この写真処理廃液の処理装置において、濃縮液を
収納する容器を備え、この容器に沈殿する濃縮物を直接
連続的に取り出す手段を有することを特徴としている。Further, this processing apparatus for photographic processing waste liquid is characterized in that it is provided with a container for storing a concentrated liquid, and has a means for directly and continuously taking out the concentrated liquid precipitated in this container.
この発明の加熱手段はニクロム線であっても良いし、カ
ートリッジヒータ、石英ヒータ、テフロンヒータ、棒ヒ
ータやパネルヒータのように加工成型されたヒータまた
はマイクロウェーブによる加熱であっても良い。また、
写真処理廃液に導電材料を直接接触させ、この導電材料
によって写真処理廃液中に電液を流すと共に、加熱する
ようにしてもよい。The heating means of the present invention may be a nichrome wire, or may be heated by a molded heater such as a cartridge heater, quartz heater, Teflon heater, rod heater, or panel heater, or microwave heating. Also,
A conductive material may be brought into direct contact with the photographic processing waste liquid, and the conductive material may cause an electric liquid to flow into the photographic processing waste liquid and heat the photographic processing waste liquid.
さらに、ヒートポンプを使用することもでき、このヒー
トポンプは低温の熱源から熱エネルギーを取り出し、そ
れをより高温な利用しやすい熱エネルギーに変換する装
置であり、ヒートポンプを用いて写真処理廃液を加熱し
て、この加熱によりて生じる蒸気を冷却して蒸留水を得
、このとき熱交換で得られる熱エネルギーで加熱でき、
効率的な処理ができる。Additionally, you can use a heat pump, which is a device that extracts thermal energy from a low-temperature heat source and converts it into higher-temperature, more usable thermal energy. , the steam generated by this heating is cooled to obtain distilled water, which can be heated using the thermal energy obtained through heat exchange.
Efficient processing is possible.
この加熱手段の熱密度は、好ましく1〜20W/ c
m ’であり、さらに好ましくは5W/cm2に設定さ
れる。The heat density of this heating means is preferably 1 to 20 W/c
m', more preferably set to 5 W/cm2.
写真処理廃液と、この蒸発により濃縮した液中に生じる
濃縮物とを収納する容器には、写真処理廃液とこの蒸発
濃縮によって生じる濃縮物とを収納することができれば
大きさや形状等特に限定されない。また、この容器に加
熱手段を備えてもよく、さらに容器は循環系を備え写真
処理廃液を循環させてもよく、この場合循環系に加熱手
段を備えることもできる。The container for storing the photographic processing waste liquid and the concentrate produced in the liquid concentrated by the evaporation is not particularly limited in size or shape, as long as it can contain the photographic processing waste liquid and the concentrate produced by the evaporation concentration. Further, the container may be equipped with a heating means, and furthermore, the container may be equipped with a circulation system to circulate the photographic processing waste liquid, and in this case, the circulation system can also be equipped with a heating means.
写真処理廃液を蒸発濃縮する温度は100℃以下が突沸
が生じなく、濃縮物の過熱分解を防止でき好ましく、こ
の温度は加熱によって生じるガスを含む蒸気と写真処理
廃液とを分離させると、濃縮された濃縮物の過熱分解を
より有効に防止でき、硫化水素、アンモニアガス等の臭
気の発生を大幅に抑制することができる範囲に設定され
る。The temperature at which the photographic processing waste liquid is evaporated and concentrated is preferably 100°C or lower, since bumping does not occur and overheating decomposition of the concentrate is prevented. The temperature is set within a range that can more effectively prevent overheated decomposition of the concentrated product and can significantly suppress the generation of odors such as hydrogen sulfide and ammonia gas.
この蒸発濃縮の温度は、常圧下で100℃以下が、蒸発
によって分離される濃縮物の粒径が大ぎくなって沈殿し
やすくなり、また、比重の小さいものが少なくなり、こ
の発明の目的のためには、50〜95℃が好ましく、さ
らに好ましくは60〜85℃である。また、減圧下で蒸
発濃縮を行なうと、さらに濃縮物の粒径が大きくなって
沈殿しやすくなる。この減圧下での蒸発濃縮の温度は、
30〜90℃が好ましく、さらに好ましくは40〜80
℃である。If the temperature of this evaporative concentration is 100°C or less under normal pressure, the particle size of the concentrate separated by evaporation becomes large and tends to precipitate, and particles with low specific gravity decrease, which is the purpose of the present invention. For this purpose, the temperature is preferably 50 to 95°C, more preferably 60 to 85°C. Furthermore, when evaporation and concentration are performed under reduced pressure, the particle size of the concentrate becomes even larger, making it easier to precipitate. The temperature of this evaporation concentration under reduced pressure is
30~90℃ is preferable, more preferably 40~80℃
It is ℃.
