JPH0330888A - Apparatus for treating waste photographic processing solution - Google Patents
Apparatus for treating waste photographic processing solutionInfo
- Publication number
- JPH0330888A JPH0330888A JP16379589A JP16379589A JPH0330888A JP H0330888 A JPH0330888 A JP H0330888A JP 16379589 A JP16379589 A JP 16379589A JP 16379589 A JP16379589 A JP 16379589A JP H0330888 A JPH0330888 A JP H0330888A
- Authority
- JP
- Japan
- Prior art keywords
- waste liquid
- container
- waste solution
- photographic processing
- condensed water
- 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
- 239000002699 waste material Substances 0.000 title claims abstract description 250
- 238000012545 processing Methods 0.000 title claims description 132
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 76
- 238000005192 partition Methods 0.000 claims abstract description 13
- 239000007788 liquid Substances 0.000 claims description 242
- 238000001704 evaporation Methods 0.000 claims description 50
- 230000008020 evaporation Effects 0.000 claims description 44
- 238000009833 condensation Methods 0.000 claims description 6
- 230000005494 condensation Effects 0.000 claims description 6
- 238000011084 recovery Methods 0.000 abstract description 10
- 239000000463 material Substances 0.000 description 24
- 238000000034 method Methods 0.000 description 17
- 239000000243 solution Substances 0.000 description 16
- 239000003795 chemical substances by application Substances 0.000 description 14
- 150000001875 compounds Chemical class 0.000 description 13
- 238000005406 washing Methods 0.000 description 13
- 239000007789 gas Substances 0.000 description 11
- 239000007844 bleaching agent Substances 0.000 description 9
- 150000003839 salts Chemical class 0.000 description 9
- -1 aromatic primary amine Chemical class 0.000 description 8
- 238000011161 development Methods 0.000 description 8
- 238000005086 pumping Methods 0.000 description 8
- 239000002253 acid Substances 0.000 description 7
- 238000004061 bleaching Methods 0.000 description 7
- 238000005057 refrigeration Methods 0.000 description 7
- LYCAIKOWRPUZTN-UHFFFAOYSA-N Ethylene glycol Chemical compound OCCO LYCAIKOWRPUZTN-UHFFFAOYSA-N 0.000 description 6
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 6
- RAHZWNYVWXNFOC-UHFFFAOYSA-N Sulphur dioxide Chemical compound O=S=O RAHZWNYVWXNFOC-UHFFFAOYSA-N 0.000 description 6
- 238000010438 heat treatment Methods 0.000 description 6
- 230000006641 stabilisation Effects 0.000 description 6
- 238000011105 stabilization Methods 0.000 description 6
- 229940121375 antifungal agent Drugs 0.000 description 5
- 230000017525 heat dissipation Effects 0.000 description 5
- 230000005855 radiation Effects 0.000 description 5
- 230000000087 stabilizing effect Effects 0.000 description 5
- LSNNMFCWUKXFEE-UHFFFAOYSA-N Sulfurous acid Chemical compound OS(O)=O LSNNMFCWUKXFEE-UHFFFAOYSA-N 0.000 description 4
- 150000007513 acids Chemical class 0.000 description 4
- XYXNTHIYBIDHGM-UHFFFAOYSA-N ammonium thiosulfate Chemical compound [NH4+].[NH4+].[O-]S([O-])(=O)=S XYXNTHIYBIDHGM-UHFFFAOYSA-N 0.000 description 4
- 230000000694 effects Effects 0.000 description 4
- 238000011160 research Methods 0.000 description 4
- 229910052709 silver Inorganic materials 0.000 description 4
- 239000004332 silver Substances 0.000 description 4
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 3
- CPELXLSAUQHCOX-UHFFFAOYSA-M Bromide Chemical compound [Br-] CPELXLSAUQHCOX-UHFFFAOYSA-M 0.000 description 3
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 description 3
- 230000000844 anti-bacterial effect Effects 0.000 description 3
- 239000003429 antifungal agent Substances 0.000 description 3
- 239000002585 base Substances 0.000 description 3
- KRKNYBCHXYNGOX-UHFFFAOYSA-N citric acid Chemical class OC(=O)CC(O)(C(O)=O)CC(O)=O KRKNYBCHXYNGOX-UHFFFAOYSA-N 0.000 description 3
- 229910017052 cobalt Inorganic materials 0.000 description 3
- 239000010941 cobalt Substances 0.000 description 3
- GUTLYIVDDKVIGB-UHFFFAOYSA-N cobalt atom Chemical compound [Co] GUTLYIVDDKVIGB-UHFFFAOYSA-N 0.000 description 3
- 238000001816 cooling Methods 0.000 description 3
- 230000007423 decrease Effects 0.000 description 3
- MTHSVFCYNBDYFN-UHFFFAOYSA-N diethylene glycol Chemical compound OCCOCCO MTHSVFCYNBDYFN-UHFFFAOYSA-N 0.000 description 3
- 238000005516 engineering process Methods 0.000 description 3
- 229910000037 hydrogen sulfide Inorganic materials 0.000 description 3
- 150000004694 iodide salts Chemical class 0.000 description 3
- 229910052742 iron Inorganic materials 0.000 description 3
- IMNIMPAHZVJRPE-UHFFFAOYSA-N triethylenediamine Chemical compound C1CN2CCN1CC2 IMNIMPAHZVJRPE-UHFFFAOYSA-N 0.000 description 3
- RNMCCPMYXUKHAZ-UHFFFAOYSA-N 2-[3,3-diamino-1,2,2-tris(carboxymethyl)cyclohexyl]acetic acid Chemical compound NC1(N)CCCC(CC(O)=O)(CC(O)=O)C1(CC(O)=O)CC(O)=O RNMCCPMYXUKHAZ-UHFFFAOYSA-N 0.000 description 2
- CDAWCLOXVUBKRW-UHFFFAOYSA-N 2-aminophenol Chemical class NC1=CC=CC=C1O CDAWCLOXVUBKRW-UHFFFAOYSA-N 0.000 description 2
- KCXVZYZYPLLWCC-UHFFFAOYSA-N EDTA Chemical compound OC(=O)CN(CC(O)=O)CCN(CC(O)=O)CC(O)=O KCXVZYZYPLLWCC-UHFFFAOYSA-N 0.000 description 2
- WSFSSNUMVMOOMR-UHFFFAOYSA-N Formaldehyde Chemical compound O=C WSFSSNUMVMOOMR-UHFFFAOYSA-N 0.000 description 2
- MHAJPDPJQMAIIY-UHFFFAOYSA-N Hydrogen peroxide Chemical compound OO MHAJPDPJQMAIIY-UHFFFAOYSA-N 0.000 description 2
- QIGBRXMKCJKVMJ-UHFFFAOYSA-N Hydroquinone Chemical compound OC1=CC=C(O)C=C1 QIGBRXMKCJKVMJ-UHFFFAOYSA-N 0.000 description 2
- QPCDCPDFJACHGM-UHFFFAOYSA-N N,N-bis{2-[bis(carboxymethyl)amino]ethyl}glycine Chemical compound OC(=O)CN(CC(O)=O)CCN(CC(=O)O)CCN(CC(O)=O)CC(O)=O QPCDCPDFJACHGM-UHFFFAOYSA-N 0.000 description 2
- 239000003242 anti bacterial agent Substances 0.000 description 2
- 230000000843 anti-fungal effect Effects 0.000 description 2
- 239000002738 chelating agent Substances 0.000 description 2
- 238000000605 extraction Methods 0.000 description 2
- 239000003112 inhibitor Substances 0.000 description 2
- 238000011068 loading method Methods 0.000 description 2
- 238000012423 maintenance Methods 0.000 description 2
- 229910052751 metal Inorganic materials 0.000 description 2
- 239000002184 metal Substances 0.000 description 2
- 238000012986 modification Methods 0.000 description 2
- 230000004048 modification Effects 0.000 description 2
- 229960003330 pentetic acid Drugs 0.000 description 2
- JRKICGRDRMAZLK-UHFFFAOYSA-L persulfate group Chemical group S(=O)(=O)([O-])OOS(=O)(=O)[O-] JRKICGRDRMAZLK-UHFFFAOYSA-L 0.000 description 2
- 239000000088 plastic resin Substances 0.000 description 2
- 239000002244 precipitate Substances 0.000 description 2
- 239000003755 preservative agent Substances 0.000 description 2
- 230000001737 promoting effect Effects 0.000 description 2
- 239000002689 soil Substances 0.000 description 2
- 125000003396 thiol group Chemical group [H]S* 0.000 description 2
- 150000004764 thiosulfuric acid derivatives Chemical class 0.000 description 2
- BJEPYKJPYRNKOW-REOHCLBHSA-N (S)-malic acid Chemical class OC(=O)[C@@H](O)CC(O)=O BJEPYKJPYRNKOW-REOHCLBHSA-N 0.000 description 1
- JLHMJWHSBYZWJJ-UHFFFAOYSA-N 1,2-thiazole 1-oxide Chemical class O=S1C=CC=N1 JLHMJWHSBYZWJJ-UHFFFAOYSA-N 0.000 description 1
- VZYDKJOUEPFKMW-UHFFFAOYSA-N 2,3-dihydroxybenzenesulfonic acid Chemical class OC1=CC=CC(S(O)(=O)=O)=C1O VZYDKJOUEPFKMW-UHFFFAOYSA-N 0.000 description 1
- QTLHLXYADXCVCF-UHFFFAOYSA-N 2-(4-amino-n-ethyl-3-methylanilino)ethanol Chemical compound OCCN(CC)C1=CC=C(N)C(C)=C1 QTLHLXYADXCVCF-UHFFFAOYSA-N 0.000 description 1