このように減圧手段で減圧して加熱すると、液中より濃
縮物を直接回収し易くなるばかりでなく、常圧の蒸発方
式に比較して蒸発濃縮物中に発生するタールが少なく、
蒸発釜の壁への付着物も低減することができる。By reducing the pressure and heating with a pressure reducing means, it is not only easier to recover the concentrate directly from the liquid, but also produces less tar in the evaporated concentrate compared to the normal pressure evaporation method.
It is also possible to reduce deposits on the walls of the evaporation pot.
この減圧は好ましくは610mmHg以下にすることで
あり、さらに好ましくは520mmHg以下にすること
であり、特に好ましくは230mmHg以下にすること
である。また、減圧の下限は特にないが、減圧状態を作
るときの装置のコストよりlmmHg以上が好ましく、
10mmHg以上であることが簡易な装置で済み好まし
い。This reduced pressure is preferably 610 mmHg or less, more preferably 520 mmHg or less, particularly preferably 230 mmHg or less. In addition, there is no particular lower limit to the reduced pressure, but it is preferably 1 mmHg or more in view of the cost of the equipment used to create the reduced pressure state.
It is preferable that the pressure is 10 mmHg or more because a simple device can be used.
さらに、減圧手段は真空ポンプ、エジェクター等が使用
される。エジェクターを使用する場合にはエジェクター
中に送り込まれる水は、水道の蛇口から直接導いても良
いが、九本をポンプによって循環させることが配管が省
略でき好ましい。さらに、好ましい実施態様としては凝
結氷をポンプによって循環させ、エジェクター中に送り
込む方式がある。Furthermore, a vacuum pump, an ejector, etc. are used as the pressure reducing means. When an ejector is used, the water sent into the ejector may be led directly from a water tap, but it is preferable to circulate the water using nine pumps, since piping can be omitted. Furthermore, as a preferred embodiment, there is a method in which the frozen ice is circulated by a pump and fed into the ejector.
減圧手段として、蒸気以外の真空ポンプ等としては86
/87科学機器総覧(編集兼発行所、東京科学機器協会
)第537頁〜第610頁記載のものを使用することも
できる。86 as a vacuum pump other than steam as a pressure reducing means
/87 Scientific Instruments Directory (edited and published by Tokyo Scientific Instruments Association), pages 537 to 610 can also be used.
また、この発明の写真処理廃液の処理装置において、循
環系に空気を混入させることができ、この空気量は加熱
量に対して0,1〜100J2/kcaJ2が好ましい
。この空気の混入によって、写真処理廃液の突沸状態を
なくし蒸発温度を低下させて、硫化水素、アンモニアガ
ス等の臭気の発生を抑制する。Further, in the photographic processing waste liquid processing apparatus of the present invention, air can be mixed into the circulation system, and the amount of air is preferably 0.1 to 100 J2/kcaJ2 relative to the amount of heating. By mixing this air, the bumping state of the photographic processing waste liquid is eliminated and the evaporation temperature is lowered, thereby suppressing the generation of odors such as hydrogen sulfide and ammonia gas.