- JVXHQHGWBAHSSF-UHFFFAOYSA-L 2-[2-[bis(carboxylatomethyl)amino]ethyl-(carboxylatomethyl)amino]acetate;hydron;iron(2+) Chemical compound [H+].[H+].[Fe+2].[O-]C(=O)CN(CC([O-])=O)CCN(CC([O-])=O)CC([O-])=O JVXHQHGWBAHSSF-UHFFFAOYSA-L 0.000 description 1
- XWSGEVNYFYKXCP-UHFFFAOYSA-N 2-[carboxymethyl(methyl)amino]acetic acid Chemical compound OC(=O)CN(C)CC(O)=O XWSGEVNYFYKXCP-UHFFFAOYSA-N 0.000 description 1
- ZFIQGRISGKSVAG-UHFFFAOYSA-N 4-methylaminophenol Chemical compound CNC1=CC=C(O)C=C1 ZFIQGRISGKSVAG-UHFFFAOYSA-N 0.000 description 1
- XBTWVJKPQPQTDW-UHFFFAOYSA-N 4-n,4-n-diethyl-2-methylbenzene-1,4-diamine Chemical compound CCN(CC)C1=CC=C(N)C(C)=C1 XBTWVJKPQPQTDW-UHFFFAOYSA-N 0.000 description 1
- FFAJEKUNEVVYCW-UHFFFAOYSA-N 4-n-ethyl-4-n-(2-methoxyethyl)-2-methylbenzene-1,4-diamine Chemical compound COCCN(CC)C1=CC=C(N)C(C)=C1 FFAJEKUNEVVYCW-UHFFFAOYSA-N 0.000 description 1
- 241000894006 Bacteria Species 0.000 description 1
- 241000283690 Bos taurus Species 0.000 description 1
- BHPQYMZQTOCNFJ-UHFFFAOYSA-N Calcium cation Chemical compound [Ca+2] BHPQYMZQTOCNFJ-UHFFFAOYSA-N 0.000 description 1
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 description 1
- VYZAMTAEIAYCRO-UHFFFAOYSA-N Chromium Chemical compound [Cr] VYZAMTAEIAYCRO-UHFFFAOYSA-N 0.000 description 1
- JPVYNHNXODAKFH-UHFFFAOYSA-N Cu2+ Chemical compound [Cu+2] JPVYNHNXODAKFH-UHFFFAOYSA-N 0.000 description 1
- FEWJPZIEWOKRBE-JCYAYHJZSA-N Dextrotartaric acid Chemical class OC(=O)[C@H](O)[C@@H](O)C(O)=O FEWJPZIEWOKRBE-JCYAYHJZSA-N 0.000 description 1
- 229920001174 Diethylhydroxylamine Polymers 0.000 description 1
- DBVJJBKOTRCVKF-UHFFFAOYSA-N Etidronic acid Chemical compound OP(=O)(O)C(O)(C)P(O)(O)=O DBVJJBKOTRCVKF-UHFFFAOYSA-N 0.000 description 1
- AVXURJPOCDRRFD-UHFFFAOYSA-N Hydroxylamine Chemical compound ON AVXURJPOCDRRFD-UHFFFAOYSA-N 0.000 description 1
- JLVVSXFLKOJNIY-UHFFFAOYSA-N Magnesium ion Chemical compound [Mg+2] JLVVSXFLKOJNIY-UHFFFAOYSA-N 0.000 description 1
- JYXGIOKAKDAARW-UHFFFAOYSA-N N-(2-hydroxyethyl)iminodiacetic acid Chemical compound OCCN(CC(O)=O)CC(O)=O JYXGIOKAKDAARW-UHFFFAOYSA-N 0.000 description 1
- 229910019142 PO4 Inorganic materials 0.000 description 1
- AVKHCKXGKPAGEI-UHFFFAOYSA-N Phenicarbazide Chemical class NC(=O)NNC1=CC=CC=C1 AVKHCKXGKPAGEI-UHFFFAOYSA-N 0.000 description 1
- 229920003171 Poly (ethylene oxide) Polymers 0.000 description 1
- 239000002202 Polyethylene glycol Substances 0.000 description 1
- BQCADISMDOOEFD-UHFFFAOYSA-N Silver Chemical compound [Ag] BQCADISMDOOEFD-UHFFFAOYSA-N 0.000 description 1
- FEWJPZIEWOKRBE-UHFFFAOYSA-N Tartaric acid Chemical class [H+].[H+].[O-]C(=O)C(O)C(O)C([O-])=O FEWJPZIEWOKRBE-UHFFFAOYSA-N 0.000 description 1
- GSEJCLTVZPLZKY-UHFFFAOYSA-N Triethanolamine Chemical compound OCCN(CCO)CCO GSEJCLTVZPLZKY-UHFFFAOYSA-N 0.000 description 1
- WZGNVVUXVXNNOX-UHFFFAOYSA-N [Fe+] Chemical compound [Fe+] WZGNVVUXVXNNOX-UHFFFAOYSA-N 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- 238000009825 accumulation Methods 0.000 description 1
- MKBUQYWFFBCMFG-UHFFFAOYSA-N acetic acid propane-1,1-diamine Chemical compound CC(O)=O.CC(O)=O.CC(O)=O.CC(O)=O.CCC(N)N MKBUQYWFFBCMFG-UHFFFAOYSA-N 0.000 description 1
- 230000002411 adverse Effects 0.000 description 1
- 229910000288 alkali metal carbonate Inorganic materials 0.000 description 1
- 150000008041 alkali metal carbonates Chemical class 0.000 description 1
- BJEPYKJPYRNKOW-UHFFFAOYSA-N alpha-hydroxysuccinic acid Chemical class OC(=O)C(O)CC(O)=O BJEPYKJPYRNKOW-UHFFFAOYSA-N 0.000 description 1
- 150000001412 amines Chemical class 0.000 description 1
- 239000007864 aqueous solution Substances 0.000 description 1
- 239000012298 atmosphere Substances 0.000 description 1
- 150000001556 benzimidazoles Chemical class 0.000 description 1
- IOJUPLGTWVMSFF-UHFFFAOYSA-N benzothiazole Chemical class C1=CC=C2SC=NC2=C1 IOJUPLGTWVMSFF-UHFFFAOYSA-N 0.000 description 1
- QRUDEWIWKLJBPS-UHFFFAOYSA-N benzotriazole Chemical compound C1=CC=C2N[N][N]C2=C1 QRUDEWIWKLJBPS-UHFFFAOYSA-N 0.000 description 1
- 239000012964 benzotriazole Substances 0.000 description 1
- MOOAHMCRPCTRLV-UHFFFAOYSA-N boron sodium Chemical compound [B].[Na] MOOAHMCRPCTRLV-UHFFFAOYSA-N 0.000 description 1
- 150000001642 boronic acid derivatives Chemical class 0.000 description 1
- SXDBWCPKPHAZSM-UHFFFAOYSA-M bromate Chemical class [O-]Br(=O)=O SXDBWCPKPHAZSM-UHFFFAOYSA-M 0.000 description 1
- 229940006460 bromide ion Drugs 0.000 description 1
- 150000003842 bromide salts Chemical class 0.000 description 1
- 239000000872 buffer Substances 0.000 description 1
- 229910001424 calcium ion Inorganic materials 0.000 description 1
- 239000000460 chlorine Substances 0.000 description 1
- 229910052801 chlorine Inorganic materials 0.000 description 1
- 229910052804 chromium Inorganic materials 0.000 description 1
- 239000011651 chromium Substances 0.000 description 1
- 235000015165 citric acid Nutrition 0.000 description 1
- 238000004140 cleaning Methods 0.000 description 1
- 230000002860 competitive effect Effects 0.000 description 1
- 235000008504 concentrate Nutrition 0.000 description 1
- 239000012141 concentrate Substances 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 239000002781 deodorant agent Substances 0.000 description 1
- 239000000645 desinfectant Substances 0.000 description 1
- SOCTUWSJJQCPFX-UHFFFAOYSA-N dichromate(2-) Chemical compound [O-][Cr](=O)(=O)O[Cr]([O-])(=O)=O SOCTUWSJJQCPFX-UHFFFAOYSA-N 0.000 description 1
- FVCOIAYSJZGECG-UHFFFAOYSA-N diethylhydroxylamine Chemical compound CCN(O)CC FVCOIAYSJZGECG-UHFFFAOYSA-N 0.000 description 1
- 150000005205 dihydroxybenzenes Chemical class 0.000 description 1
- 125000002228 disulfide group Chemical group 0.000 description 1
- SRPOMGSPELCIGZ-UHFFFAOYSA-N disulfino carbonate Chemical class OS(=O)OC(=O)OS(O)=O SRPOMGSPELCIGZ-UHFFFAOYSA-N 0.000 description 1
- 239000000839 emulsion Substances 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- DEFVIWRASFVYLL-UHFFFAOYSA-N ethylene glycol bis(2-aminoethyl)tetraacetic acid Chemical compound OC(=O)CN(CC(O)=O)CCOCCOCCN(CC(O)=O)CC(O)=O DEFVIWRASFVYLL-UHFFFAOYSA-N 0.000 description 1
- YAGKRVSRTSUGEY-UHFFFAOYSA-N ferricyanide Chemical compound [Fe+3].N#[C-].N#[C-].N#[C-].N#[C-].N#[C-].N#[C-] YAGKRVSRTSUGEY-UHFFFAOYSA-N 0.000 description 1
- 238000011010 flushing procedure Methods 0.000 description 1
- 239000000417 fungicide Substances 0.000 description 1
- 239000003365 glass fiber Substances 0.000 description 1
- WUWHPEZEVZLKEJ-UHFFFAOYSA-N hydrazine;sulfurous acid Chemical class NN.OS(O)=O WUWHPEZEVZLKEJ-UHFFFAOYSA-N 0.000 description 1
- 150000003840 hydrochlorides Chemical class 0.000 description 1
- 238000009434 installation Methods 0.000 description 1
- 150000002505 iron Chemical class 0.000 description 1
- 235000014666 liquid concentrate Nutrition 0.000 description 1
- 229910001425 magnesium ion Inorganic materials 0.000 description 1
- 239000001630 malic acid Chemical class 0.000 description 1
- 235000011090 malic acid Nutrition 0.000 description 1
- 150000002739 metals Chemical class 0.000 description 1
- 244000005700 microbiome Species 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- NPKFETRYYSUTEC-UHFFFAOYSA-N n-[2-(4-amino-n-ethyl-3-methylanilino)ethyl]methanesulfonamide Chemical compound CS(=O)(=O)NCCN(CC)C1=CC=C(N)C(C)=C1 NPKFETRYYSUTEC-UHFFFAOYSA-N 0.000 description 1
- MGFYIUFZLHCRTH-UHFFFAOYSA-N nitrilotriacetic acid Chemical compound OC(=O)CN(CC(O)=O)CC(O)=O MGFYIUFZLHCRTH-UHFFFAOYSA-N 0.000 description 1
- 150000002828 nitro derivatives Chemical class 0.000 description 1
- 150000005181 nitrobenzenes Chemical class 0.000 description 1
- 239000003960 organic solvent Substances 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 150000004989 p-phenylenediamines Chemical class 0.000 description 1
- 238000010979 pH adjustment Methods 0.000 description 1
- 150000004965 peroxy acids Chemical class 0.000 description 1
- CMCWWLVWPDLCRM-UHFFFAOYSA-N phenidone Chemical compound N1C(=O)CCN1C1=CC=CC=C1 CMCWWLVWPDLCRM-UHFFFAOYSA-N 0.000 description 1
- WVDDGKGOMKODPV-ZQBYOMGUSA-N phenyl(114C)methanol Chemical compound O[14CH2]C1=CC=CC=C1 WVDDGKGOMKODPV-ZQBYOMGUSA-N 0.000 description 1
- 235000021317 phosphate Nutrition 0.000 description 1
- ZJAOAACCNHFJAH-UHFFFAOYSA-N phosphonoformic acid Chemical class OC(=O)P(O)(O)=O ZJAOAACCNHFJAH-UHFFFAOYSA-N 0.000 description 1
- 150000003013 phosphoric acid derivatives Chemical class 0.000 description 1
- 229920000768 polyamine Polymers 0.000 description 1
- 229920001223 polyethylene glycol Polymers 0.000 description 1
- 239000002243 precursor Substances 0.000 description 1
- 230000002265 prevention Effects 0.000 description 1
- NDGRWYRVNANFNB-UHFFFAOYSA-N pyrazolidin-3-one Chemical class O=C1CCNN1 NDGRWYRVNANFNB-UHFFFAOYSA-N 0.000 description 1
- 150000003242 quaternary ammonium salts Chemical class 0.000 description 1
- 150000004053 quinones Chemical class 0.000 description 1
- 239000003507 refrigerant Substances 0.000 description 1
- 239000010865 sewage Substances 0.000 description 1
- QHFDHWJHIAVELW-UHFFFAOYSA-M sodium;4,6-dioxo-1h-1,3,5-triazin-2-olate Chemical class [Na+].[O-]C1=NC(=O)NC(=O)N1 QHFDHWJHIAVELW-UHFFFAOYSA-M 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 125000006850 spacer group Chemical group 0.000 description 1
- 238000004659 sterilization and disinfection Methods 0.000 description 1
- 150000003455 sulfinic acids Chemical class 0.000 description 1
- LSNNMFCWUKXFEE-UHFFFAOYSA-L sulfite Chemical class [O-]S([O-])=O LSNNMFCWUKXFEE-UHFFFAOYSA-L 0.000 description 1
- 150000003467 sulfuric acid derivatives Chemical class 0.000 description 1
- 239000013589 supplement Substances 0.000 description 1
- 239000004094 surface-active agent Substances 0.000 description 1
- 239000011975 tartaric acid Chemical class 0.000 description 1
- 235000002906 tartaric acid Nutrition 0.000 description 1
- 235000010296 thiabendazole Nutrition 0.000 description 1
- 150000003567 thiocyanates Chemical class 0.000 description 1
- 150000003568 thioethers Chemical class 0.000 description 1
- 150000003585 thioureas Chemical class 0.000 description 1
- JOXIMZWYDAKGHI-UHFFFAOYSA-N toluene-4-sulfonic acid Chemical class CC1=CC=C(S(O)(=O)=O)C=C1 JOXIMZWYDAKGHI-UHFFFAOYSA-N 0.000 description 1
- 150000003672 ureas Chemical class 0.000 description 1
- 150000003673 urethanes Chemical class 0.000 description 1
- 230000002747 voluntary effect Effects 0.000 description 1
Landscapes
- Heat Treatment Of Water, Waste Water Or Sewage (AREA)
- 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〕
本発明は写真の現像処理廃液を濃縮するために用いられ
る写真処理廃液処理装置に関する。DETAILED DESCRIPTION OF THE INVENTION [Field of Industrial Application] The present invention relates to a photographic processing waste liquid processing apparatus used for concentrating photographic processing waste liquid.
写真の現像処理によってもたらされた廃液は、公害防止
の点から河川等に廃棄することができないため、専門業
者に処理を依頼しているのが実情である。写真処理廃液
は大部分が水であるので、写真処理廃液を濃縮又は固化
すれば、保管量は極めて少量でもよいことになり、保管
のスペース及びその後の処理も簡単になり、専門業者へ
の委託経費も大幅に削減される。The waste liquid produced by photographic processing cannot be disposed of in rivers or the like to prevent pollution, so the actual situation is that the waste liquid produced by photographic processing must be disposed of by specialized companies. Most of the photographic processing waste liquid is water, so if the photographic processing waste liquid is concentrated or solidified, the storage amount can be kept in a very small amount, which simplifies storage space and subsequent processing, making it easier to outsource to specialized companies. Expenses will also be significantly reduced.
そのための装置として、写真処理廃液中に含まれている
固形分を水分と分離する写真処理廃液処理装置がある。As an apparatus for this purpose, there is a photographic processing waste liquid processing apparatus that separates solid content contained in the photographic processing waste liquid from water.
写真処理廃液処理装置としては、吸気口と排気口を備え
た本体ケースの中に、廃液を溜める貯液手段と、廃液の
加熱蒸発手段と、蒸発手段に廃液を供給する手段と、上
記廃液を凝縮する熱交換手段及び/又は熱交換手段を通
して加熱蒸発手段に空気を送る手段とを有する装置であ
った。(特開昭63−19655号、特開昭63−10
7795号各公報参照)
しかしながら、従来の装置は廃液の加熱蒸発の際に、6
0〜90℃に廃液温度を上昇させて蒸発を促進させるこ
とにより、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が高温のた
めに分解し、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。そして、
これらのガスが本体ケースの排気口より装置外に放出さ
れると、装置周囲の雰囲気を汚染してしまうので、この
問題を解決するために、凝結水の濾過装置、排ガス吸着
装置、濃縮液排出機構、消臭剤供給手段、固化剤供給手
段等の2次処理装置を必要とし、装置全体が非常に複雑
な大きな装置となり、運転操作も複雑であった。The photographic processing waste liquid processing apparatus has a main body case equipped with an intake port and an exhaust port, and includes a storage means for storing the waste liquid, a heating evaporation means for the waste liquid, a means for supplying the waste liquid to the evaporation means, and a means for supplying the waste liquid to the evaporation means. It was an apparatus having a heat exchange means for condensing and/or a means for sending air through the heat exchange means to a heating evaporation means. (JP-A No. 63-19655, JP-A No. 63-10
(Refer to each publication No. 7795) However, in the conventional device, when heating and evaporating the waste liquid, the
By increasing the waste liquid temperature to 0 to 90°C to promote evaporation, ammonium thiosulfate and sulfite, which are commonly used as fixing solutions and bleach-fixing solutions for photographic processing solutions, decompose due to the high temperature, producing sulfur dioxide gas and hydrogen sulfide. , harmful or extremely foul-smelling gases such as ammonia gas are generated. and,
If these gases are released outside the device from the exhaust port on the main body case, they will contaminate the atmosphere around the device. It requires secondary processing equipment such as a mechanism, a deodorant supply means, a solidifying agent supply means, etc., and the entire apparatus becomes a very complicated and large apparatus, and its operation is also complicated.
更に、蒸発効率を高めるために、大型の蒸発手段を備え
るので、装置が大型化するとともに、消費電力も増大す
る。Furthermore, in order to improve evaporation efficiency, a large evaporation means is provided, which increases the size of the device and increases power consumption.
また、本体内の温度や湿度が変化して、回収した水分の
pHやCOD等の処理品質や処理能力が変化するという
問題がある。Furthermore, there is a problem in that the temperature and humidity inside the main body change, and the processing quality and processing capacity of the collected water, such as pH and COD, change.
上記問題点を解消し、2次処理装置を必要とせず、小型
かつ処理効率の高い写真処理廃液処理装置として、本体
ケース内で、写真処理廃液に一部浸漬した蒸発媒体に廃
液を付着又は含浸し、廃液を空気にさらして蒸発させる
蒸発部と、蒸発した水分を冷却して凝縮させる凝縮部と
を有する写真処理廃液処理装置が提案されている。Solving the above problems, the waste liquid is attached to or impregnated into the evaporation medium that is partially immersed in the photographic processing waste liquid inside the main body case as a small and highly efficient photographic processing waste liquid treatment device that does not require a secondary processing device. However, a photographic processing waste liquid processing apparatus has been proposed that has an evaporation section that exposes the waste liquid to air and evaporates it, and a condensation section that cools and condenses the evaporated water.