この発明において、写真処理廃液を蒸発により濃縮した
液中に生じる濃縮物を、濃縮液中から直接連続的に取り
出す手段とは、自動的に取り出す手段であり、断続的な
取り出し装置の稼動によるものも含まれる。この濃縮物
の取り出しは濃縮液が濃縮物に付着して取り出されるこ
とを含んでおり、この濃縮液の取り出しは少ない方が好
ましい。この直接連続的に取り出す手段として、無端ベ
ルト等の搬送手段上に濃縮物を蓄積させて取り出すもの
があり、この直接連続的に取り出す手段と場合無端ベル
トの表面は濃縮物を掻き上げることが可能な表面粗さに
設定され、また無端ベルトの表面に掻上羽根等を設けて
もよい。さらに、容器に蓄積する濃縮物を回転する掻き
取り手段等で掻き上げるようにすることができる。この
ようにして、写真処理廃液の濃縮蒸発で生じる濃縮物を
連続的に直接取り出すと、濃縮物が加熱されることを防
止でき、臭気の発生を軽減することができる。In this invention, the means for directly and continuously taking out the concentrate generated in the liquid obtained by concentrating the photographic processing waste liquid by evaporation is a means for automatically taking out the concentrate produced in the liquid by evaporating the photographic processing waste liquid, which is a means for automatically taking out the concentrate produced by the intermittent operation of the taking-out device. Also included. Removal of this concentrate includes the fact that the concentrate adheres to the concentrate and is removed, and it is preferable that the amount of concentrated liquid removed is small. As a means for directly and continuously taking out the concentrate, there is a method of accumulating the concentrate on a conveying means such as an endless belt and then taking it out. The surface roughness of the endless belt may be set to a certain level, and scraping blades or the like may be provided on the surface of the endless belt. Furthermore, the concentrate accumulated in the container can be scraped up by a rotating scraping means or the like. In this way, when the concentrate produced by concentration and evaporation of the photographic processing waste liquid is continuously and directly taken out, the concentrate can be prevented from being heated, and the generation of odor can be reduced.
この取り出された濃縮物は水分を多く含んでおり、この
水分を除去するために乾燥することが好ましく、この乾
燥は加熱或いは空気の吹き付け、また加熱と空気の吹き
付けを併用してもよく、或いは熱風吹き付けで乾燥させ
ることが好ましい。This extracted concentrate contains a large amount of water, and is preferably dried to remove this water. This drying may be performed by heating or blowing air, or by a combination of heating and blowing air, or It is preferable to dry by blowing hot air.
この濃縮物はバッグに収納して廃棄され、このバッグに
は満杯検出手段を備えることが好ましい。さらに、この
満杯検出手段としては重量検出が好ましく、この満杯検
出信号により、運転を停止する制御が行なわれる。This concentrate is disposed of in a bag, which bag is preferably provided with fullness detection means. Furthermore, weight detection is preferable as the fullness detection means, and control for stopping the operation is performed based on this fullness detection signal.
この発明による処理を行なうことができる写真処理廃液
の代表例については、この出願人が先に出願した特願昭
82L−194615号明細書等に記載されるものが用
いられ、特に、この発明の処理装置においては、チオ硫
酸塩、亜硫酸塩、アンモニラム塩を多量に含有する写真
処理廃液の場合に有効であり、特に有機酸第2鉄錯塩及
びチオ硫酸塩を含有する場合極めて有効である。Typical examples of photographic processing waste liquids that can be processed according to the present invention include those described in Japanese Patent Application No. 1982-194615 previously filed by the present applicant. In processing equipment, it is effective for photographic processing waste liquids containing large amounts of thiosulfates, sulfites, and ammonium salts, and is particularly effective when containing organic acid ferric complex salts and thiosulfates.
この発明の好ましい適用例としては、自動現像機による
写真感光材料の現像処理に伴ない発生する写真処理廃液
を自動現像機内もしくはその近傍にて処理を行なうのに
適している。A preferred application of the present invention is to treat photographic processing waste liquid generated during the development of photographic light-sensitive materials using an automatic processor in or near the automatic processor.
[作用]
この発明では、写真処理廃液を蒸発により濃縮し、沈殿
する濃縮物を液中から直接連続的に取り出している。こ
のため、蒸発濃縮によって生じる濃縮物が蓄積して、過
加熱されることがなくなり、濃縮物の過熱分解を防止し
て、悪臭の発生を軽減することができる。[Operation] In this invention, the photographic processing waste liquid is concentrated by evaporation, and the precipitated concentrate is directly and continuously taken out from the liquid. Therefore, the concentrate produced by evaporation concentration will not accumulate and be overheated, and the concentrate will be prevented from being decomposed by overheating, thereby reducing the occurrence of bad odor.
また、濃縮液を収納する容器に、濃縮物を沈殿させ、こ
の沈殿する濃縮物を直接連続的に取り出すようにすると
、多くの濃縮物を容易に取り出すことができるようにな
る。Further, if the concentrate is allowed to settle in a container for storing the concentrate and the precipitated concentrate is directly and continuously taken out, a large amount of the concentrate can be easily taken out.
[実施例]
第1図はこの発明の写真処理廃液の処理装置を示す概略
構成図である。[Example] FIG. 1 is a schematic diagram showing a processing apparatus for photographic processing waste liquid according to the present invention.