写真処理廃液を蒸発、凝縮する写真処理廃液処理装置は
、蒸発部へ供給する廃液を収容する廃液収容手段と、凝
縮した水分を回収して収容する凝縮水収容手段とがそれ
ぞれ必要である。したがって、各収容手段を写真処理廃
液処理装置に対して装脱する操作煩雑であり、しかも上
記構成は写真処理廃液処理装置を大型化する要因となっ
ている。A photographic processing waste liquid processing apparatus that evaporates and condenses photographic processing waste liquid requires a waste liquid storage means for storing the waste liquid to be supplied to the evaporator, and a condensed water storage means for recovering and storing condensed water. Therefore, the operation of loading and unloading each storage means into the photographic processing waste liquid processing apparatus is complicated, and the above-mentioned configuration is also a factor in increasing the size of the photographic processing waste liquid processing apparatus.
本発明の目的は上記問題点を解消することにあり、廃液
の供給、凝縮水、濃縮廃液の回収が容易で、操作性に優
れた写真処理廃液処理装置を提供することにある。SUMMARY OF THE INVENTION An object of the present invention is to solve the above-mentioned problems, and to provide a photographic processing waste liquid treatment apparatus that is easy to supply waste liquid, recover condensed water, and concentrated waste liquid, and has excellent operability.
〔課題を解決するための手段及び作用〕本発明の上記目
的は、写真処理廃液中の水分を蒸発させ、蒸発した水分
を凝縮して回収する写真処理廃液処理装置において、写
真処理廃液、凝縮水、a縮廃液の少なくとも2種の液を
それぞれ収容可能に、可撓性隔壁により分割した複数の
収容部を有する容器と、第1収容部に収容される廃液を
蒸発部に供給する廃液供給手段と、凝縮部により凝縮さ
れた水分及び濃縮廃液の少なくとも一方を第2収容部へ
回収する回収手段とを備えた写真処理廃液処理装置によ
って達成される。[Means and effects for solving the problems] The above-mentioned object of the present invention is to provide a photographic processing waste liquid processing apparatus that evaporates water in photographic processing waste liquid and condenses and recovers the evaporated water. , a container having a plurality of storage sections divided by flexible partitions so as to be able to accommodate at least two types of waste liquids, respectively; and a waste liquid supply means for supplying the waste liquid contained in the first storage section to the evaporation section. This is achieved by a photographic processing waste liquid processing apparatus comprising: and a recovery means for recovering at least one of the moisture condensed by the condensation section and the concentrated waste liquid to the second storage section.
すなわち、可撓性隔壁により分割した複数の収容部を有
する容器に、廃液、凝縮水及び濃縮廃液をそれぞれ独立
に収容することにより、1つの容器にすべての液を収容
することもできる。したがって、蒸発部への廃液供給、
凝縮部からのI種水回収、濃縮廃液の回収とを同時に行
い、廃液供給後に容器を交換することにより、凝縮水及
び濃縮廃液の回収が容易になる。That is, by storing the waste liquid, condensed water, and concentrated waste liquid independently in a container having a plurality of storage parts divided by a flexible partition, all the liquids can be stored in one container. Therefore, the waste liquid supply to the evaporation section,
By performing the collection of type I water from the condensation section and the concentrated waste liquid at the same time, and replacing the container after the waste liquid is supplied, the condensed water and the concentrated waste liquid can be easily collected.
また、1つの容器に、廃液と凝縮水、又は廃液と濃縮廃
液のように2種の液を収容することができるので、廃液
供給と凝縮水又は濃縮廃液の回収が容易になる。Moreover, since two types of liquids, such as a waste liquid and condensed water, or a waste liquid and a concentrated waste liquid, can be stored in one container, it becomes easy to supply the waste liquid and recover the condensed water or the concentrated waste liquid.
なお、本発明における濃縮廃液は廃液中の残渣をも含む
。Note that the concentrated waste liquid in the present invention also includes residues in the waste liquid.
本発明における容器は、可撓性隔壁により内部を複数に
分割されており、容器の全容積分の廃液を収容すること
ができる。このとき、凝縮水及び濃縮廃液の収容容積は
ほぼゼロに等しい。そして、容器内の廃液を蒸発部に供
給するに従って廃液収容容積が減って行き、逆に凝縮水
及びa縮廃液の収容容積が増えて行く。The container according to the present invention is internally divided into a plurality of parts by a flexible partition wall, and can contain the entire volume of waste liquid of the container. At this time, the capacity of the condensed water and concentrated waste liquid is approximately equal to zero. Then, as the waste liquid in the container is supplied to the evaporator, the waste liquid storage volume decreases, and conversely, the storage capacity of the condensed water and the a-condensed waste liquid increases.
したがって、廃液を収容していた容器に凝縮水及び濃縮
廃液を案内して回収することにより、廃液の供給、凝縮
水及び濃縮廃液の回収に伴う容器の装脱が1回で済み、
凝縮水及び濃縮廃液の回収を容易に行うことができる。Therefore, by guiding and collecting the condensed water and concentrated waste liquid into the container that contained the waste liquid, only one time is required to supply the waste liquid and to load and unload the container in conjunction with the collection of the condensed water and concentrated waste liquid.
Condensed water and concentrated waste liquid can be easily recovered.
また、廃液を収容していた容器内に凝縮水及び濃縮廃液
を収容するので、1つの容器を廃液供給及び凝縮水回収
に兼用でき、写真処理廃液処理装置内での容器収納領域
を低減できる。したがって、写真処理廃液処理装置を小
型化することができる。Furthermore, since the condensed water and concentrated waste liquid are stored in the container that previously contained the waste liquid, one container can be used both for supplying the waste liquid and collecting the condensed water, and the container storage area within the photographic processing waste liquid processing apparatus can be reduced. Therefore, the photographic processing waste liquid treatment apparatus can be downsized.
更に、写真処理廃液処理装置を小型に構成できるので、
自動現像装置と一体化もしくは自動現像装置に内蔵する
ことも可能になる。Furthermore, since the photographic processing waste liquid treatment device can be configured in a small size,
It also becomes possible to integrate it with an automatic developing device or to incorporate it into the automatic developing device.
なお、本発明における写真処理廃液処理装置の本体ケー
スは実質的に密閉していてもよく、また外部に対して開
放していてもよい。この場合、実質的に密閉した本体ケ
ースとは、本体ケースに写真処理廃液を供給する場合、
凝縮水を本体ケースから取り出す場合など以外は、本体
ケース内の空気、場合によっては悪臭性の空気が外へ漏
失しない程度に、外界と分離されているものを意味する
。The main body case of the photographic processing waste liquid processing apparatus according to the present invention may be substantially sealed, or may be open to the outside. In this case, a substantially sealed main body case means that when photographic processing waste liquid is supplied to the main body case,
This means that the air inside the main case, and in some cases malodorous air, is separated from the outside world to the extent that it does not leak outside, except when removing condensed water from the main case.
本体ケースを実質的に密閉構成とすることにより、廃液
中から蒸発した水分又はガスが外部に放散することがな
゛いので、写真処理廃液処理装置外に悪影響を及ぼすこ
とはない。By making the main body case substantially airtight, moisture or gas evaporated from the waste liquid will not be diffused to the outside, so that it will not have an adverse effect on the outside of the photographic processing waste liquid processing apparatus.
本写真処理廃液処理装置に得られた凝縮水は必要に応じ
て簡単な処理(例えばpH調整)を行った後、下水へ流
すこともできる。The condensed water obtained by this photographic processing waste liquid treatment apparatus can be subjected to simple treatment (for example, pH adjustment) if necessary, and then drained to the sewer.
また、本写真処理廃液処理装置で得られた濃縮された写
真処理廃液は回収して加熱焼却することができる。濃縮
廃液を廃液槽から抜き取る場合には、廃液槽の底に設け
られた栓をあけることにより、容易に抜き取ることがで
きる。濃縮廃液を抜き取る際には、運搬性、抜取後の取
扱性の向上のために、同化剤を用いて濃縮廃液を固化す
ることができる。同化剤として用いられるものは、詳し
くは特願平1−96435、同1−96436号明細書
、特開昭61−231548号公報に記載されている。Further, the concentrated photographic processing waste liquid obtained by the present photographic processing waste liquid processing apparatus can be recovered and heated and incinerated. When the concentrated waste liquid is removed from the waste liquid tank, it can be easily removed by opening a stopper provided at the bottom of the waste liquid tank. When extracting the concentrated waste liquid, an assimilating agent can be used to solidify the concentrated waste liquid in order to improve transportability and ease of handling after extraction. Those used as assimilating agents are described in detail in Japanese Patent Applications Hei 1-96435 and Hei 1-96436, and Japanese Patent Application Laid-Open No. 61-231548.
また、本発明における写真処理廃液とは、現像(カラー
、黒白)、漂白、漂白定着、安定等の写真処理を行った
後の廃液であればいかなる廃液であってもよい。Further, the photographic processing waste liquid in the present invention may be any waste liquid after performing photographic processing such as development (color, black and white), bleaching, bleach-fixing, stabilization, etc.
本発明の一実施例を図を用いて説明する。但し本発明は
本実施例のみに限定されるものではない。An embodiment of the present invention will be described with reference to the drawings. However, the present invention is not limited to this example.
第1図は本発明の写真処理廃液処理装置の第1実施例の
概略側面図である。FIG. 1 is a schematic side view of a first embodiment of the photographic processing waste liquid treatment apparatus of the present invention.
写真処理廃液処理装置の密閉した本体ケース2の中に、
写真処理廃液を収容する廃液槽3が本体ケースより取出
し可能に据付けられている。廃液槽3への廃液の補充は
配管31とポンプ32によって容器33から行える。廃
液槽3内の廃液のレベルコントロールは別に行えるよう
になっている(図示せず)。Inside the sealed body case 2 of the photographic processing waste liquid treatment device,
A waste liquid tank 3 containing photographic processing waste liquid is installed so as to be removable from the main body case. The waste liquid tank 3 can be replenished with waste liquid from a container 33 using a pipe 31 and a pump 32. The level of waste liquid in the waste liquid tank 3 can be controlled separately (not shown).
本実施例は本体ケース2を実質的に密閉した構成である
が、本発明は本体ケースを非密閉に構成した写真処理廃
液処理装置にも適用することができる。その場合、廃液
から発生する有害又は悪臭性のガスを処理するための2
次処理装置を設けて、有害又は悪臭性のガスが写真処理
廃液処理装置外に放散されないようにする。Although this embodiment has a structure in which the main body case 2 is substantially sealed, the present invention can also be applied to a photographic processing waste liquid processing apparatus in which the main body case is non-sealed. In that case, 2.
A subsequent treatment device is provided to prevent harmful or malodorous gases from being released outside the photographic processing waste liquid treatment device.
蒸発媒体としてのエンドレスベルト4は、グラスファイ
バーより作られたメツシュ構造で、その蒸発面を循環風
に対して直角にして回転移動する。The endless belt 4 as an evaporation medium has a mesh structure made of glass fiber and rotates with its evaporation surface perpendicular to the circulating air.
そして、エンドレスベルト4は下部を廃液槽3内の廃液
に浸漬され、回転により廃液を汲み上げている。The lower part of the endless belt 4 is immersed in the waste liquid in the waste liquid tank 3, and the waste liquid is pumped up by rotation.
本実施例においては、2つのエンドレスベルト4をそれ
ぞれ独立に設けて駆動しているが、複数のエンドレスベ
ルト4をスペーサを介して重畳して駆動することにより
、蒸発効率を変えずにエンドレスベルト4の設置領域を
低減することができる。In this embodiment, two endless belts 4 are provided and driven independently, but by driving a plurality of endless belts 4 in a superimposed manner via a spacer, the endless belts 4 can be driven without changing the evaporation efficiency. The installation area can be reduced.
エンドレスベルト4により汲み上げられた廃液は蒸発し
、蒸発した水分が空気中に含まれる。The waste liquid pumped up by the endless belt 4 evaporates, and the evaporated moisture is contained in the air.
本装置に備える冷凍装置は、冷却器8、第1放熱部11
、第2放熱部72、圧′ls機71、膨張弁73を有し
、これらに冷媒を循環させる構成である。The refrigeration device included in this device includes a cooler 8, a first heat radiation section 11
, a second heat radiating section 72, a pressure unit 71, and an expansion valve 73, and is configured to circulate refrigerant through these.
蒸発した水分を充分含んだ循環空気は、冷凍装置の冷却
器(凝縮器)8によって露点以下に冷却され、凝縮した
水分は受器9に落下する。受器9内の凝縮水は、°配管
34及び弁35により容器33に回収される。容器33
は本体ケース2の下方の基部ケース10内に設置されて
いる。冷凍装置の放熱部は2分割され、冷却器8の下流
に設けられた第1放熱部(空気加熱器)11と、写真処
理廃液処理装置外に設けられ外気に熱を放散する第2放
熱部(空冷部)72により構成されている。The circulating air containing sufficient evaporated moisture is cooled to below the dew point by a cooler (condenser) 8 of the refrigeration system, and the condensed moisture falls into a receiver 9. The condensed water in the receiver 9 is collected into a container 33 by a pipe 34 and a valve 35. Container 33
is installed in the base case 10 below the main body case 2. The heat dissipation section of the refrigeration system is divided into two parts: a first heat dissipation section (air heater) 11 provided downstream of the cooler 8, and a second heat dissipation section provided outside the photographic processing waste liquid processing apparatus that dissipates heat to the outside air. (Air cooling section) 72.
第1放熱部11の放熱量は冷却器8の吸熱看以下に設定
され、過剰の放熱は第2放熱部72により行われる。The amount of heat radiated by the first heat radiator 11 is set to be less than the heat absorption capacity of the cooler 8, and excess heat is radiated by the second heat radiator 72.
第1放熱部11の次には循環用ファン12があり、蒸発
用ファン5と協力して空気を循環させる。A circulation fan 12 is provided next to the first heat radiating section 11, and cooperates with the evaporation fan 5 to circulate the air.
容器33に溜った凝縮水は廃棄又は再利用される。The condensed water collected in the container 33 is discarded or reused.
冷却されて水分を除去された循環空気は、蒸発用ファン
5によって、第1放熱部11の加熱を補う補助加熱器6
へ送られて、エンドレスベルト通過後で冷却器通過前の
温度が15〜30℃、好ましくは20〜25℃になるよ
うに調節された後、エンドレスベルト4を通りエンドレ
スベルト4に付着した廃液の水分を蒸発させる。The cooled and moisture-removed circulating air is passed through an evaporation fan 5 to an auxiliary heater 6 that supplements the heating of the first heat radiating section 11.
After passing through the endless belt and before passing through the cooler, the temperature is adjusted to 15 to 30°C, preferably 20 to 25°C, and then the waste liquid that has passed through the endless belt 4 and adhered to the endless belt 4 is Evaporate moisture.
補助加熱器6は所定の温度に空気を温めて、空気の相対
湿度を下げることによって、廃液から蒸発する水分の受
入を確実に安定化させる役目をなす。The auxiliary heater 6 serves to warm the air to a predetermined temperature and lower the relative humidity of the air, thereby ensuring stabilization of the reception of moisture evaporated from the waste liquid.
廃液槽3の上方には、蒸発部の空気の温度を検出する温
度センサ25が設けられ、この温度センサ25はコント
ローラ28と接続されている。温度センサ25は、好ま
しくは蒸発部の下流側で冷却器8の直前に設けられる。A temperature sensor 25 is provided above the waste liquid tank 3 to detect the temperature of the air in the evaporation section, and this temperature sensor 25 is connected to a controller . The temperature sensor 25 is preferably provided immediately before the cooler 8 on the downstream side of the evaporation section.
温度センサ25は、エンドレスベルト通過後で冷却器通
過前の空気温度を検出し、コントローラ28は温度セン
サ25付近の温度が15〜30℃、好ましくは20〜2
5℃になるように補助加熱器6の作動を制御する。The temperature sensor 25 detects the temperature of the air after passing through the endless belt and before passing through the cooler, and the controller 28 detects the temperature of the air near the temperature sensor 25 of 15 to 30 degrees Celsius, preferably 20 to 2 degrees Celsius.
The operation of the auxiliary heater 6 is controlled so that the temperature is 5°C.
温度センサ25により蒸発部の温度を検出し、コントロ
ーラ28により補助加熱器6の作動を制御して、蒸発媒
体通過後で冷却器通過前の空気の温度を一定温度に維持
することにより、単位時間当たりの蒸発、凝縮能力を一
定にすることができ、また処理能力を調整することもで
きる。The temperature of the evaporator section is detected by the temperature sensor 25, and the controller 28 controls the operation of the auxiliary heater 6 to maintain the temperature of the air at a constant temperature after passing through the evaporating medium and before passing through the cooler. The evaporation and condensation capacity per unit can be kept constant, and the processing capacity can also be adjusted.
冷凍装置の圧縮機71及び第2放熱部72は本体ケース
2外に設けられており、第2放熱部72からの放熱はフ
ァン75により外部に放散される。The compressor 71 and the second heat radiating section 72 of the refrigeration system are provided outside the main body case 2, and the heat radiated from the second heat radiating section 72 is radiated to the outside by the fan 75.
したがって、本装置のように密閉本体ケース2の中に外
気の吸引がない状態での運転時に、蒸発に用いる空気の
加熱、冷却の熱収支にモータ及び第2放熱部の余熱が影
響することはない。Therefore, when the device is operated in a state where outside air is not drawn into the sealed main body case 2, the residual heat of the motor and the second heat radiating section does not affect the heat balance of heating and cooling the air used for evaporation. do not have.
本体ケース2内の蒸発部における、エンドレスベルト通
過後で冷却器通過前の空気温度は15〜30℃、好まし
くは20〜25℃の低温に維持されるので、写真処理廃
液中のチオ硫酸アンモニウムや亜硫酸塩が高温により分
解することはなく、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と
がない。The temperature of the air in the evaporation section inside the main body case 2 after passing through the endless belt and before passing through the cooler is maintained at a low temperature of 15 to 30°C, preferably 20 to 25°C, so that ammonium thiosulfate and sulfite in the photographic processing waste liquid are Salt does not decompose at high temperatures, and no harmful or extremely malodorous gases such as sulfur dioxide gas, hydrogen sulfide, or ammonia gas are generated.
したがって、ガスを処理するための第2次処理装置も簡
易になり、小型化が可能になる。また、高温により写真
処理廃液が装置を腐食することもなく、装置の保守も容
易になる。Therefore, the secondary processing device for processing gas is also simplified and can be downsized. Further, the photographic processing waste liquid does not corrode the apparatus due to high temperatures, and maintenance of the apparatus becomes easier.
更に冷凍装置の放熱部の熱利用により装置の運転コスト
を下げることができる。Furthermore, by utilizing heat from the heat dissipation section of the refrigeration system, the operating cost of the system can be reduced.
廃液中の水分が蒸発した濃縮廃液は、配管40及び弁4
1により他の容器42に必要に応じて回収される。The concentrated waste liquid in which the water in the waste liquid has evaporated is transferred to the pipe 40 and the valve 4.