図において、符号1は写真処理廃液とこの蒸発濃縮によ
って生じる濃縮物とを収納する容器で、この容器1には
連結バイブ2が備えられている。In the figure, reference numeral 1 denotes a container for storing photographic processing waste liquid and a concentrate produced by evaporation and concentration of the waste liquid, and this container 1 is equipped with a connecting vibrator 2.
この連結バイブ2にはヒータ3が設けられており、この
ヒータ3によって写真処理廃液が加熱されて循環し、こ
の蒸発濃縮によって生じる濃縮液中に生じる濃縮物は容
器1の底部1aに沈澱するようになっている。ヒータ3
は連結バイブ2の内部に配置し、写真処理廃液を直接加
熱するようにしてもよく、また容器1に設けてもよい。This connecting vibe 2 is provided with a heater 3, and the photographic processing waste liquid is heated and circulated by the heater 3, and the concentrate produced in the concentrate produced by this evaporation concentration is deposited at the bottom 1a of the container 1. It has become. Heater 3
may be placed inside the connecting vibrator 2 to directly heat the photographic processing waste liquid, or may be provided in the container 1.
容器1には液面検出センサ4が設けられており、この液
面検出センサ4で循環系の写真処理廃液の液量を監視し
ている。この容器1には無端ベルト5が所定角度傾斜し
て設けられ、この無端ベルト5の一端部5aは写真処理
廃液の液中で容器1の底部1aに位置し、他端部5bは
液外で容器1の濃縮物取出し部1bに位置している。写
真処理廃液の蒸発濃縮によって生じる濃縮物は無端ベル
ト5上に蓄積し、この無端ベルト5の駆動で付着したま
ま連続的に取り出され、容器1の濃縮物取出し部1bに
設けられた掻取部材6で掻き落とされ、バッグ7に排出
される。無端ベルト5の表面は濃縮物を取出すことが可
能な表面粗さに設定され、また無端ベルト5の傾斜角度
も濃縮物を取出すことが可能な角度に設定される。容器
1の濃縮物取出し部1bにはエアポンプ8の駆動で、空
気がヒータ9を介して送られ、濃縮物を乾燥させるよう
になつており、バッグ7には乾燥された濃縮物が収納さ
れる。A liquid level detection sensor 4 is provided in the container 1, and the liquid level detection sensor 4 monitors the amount of photographic processing waste liquid in the circulation system. This container 1 is provided with an endless belt 5 inclined at a predetermined angle, one end 5a of this endless belt 5 is located at the bottom 1a of the container 1 in the photographic processing waste liquid, and the other end 5b is located outside the liquid. It is located at the concentrate outlet portion 1b of the container 1. The concentrate generated by evaporation concentration of the photographic processing waste liquid is accumulated on the endless belt 5, and is continuously taken out while remaining adhered by the drive of the endless belt 5. 6 and is scraped off and discharged into a bag 7. The surface of the endless belt 5 is set to a surface roughness that allows the concentrate to be taken out, and the inclination angle of the endless belt 5 is also set to an angle that allows the concentrate to be taken out. Air is sent to the concentrate take-out part 1b of the container 1 via a heater 9 by driving an air pump 8 to dry the concentrate, and the dried concentrate is stored in the bag 7. .
容器1の上部には分離手段1oが設けられ、この分離手
段10の内部には邪魔板10aが配置されており、写真
処理廃液の蒸気と濃縮物とを分離し、蒸気は蒸気排出管
11を介して取り出され、濃縮物は容器1に落下する。Separation means 1o is provided in the upper part of the container 1, and a baffle plate 10a is arranged inside this separation means 10 to separate the vapor of the photographic processing waste liquid from the concentrate. The concentrate falls into container 1.
この蒸気排出管11を介して取り出される蒸気は、容器
1の濃縮物取出し部1bから蒸気排出管12を介して取
り出される蒸気と合流して凝縮器13に送られる。この
凝縮器13で蒸気を冷却して凝縮し、これにより得られ
る蒸留水が蒸留タンク14に貯留される。The steam taken out through the steam exhaust pipe 11 is combined with the steam taken out through the steam exhaust pipe 12 from the concentrate take-out part 1b of the container 1, and is sent to the condenser 13. The steam is cooled and condensed in the condenser 13, and the resulting distilled water is stored in the distillation tank 14.