1 into another container 42 as necessary.
廃液の供給及び凝縮水の回収に用いる容器33と、aw
3廃液の回収に用いる容器42は、ともに基部ケース1
0内から容易に脱着可能である。したがって、自動現像
装置からの写真処理廃液を回収して収容した容器33は
、本写真処理廃液処理装置に装着され、凝縮水が内部に
溜まった後に取り外される。また、他方の容器42も濃
縮廃液が溜まった後に取り外される。A container 33 used for supplying waste liquid and collecting condensed water, and an aw
3. Containers 42 used for collecting waste liquid are both attached to the base case 1.
It can be easily attached and detached from within 0. Therefore, the container 33 that collects and stores the photographic processing waste liquid from the automatic developing apparatus is attached to the present photographic processing waste liquid processing apparatus, and is removed after the condensed water has accumulated inside. Further, the other container 42 is also removed after the concentrated waste liquid has accumulated therein.
第2図は廃液及び凝縮水を収容する容器33の断面図で
ある。FIG. 2 is a cross-sectional view of a container 33 containing waste liquid and condensed water.
容器33は内部に備えた可撓性の隔壁36により2つの
収容部37a、37bが画成されている。The container 33 has two storage portions 37a and 37b defined by a flexible partition wall 36 provided therein.
容器33内の第1収容部37aには廃液が収容され、廃
液は配管31及びポンプ32により汲み上げられて廃液
槽3に供給される。また、容器33内の第2収容部37
bには、受器9に溜まった凝縮水が必要に応じて配管3
4及び弁35により回収される。隔壁36の上部は蓋体
38に固定されている。A first storage portion 37a in the container 33 stores waste liquid, and the waste liquid is pumped up by the piping 31 and the pump 32 and supplied to the waste liquid tank 3. In addition, the second storage section 37 inside the container 33
b, the condensed water collected in the receiver 9 is transferred to the pipe 3 as necessary.
4 and valve 35. The upper part of the partition wall 36 is fixed to a lid body 38.
廃液槽3内の廃液中の水分が蒸発するに従って、廃液槽
3内に廃液を補充する必要があるとき、廃液を収容した
容器33を本体ケース2内に装填する。それぞれの配管
31.34は、好ましくは容器33に設けた蓋体38と
着脱自在に設けられ、容器33内にはそれぞれの配管3
1.34と接続可能な他の配管31a、34aを設ける
ことが好ましい。As the moisture in the waste liquid in the waste liquid tank 3 evaporates, when it is necessary to replenish the waste liquid in the waste liquid tank 3, a container 33 containing the waste liquid is loaded into the main body case 2. Each pipe 31 , 34 is preferably detachably provided with a lid 38 provided on the container 33 , and each pipe 3 is provided inside the container 33 .
It is preferable to provide other piping 31a, 34a that can be connected to 1.34.
容器33の装填時、第1収容部37a内に収容した廃液
が容器33のほぼ全容積を占めている。When the container 33 is loaded, the waste liquid stored in the first storage portion 37a occupies almost the entire volume of the container 33.
第1収容部37a内の廃液を廃液槽3に供給するに従っ
て、隔壁36は変形して第1収容部37aの容積が減少
し、第2収容部37bの容積が増加する。そして、容積
が増加した第2収容部37bに、受器9に溜まった凝縮
水が供給されて回収される。As the waste liquid in the first accommodating part 37a is supplied to the waste liquid tank 3, the partition wall 36 is deformed, the volume of the first accommodating part 37a decreases, and the volume of the second accommodating part 37b increases. Then, the condensed water accumulated in the receiver 9 is supplied to the second storage portion 37b whose volume has increased and is collected.
容器33にふいて、廃液の供給と凝縮水の回収が同時に
行われ、廃液の供給が終了するごとに容器33を離脱し
て凝縮水を回収し、下水等に廃棄することができる。By wiping the container 33, supply of waste liquid and recovery of condensed water are performed simultaneously, and each time the supply of waste liquid is finished, the container 33 is removed, the condensed water is recovered, and it can be disposed of in a sewage system or the like.
上記容器33は第1収容部37aに廃液を収容し、第2
収容部37bに凝縮水を収容する構成であるが、写真処
理廃液処理装置は第2収容部37bに濃縮廃液を収容す
る構成であってもよい。The container 33 stores waste liquid in a first storage part 37a, and a second storage part 37a.
Although the configuration is such that the condensed water is stored in the storage section 37b, the photographic processing waste liquid processing apparatus may be configured to store the concentrated waste liquid in the second storage section 37b.
本実施例においては、廃液中の水分が蒸発した後の廃液
濃縮液又は残渣は、別の容器42に回収されるが、第3
図に示すように、容器33を隔壁36により3つに分割
して、3つの収容部にそれぞれ廃液、凝縮水、濃縮廃液
を収容することもできる。In this embodiment, the waste liquid concentrate or residue after the moisture in the waste liquid has evaporated is collected in another container 42, but the third
As shown in the figure, the container 33 can be divided into three parts by a partition wall 36, and the three storage parts can contain waste liquid, condensed water, and concentrated waste liquid, respectively.
例えば、2つの可撓性隔壁36により容器33内に3つ
の収容部37a−cを画成し、廃液槽3へ供給するため
の廃液を第2収容部37bに収容し、廃液槽3からの濃
縮廃液を配管40及び弁41により第1収容部37aへ
案内して回収し、受器9内の凝縮水を配管34及び弁3
5により第3収容部37cへ案内して回収する。この構
成により、1つの容器33を廃液の供給、凝縮水及び濃
縮廃液の回収に用いることができる。For example, three storage parts 37a-c are defined in the container 33 by two flexible partition walls 36, waste liquid to be supplied to the waste liquid tank 3 is stored in the second storage part 37b, and waste liquid to be supplied from the waste liquid tank 3 is stored. The concentrated waste liquid is guided to the first storage part 37a by the pipe 40 and the valve 41 and collected, and the condensed water in the receiver 9 is transferred to the pipe 34 and the valve 3.
5 to guide it to the third storage section 37c and collect it. With this configuration, one container 33 can be used for supplying waste liquid and collecting condensed water and concentrated waste liquid.
なお、容器33は上記構成に限らず、隔壁360代わり
に、可撓性を有する袋体により複数の収容部を画成する
構成であってもよい。Note that the container 33 is not limited to the above configuration, and may have a configuration in which a plurality of storage portions are defined by a flexible bag body instead of the partition wall 360.
更に、容器33は例えば段ボール、厚紙、硬質プラスチ
ック樹脂等の硬質材料から成形されるが、可撓性を有す
るプラスチック樹脂等の材料により成形してもよい。Furthermore, although the container 33 is molded from a hard material such as cardboard, cardboard, or hard plastic resin, it may be molded from a flexible material such as plastic resin.
容器33は、例えば、現像、漂白、漂白定着、定着等の
写真処理液の自動現像装置への補充、及びこの処理液の
廃液の回収に用いて好適である。The container 33 is suitable for use, for example, in replenishing an automatic developing device with a photographic processing solution for developing, bleaching, bleach-fixing, fixing, etc., and for collecting waste liquid of this processing solution.
そこで、容器33に自動現像装置から廃液を回収し、こ
れをそのまま写真処理廃液処理装置に装填することによ
り、廃液槽3への廃液供給作業及び受器9からの凝縮水
の回収作業が極めて容易になる。Therefore, by collecting the waste liquid from the automatic developing device into the container 33 and loading it as it is into the photographic processing waste liquid processing device, the work of supplying the waste liquid to the waste liquid tank 3 and the work of collecting condensed water from the receiver 9 are extremely facilitated. become.
容器33は、写真処理廃液処理装置内、自動現像装置、
又は両者が一体となった装置内のいずれに設けてもよい
。また、写真処理廃液処理装置に容器33を設ける場合
は、本体ケース内外のいずれに容器33を設けてもよい
が、好ましくは本体ケース外に容器33を装置から脱着
できるように設けることにより、後工程処理が容易にな
る。The container 33 is located inside a photographic processing waste liquid processing device, an automatic developing device,
Alternatively, they may be provided anywhere within a device in which both are integrated. In addition, when the container 33 is provided in the photographic processing waste liquid processing apparatus, the container 33 may be provided either inside or outside the main body case, but it is preferable to provide the container 33 outside the main body case so that it can be detached from the apparatus. Process processing becomes easier.
写真処理廃液処理装置を自動現像装置と一体に構成する
場合は、自動現像装置内の写真処理廃液が容器33の廃
液収容部に案内される構成が好ましい。When the photographic processing waste liquid processing apparatus is integrated with the automatic developing apparatus, it is preferable that the photographic processing waste liquid in the automatic developing apparatus is guided to the waste liquid storage part of the container 33.
第4図は本発明の写真処理廃液処理装置の第2実施例の
概略側面図である。本実施例が第1図に示す実施例と異
なるのは、廃液を濃縮処理するための構成であり、廃液
の供給、凝縮水及び濃縮廃液の回収構成は第1実施例と
同じである。したがって、以下には異なる構成について
のみ説明する。FIG. 4 is a schematic side view of a second embodiment of the photographic processing waste liquid treatment apparatus of the present invention. This embodiment differs from the embodiment shown in FIG. 1 in the structure for concentrating the waste liquid, and the structure for supplying the waste liquid and collecting condensed water and concentrated waste liquid is the same as in the first embodiment. Therefore, only the different configurations will be described below.
実質的に気密に構成した本体ケース2内の空気は、蒸発
用ファン5と循環用ファン12により本体ケース2内を
循環する。Air within the main body case 2, which is configured to be substantially airtight, is circulated within the main body case 2 by an evaporation fan 5 and a circulation fan 12.
廃液槽3内の廃液はエンドレスベルト4にヨリ汲み上げ
られ、エンドレスベルト4に付着又は含浸した廃液中の
水分が蒸発する。蒸発した水分を充分含んだ空気は、冷
凍装置の冷却器8により冷却され水分が凝縮し、凝縮し
た水分は受器9に落下する。冷却されて水分を除去され
た空気は、空気加熱器7によりエンドレスベルト通過後
で冷却器通過前の温度が15〜30℃、好ましくは20
〜25℃になるように加熱された後、循環用ファン12
及び蒸発用ファン5により、エンドレスベルト4へ送ら
れる。The waste liquid in the waste liquid tank 3 is pumped up by the endless belt 4, and the moisture in the waste liquid that has adhered to or impregnated the endless belt 4 evaporates. The evaporated air containing sufficient moisture is cooled by a cooler 8 of the refrigeration system, and the moisture is condensed, and the condensed moisture falls into a receiver 9. The cooled air from which water has been removed has a temperature of 15 to 30° C., preferably 20° C., after passing through the endless belt by the air heater 7 and before passing through the cooler.
After being heated to ~25°C, the circulation fan 12
and is sent to the endless belt 4 by the evaporation fan 5.
廃液槽3の上方には、蒸発部の空気の温度を検出する温
度センサ25が設けられ、この温度センサ25はコント
ローラ28と接続されている。温度センサ25は、好ま
しくは蒸発部の下流側で冷却器8の直前に設けられる。A temperature sensor 25 is provided above the waste liquid tank 3 to detect the temperature of the air in the evaporation section, and this temperature sensor 25 is connected to a controller . The temperature sensor 25 is preferably provided immediately before the cooler 8 on the downstream side of the evaporation section.
温度センサ25は、エンドレスベルト通過後で冷却器通
過前の空気温度を検出し、コントローラ28は温度セン
サ25付近の温度が15〜30℃、好ましくは20〜2
5℃になるように空気加熱器6の作動を制御する。The temperature sensor 25 detects the temperature of the air after passing through the endless belt and before passing through the cooler, and the controller 28 detects the temperature of the air near the temperature sensor 25 of 15 to 30 degrees Celsius, preferably 20 to 2 degrees Celsius.
The operation of the air heater 6 is controlled so that the temperature is 5°C.
温度センサ25により蒸発部の温度を検出し、コントロ
ーラ28により空気加熱器6の作動を制御して、エンド
レスベルト通過後で冷却器通過前の空気の温度を一定温
度に維持することにより、単位時間当たりの蒸発、凝縮
能力を一定にすることができ、また処理能力を調整する
こともできる。The temperature of the evaporator section is detected by the temperature sensor 25, and the controller 28 controls the operation of the air heater 6 to maintain the temperature of the air at a constant temperature after passing through the endless belt and before passing through the cooler. The evaporation and condensation capacity per unit can be kept constant, and the processing capacity can also be adjusted.
冷凍装置の圧縮機71、放熱部72及び膨張弁73は本
体ケース2外の基部ケース10内に設けられており、放
熱部72からの熱はファン75により外部に放散される
。したがって、本装置のように密閉本体ケース2の中に
外気の吸引がない状態での運転時に、蒸発に用いる空気
の加熱、冷却の熱収支にモータ及び放熱部の余熱が影響
することはない。A compressor 71, a heat radiation part 72, and an expansion valve 73 of the refrigeration system are provided inside the base case 10 outside the main body case 2, and heat from the heat radiation part 72 is radiated to the outside by a fan 75. Therefore, when the device is operated in a state where outside air is not drawn into the closed main body case 2 as in the case of the present device, residual heat from the motor and the heat radiation section does not affect the heat balance for heating and cooling the air used for evaporation.
本体ケース2内の蒸発部における、エンドレスベルト通
過後で冷却器通過前の空気温度は15〜30℃、好まし
くは20〜25℃の低温に維持されるので、写真処理廃
液中のチオ硫酸アンモニウムや亜硫酸塩が高温により分
解することはなく、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と
がない。The temperature of the air in the evaporation section inside the main body case 2 after passing through the endless belt and before passing through the cooler is maintained at a low temperature of 15 to 30°C, preferably 20 to 25°C, so that ammonium thiosulfate and sulfite in the photographic processing waste liquid are Salt does not decompose at high temperatures, and no harmful or extremely malodorous gases such as sulfur dioxide gas, hydrogen sulfide, or ammonia gas are generated.
したがって、ガスを処理するための第2次処理装置も簡
易になり、小型化が可能になる。また、高温により写真
処理廃液が装置を腐食することもなく、装置の保守も容
易になる。Therefore, the secondary processing device for processing gas is also simplified and can be downsized. Further, the photographic processing waste liquid does not corrode the apparatus due to high temperatures, and maintenance of the apparatus becomes easier.
第5図は蒸発部の変形例の断面図であり、本変形例を上
記実施例の蒸発部に代えることができる。FIG. 5 is a sectional view of a modified example of the evaporator, and this modified example can be replaced with the evaporator of the above embodiment.
蒸発部は、廃液槽3と、廃液槽3内の廃液に一部浸漬し
た廃液後土用エンドレスベルト43と、この汲上用エン
ドレスベルト43に接触した廃液蒸発用エンドレスベル
ト44とからなり、2つのエンドレスベルト43.44
は、略鉛直方向に配設されている。汲上用エンドレスベ
ルト43は廃液槽3と一体に構成され、また蒸発用エン
ドレスベルト44は写真処理廃液処理装置の本体ケース
2に固定されている。汲上用エンドレスベルト43は上
端面が露出して廃液槽3に設けられ、汲上用エンドレス
ベルト43は蒸発用エンドレスベルト44と接触しなが
ら回転することにより、汲み上げた廃液を蒸発用エンド
レスベルト44に転移させる。蒸発用エンドレスベルト
44に転移した廃液中の水分はエンドレスベルト40表
面から蒸発する。The evaporation section consists of a waste liquid tank 3, an endless belt 43 for waste liquid soil partially immersed in the waste liquid in the waste liquid tank 3, and an endless belt 44 for waste liquid evaporation that is in contact with this endless belt 43 for pumping up. Endless belt 43.44
are arranged substantially vertically. The endless belt 43 for pumping up is constructed integrally with the waste liquid tank 3, and the endless belt 44 for evaporation is fixed to the main body case 2 of the photographic processing waste liquid processing apparatus. The endless belt 43 for pumping is provided in the waste liquid tank 3 with its upper end surface exposed, and the endless belt 43 for pumping rotates while contacting the endless belt 44 for evaporation, thereby transferring the pumped waste liquid to the endless belt 44 for evaporation. let The water in the waste liquid transferred to the endless belt 44 for evaporation evaporates from the surface of the endless belt 40.
汲上用エンドレスベルト43を備えた廃液槽3は本体ケ
ース2に対して脱着が容易であり、廃液槽3を交換する
ことにより濃縮廃液及び残渣を回収することができる。The waste liquid tank 3 equipped with the endless pumping belt 43 can be easily attached to and removed from the main body case 2, and by replacing the waste liquid tank 3, concentrated waste liquid and residue can be recovered.
廃液槽3内に収容した廃液中から水分が蒸発するに従っ
て、廃液は濃縮されて粘度が高くなる。As water evaporates from the waste liquid contained in the waste liquid tank 3, the waste liquid becomes concentrated and its viscosity increases.
そして、廃液槽3に配管、弁等を設けて濃縮廃液を回収
する構成の場合、廃液槽3内の濃縮廃液が高粘度になる
と、濃縮廃液が良好に流動せず、濃縮廃液を回収するこ
とが困難である。また、廃液からの析出物が廃液槽3内
に多量に沈殿すると、水分の蒸発効率が大幅に低下する
。In the case of a configuration in which the waste liquid tank 3 is equipped with pipes, valves, etc. to recover the concentrated waste liquid, if the concentrated waste liquid in the waste liquid tank 3 becomes highly viscous, the concentrated waste liquid does not flow well, making it difficult to collect the concentrated waste liquid. is difficult. Furthermore, if a large amount of precipitates from the waste liquid settles in the waste liquid tank 3, the water evaporation efficiency will decrease significantly.
本変形例によれば、廃液槽3内の廃液が濃縮された場合
、又は廃液槽3内に析出物が多量に沈殿した場合、廃液
槽3を交換することにより、濃縮廃液及び残渣を容易に
回収することができる。また、廃液槽3を本体ケース2
から取り外して清掃することも容易である。According to this modification, when the waste liquid in the waste liquid tank 3 is concentrated or when a large amount of precipitate has settled in the waste liquid tank 3, the concentrated waste liquid and the residue can be easily removed by replacing the waste liquid tank 3. It can be recovered. In addition, the waste liquid tank 3 is connected to the main body case 2.
It is also easy to remove and clean.
廃液槽3と汲上用エンドレスベルト43とは一体に構成
され、蒸発用エンドレスベルト44は本体ケース2内に
固定されているので、廃液槽3の脱着は極めて容易であ
る。Since the waste liquid tank 3 and the pumping endless belt 43 are integrally constructed, and the evaporating endless belt 44 is fixed inside the main body case 2, the waste liquid tank 3 can be attached and detached very easily.
第6図は蒸発部の他の変形例の断面図であり、蒸発部は
1つの汲上用エンドレスベルト43に対して複数の蒸発
用エンドレスベルト44が接する構成である。本変形例
によれば、蒸発効率を向上させることができ、しかも廃
液槽3の交換、清掃が容易である。FIG. 6 is a sectional view of another modified example of the evaporating section, and the evaporating section has a structure in which a plurality of endless evaporating belts 44 are in contact with one endless belt 43 for pumping. According to this modification, the evaporation efficiency can be improved, and the waste liquid tank 3 can be easily replaced and cleaned.