凝縮器13から臭気を含む空気はエアポンプ15の作動
で、配管16を介して写真処理廃液と混合して、連結バ
イブ2に供給されて循環系に戻される。この配管16に
は廃液供給ポンプ17に駆動で、写真処理廃液が廃液タ
ンク18から供給されるようになっている。Odor-containing air from the condenser 13 is mixed with the photographic processing waste liquid through the piping 16 by the operation of the air pump 15, and is supplied to the connecting vibe 2 and returned to the circulation system. This piping 16 is driven by a waste liquid supply pump 17 to supply photographic processing waste liquid from a waste liquid tank 18 .
この配管16に混入する空気量は加熱量に対して0.1
〜100j2/kcalが好ましく、この空気の混入に
よって、写真処理廃液の蒸発温度を低下させて、硫化水
素、アンモニアガス等の臭気の発生を抑制する。The amount of air mixed into this pipe 16 is 0.1 with respect to the amount of heating.
-100j2/kcal is preferable, and by mixing this air, the evaporation temperature of the photographic processing waste liquid is lowered, and the generation of odors such as hydrogen sulfide and ammonia gas is suppressed.
第2図は他の実施例を示し、無端ベルト5には濃縮物を
掻き上げることが可能な掻き上げ羽根5Cが設けられて
おり、この掻き上げ羽根5Cによって容器1の底部1a
にたまる濃縮物を掻き上げ、また無端ベルト5上に蓄積
される濃縮物を取り出すようになっている。無端ベルト
5上の濃縮物はフィルタバッグ19に排出され、このフ
ィルタバッグ19で水分が除去される。この容器1は図
示しない、減圧手段で減圧して減圧状態で写真処理廃液
の蒸発濃縮処理が行なわれる。FIG. 2 shows another embodiment, in which the endless belt 5 is provided with scraping blades 5C capable of scraping up the concentrate, and the scraping blades 5C move the bottom 1a of the container 1.
It scrapes up the concentrate accumulated on the endless belt 5 and takes out the concentrate accumulated on the endless belt 5. The concentrate on the endless belt 5 is discharged into a filter bag 19, where moisture is removed. This container 1 is depressurized by a decompression means (not shown), and the photographic processing waste liquid is evaporated and concentrated under reduced pressure.
第3図はさらに他の実施例を示し、第1図に示す無端ベ
ルト5を写真処理廃液外に配置したもので、この無端ベ
ルト5上に写真処理廃液が循環系の連結バイブ2から供
給されるようになっている。この無端ベルト5上に供給
された写真処理廃液は無端ベルト5の駆動中に濃縮物が
無端ベルト5上に残り、水分は容器1内に落下して分離
され、水分が除去された濃縮物が、掻取部材6で掻き取
られてバッグ7に排出される。FIG. 3 shows still another embodiment, in which the endless belt 5 shown in FIG. 1 is placed outside the photographic processing waste liquid, and the photographic processing waste liquid is supplied onto this endless belt 5 from the connecting vibrator 2 of the circulation system. It has become so. Concentrates of the photographic processing waste liquid supplied onto the endless belt 5 remain on the endless belt 5 while the endless belt 5 is being driven, and water falls into the container 1 and is separated, and the concentrate from which water has been removed is , and is scraped off by the scraping member 6 and discharged into the bag 7.
第4図及び第5図はさらに他の実施例を示し、容器1の
濃縮物取出し部1bに、モータ20で回転する掻上体2
1を設けたものであり、掻上体21には一対の掻上羽根
21aが設けられている。FIGS. 4 and 5 show still another embodiment, in which a scraper 2 rotated by a motor 20 is installed in the concentrate take-out part 1b of the container 1.
1, and the scraping body 21 is provided with a pair of scraping blades 21a.
この掻上体21が回転すると、第5図に示すように、掻
上羽根21aが容器1の底部1aに蓄積されている濃縮
物を掻き上げ、濃縮物取出し部1bに形成されている孔
部22からフィルタバッグ19内に落下させ、濃縮物を
排出する。掻上体21の掻上羽根21aはこの実施例で
は一対設けてぃるが1個でもよく、特に限定されず、ま
た掻上羽根21aを複数設ける場合には等間隔に設ける
ことが好ましい。When the scraping body 21 rotates, the scraping blades 21a scrape up the concentrate accumulated on the bottom 1a of the container 1, as shown in FIG. 22 into the filter bag 19 to discharge the concentrate. Although a pair of scraping blades 21a of the scraping body 21 are provided in this embodiment, it may be one, and there is no particular limitation, and when a plurality of scraping blades 21a are provided, it is preferable to provide them at equal intervals.
この掻上体21の回転は掻上羽根21aの個数や写真処
理廃液の濃度等によって異なり、好ましくは10秒〜3
時間に1回転、より好ましくは1分〜1時間に1回転、
さらに好ましくは3分〜30分に1回転に設定される。The rotation of the scraping body 21 varies depending on the number of scraping blades 21a, the concentration of the photographic processing waste liquid, etc., and is preferably 10 seconds to 3 seconds.
1 rotation per hour, more preferably 1 rotation per minute to 1 hour,
More preferably, the rotation is set to one rotation every 3 to 30 minutes.
[発明の効果]
前記のように、この発明の写真処理廃液の処理装置は、
写真処理廃液を蒸発により濃縮し、沈殿する濃縮物を液
中から直接連続的に取り出すようにしたから、蒸発濃縮
によって生じる濃縮物が蓄積して、過加熱されることが
なくなり、濃縮物の過熱分解を防止して、悪臭の発生を
軽減することができる。[Effects of the Invention] As mentioned above, the photographic processing waste liquid processing apparatus of the present invention has the following features:
Since the photographic processing waste liquid is concentrated by evaporation and the precipitated concentrate is directly and continuously taken out from the liquid, the concentrate produced by evaporative concentration does not accumulate and overheat, and the concentrate is not overheated. It can prevent decomposition and reduce the occurrence of bad odors.
また、濃縮液を収納する容器に、濃縮物を沈殿させ、こ
の沈殿する濃縮物を直接連続的に取り出すようにすると
、多くの濃縮物を容易に取り出すことができる。Moreover, if the concentrate is allowed to settle in a container for storing the concentrate and the precipitated concentrate is directly and continuously taken out, a large amount of the concentrate can be easily taken out.
第1図はこの発明の写真処理廃液の処理装置を示す概略
構成図、342図乃至′s5図は他の実施例を示す概略
構成図である。
図面中符号1は容器、1aは底部、1bは濃縮物取出し
部、2は連結バイブ、3はヒータ、5は無端ベルト、2
1は掻上体である。
飢
C1FIG. 1 is a schematic diagram showing a processing apparatus for photographic processing waste liquid according to the present invention, and FIGS. 342 to 5' are schematic diagrams showing other embodiments. In the drawings, reference numeral 1 is a container, 1a is a bottom, 1b is a concentrate extraction part, 2 is a connecting vibe, 3 is a heater, 5 is an endless belt, 2
1 is the rachis epidermis. Starvation C1
Claims (1)
める写真処理廃液の処理装置において、前記写真処理廃
液を蒸発により濃縮した液中に生じる濃縮物を、濃縮液
中より直接連続的に取り出す手段とを備えることを特徴
とする写真処理廃液の処理装置。 2、前記請求項1記載の写真処理廃液の処理装置におい
て、濃縮液を収納する容器を備え、この容器に沈殿する
濃縮物を直接連続的に取り出す手段を有することを特徴
とする写真処理廃液の処理装置。[Scope of Claims] 1. In a processing device for photographic processing waste liquid, which heats the photographic processing waste liquid with a heating means to evaporate and concentrate the photographic processing waste liquid, the concentrate produced in the liquid obtained by concentrating the photographic processing waste liquid by evaporation is added to the concentrated liquid. 1. A processing apparatus for photographic processing waste liquid, characterized by comprising means for taking it out more directly and continuously. 2. The photographic processing waste liquid processing apparatus according to claim 1, further comprising a container for storing the concentrated liquid, and a means for directly and continuously taking out the concentrated liquid precipitated in the container. Processing equipment.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP63303801A JPH02149396A (en) | 1988-11-30 | 1988-11-30 | Apparatus for treating waste liquid of photographic processing |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP63303801A JPH02149396A (en) | 1988-11-30 | 1988-11-30 | Apparatus for treating waste liquid of photographic processing |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPH02149396A true JPH02149396A (en) | 1990-06-07 |
Family
ID=17925465
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP63303801A Pending JPH02149396A (en) | 1988-11-30 | 1988-11-30 | Apparatus for treating waste liquid of photographic processing |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH02149396A (en) |
-
1988
- 1988-11-30 JP JP63303801A patent/JPH02149396A/en active Pending
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