第5図及び第6図に示される、汲土用エンドレスベルト
43と蒸発用エンドレスベルト44を1える蒸発部の構
成は、前述の密閉した構成の写真処理廃液処理装置に限
らず、非密閉に構成した写真処理廃液処理装置にも適用
することができ、同様の効果を奏する。更に、このよう
な蒸発部の構成は、写真処理廃液を蒸発して濃縮させる
方式のいかなる写真処理廃液処理装置にも適用すること
ができ、写真処理廃液の蒸発効率が向上し、しかも廃液
槽の交換、清掃等が容易になる。The structure of the evaporation section shown in FIGS. 5 and 6, which includes the endless belt 43 for soil extraction and the endless belt 44 for evaporation, is not limited to the above-mentioned sealed photographic processing waste liquid processing apparatus, but can also be used for non-sealed construction. The present invention can also be applied to the photographic processing waste liquid processing apparatus constructed above, and similar effects can be obtained. Furthermore, this configuration of the evaporator section can be applied to any photographic processing waste liquid processing equipment that evaporates and concentrates the photographic processing waste liquid, and improves the evaporation efficiency of the photographic processing waste liquid, and also improves the efficiency of the waste liquid tank. Replacement, cleaning, etc. become easier.
本発明によれば、可撓性隔壁により分割した複数の収容
部を存する容器に廃液、凝縮水及び濃縮廃液をそれぞれ
独立に収容することにより、1つの容器にすべての液を
収容できる。したがって、蒸発部への廃液供給、凝縮部
からの凝縮水回収、濃縮廃液の回収とを同時に行い、廃
液供給後に容器を交換することにより、凝縮水及び濃縮
廃液の回収が容易になる。According to the present invention, by storing waste liquid, condensed water, and concentrated waste liquid independently in a container having a plurality of storage sections divided by a flexible partition, all liquids can be stored in one container. Therefore, by simultaneously supplying waste liquid to the evaporator, recovering condensed water from the condensing unit, and recovering concentrated waste liquid, and replacing the container after supplying the waste liquid, it becomes easy to recover the condensed water and concentrated waste liquid.
すなわち、廃液を収容していた容器に凝縮水及び濃縮廃
液を案内して回収することにより、廃液の供給、凝縮水
及び濃縮廃液の回収に伴う容器の装脱が1回で済み、凝
縮水及び濃縮廃液の回収を容易に行うことができる。In other words, by guiding and collecting the condensed water and concentrated waste liquid into the container that had previously contained the waste liquid, it is only necessary to supply the waste liquid and to load and unload the container once in order to collect the condensed water and concentrated waste liquid. Waste liquid can be easily collected.
また、廃液を収容していた容器内に凝縮水及び濃縮廃液
を収容するので、1つの容器を廃液供給、凝縮水回収及
び濃縮廃液回収に兼用でき、写真処理廃液処理装置内で
の容器収納領域を低減できる。In addition, since the condensed water and concentrated waste liquid are stored in the container that previously contained the waste liquid, one container can be used for both the waste liquid supply, condensed water recovery, and concentrated waste liquid collection, and the container storage area in the photographic processing waste liquid processing equipment. can be reduced.
したがって、写真処理廃液処理装置を小型化することが
できる。Therefore, the photographic processing waste liquid treatment apparatus can be downsized.
更に、写真処理廃液処理装置を小型に構成できるので、
自動現像装置と一体化もしくは自動現像装置に内蔵する
ことも可能になる。Furthermore, since the photographic processing waste liquid treatment device can be configured in a small size,
It also becomes possible to integrate it with an automatic developing device or to incorporate it into the automatic developing device.
第1図は本発明の写真処理廃液処理装置の一実施例の概
略側面図、
第2図は容器の断面図、
第3図は容器の変形例の断面図、
第4図は写真処理廃液処理装置の第2実施例の概略側面
図、
第5図及び第6図は蒸発部の変形例の断面図である。
図中符号;
2 本体ケース 3 廃液槽
4 エンドレスベルト 5 蒸発用ファン6 補助加熱
器
8 空気冷却器 9 受器
11 第1放熱部 12−循環用ファン25 温度
センサ
28 コントローラ
31.31a、34.34a、40 配管32 ポン
プ
33 容器
35.41−弁
37a、37b、37c 収容部
38 蓋体
43 汲上用エンドレスベルト
44蒸発用エンドレスベルト
71−圧縮機 72 第2放熱部第1図
第
3
図
第
図
手続補正占
1.1材牛の耘
平成1年特許願第163795号
2、発明の名称
写真処理廃液処理装置
東京都千代田区霞が関3丁目8番1号
虎の門三井ビル14階 電話(581)−9601(
イ堝り5、補正命令の日付:
(自発)
8、補正の内容
「発明の詳細な説明」の欄を次のように補正する。
(1)明細書第8頁9〜12行目の「また、本発明にお
ける写真処理廃液とは、・・・・・・廃液であってもよ
い。」を下記の通りに補正する。
[また、本体ケース内の気圧を760mmHgより低く
、好ましくは1〜700nnnHg、更に好ましくは5
〜400mmHg、更に好ましくはlO〜30mml(
gに減圧して廃液から水分を蒸発させ、蒸発した水分を
凝縮してもよい。
また、本発明における写真処理廃液とは、現像(カラー
、黒白)、漂白、漂白定着、定着、水洗、安定等の写真
処理を行った後の廃液であればいかなる廃液であっても
よい。これらの各処理廃液はすべて混合して処理されて
もよく、単独で処理されてもよい。また、水洗処理と安
定処理の廃液を混合し、現像処理、定着処理及び漂白処
理の廃液を混合してそれぞれ処理してもよく、更に他の
組合せで混合して処理してもよい。
上記廃液は感光材料の写真処理に用いられた種々の処理
液を含み得るものであって、以下これらの処理液につい
て説明する。
感光材料の現像処理に用いる発色現像液は、好ましくは
芳香族第一級アミン系発色現像主薬を主成分とするアル
カリ性水溶液である。この発色現像主薬としては、アミ
ノフェノール系化合物も有用であるが、p−フェニレン
ジアミン系化合物が好ましく使用され、その代表例とし
ては3−メチル−4−アミノ−N、N−ジエチルアニリ
ン、3−メチル−4−アミノ−N−エチル−N−β−ヒ
ドロキシエチルアニリン、3−メチル−4−アミノ−N
−エチル−N−β−メタンスルホンアミドエチルアニリ
ン、3−メチル−4−アミノ−N−エチル−N−β−メ
トキシエチルアニリン及びこれらの硫酸塩、塩酸塩もし
くはp−トルエンスルボン酸塩が挙げられる。これらの
化合物は目的に応じ2種以上併用することもできる。
発色現像液は、アルカリ金属の炭酸塩、ホウ酸塩もしく
はリン酸塩のようなp++緩衝剤、臭化物塩、沃化物塩
、ベンズイミダゾール類、ベンゾチアゾール類もしくは
メルカプト化合物のような現像抑制剤またはカブリ防止
剤などを含むのが一般的である。また必要に応じて、ヒ
ドロキシルアミン、ジエチルヒドロキシルアミン、亜硫
酸塩ヒドラジン類、フェニルセミカルバジド類、トリエ
タノールアミン、カテコールスルホン酸類、トリエチレ
ンジアミン(1,4−ジアザビシクロ[2,2,2]
オクタン)頚の如き各種保恒剤、エチレングリコール、
ジエチレングリコールのような有機溶剤、ベンジルアル
コール、ポリエチレングリコール、四級アンモニウム塩
、アミン類のような現像促進剤、色素形成カプラー、競
争カプラー、ナトリウムボロンハイドライドのようなカ
ブラセ剤、1−フェニル−3−ピラゾリドンのような補
助現像主薬、粘性付与剤、アミノポリカルボン酸、アミ
ノポリホスホン酸、アルキルホスホン酸、ホスホノカル
ボン酸に代表されるような各種キレート剤、例えば、エ
チレンジアミン四酢酸、ニトリロ三酢酸、ジエチレント
リアミン五酢酸、シクロヘキサンジアミン四酢酸、ヒド
ロキシエチルイミノジ酢酸、1−ヒドロキシエチリデン
−1,1−ジホスホン酸、ニトリロ−N、 N、 N−
トリメチレンホスホン酸、エチレンジアミン−N、N、
N’、N’ −テトラメチレンホスホン酸、エチレング
リコ−ル(0−ヒドロキシフェニル酢酸)及びそれらの
塩を代表例として挙げることができる。
また反転処理を実施する場合は通常黒白現像を行ってか
ら発色現像する。この黒白現像液には、ハイドロキノン
などのジヒドロキシベンゼン類、■−フェニルー3−ピ
ラゾリドンなどの3−ピラゾリドン類またはN−メチル
−p−アミノフェノールなどのアミノフェノール類など
公知の黒白現像主薬を単独であるいは組み合わせて用い
ることができる。
これらの発色現像液及び黒白現像液のpHは9〜12で
あることが一般的である。またこれらの現像液の補充量
は、処理するカラー写真感光材料にもよるが、−iに感
光材料1平方メートル当り31以下であり、補充液中の
臭化物イオン濃度を低減させておくことにより500m
ji以下にすることもできる。補充量を低減する場合に
は処理槽の空気どの接触面積を小さくすることによって
液の蒸発、空気酸化を防止することが好ましい。また現
像液中の臭化物イオンの蓄積を抑える手段を用いること
により補充量を低減することもできる。
発色現像後の写真乳剤層は通常漂白処理される。
漂白処理は定着処理と同時に行われてもよいしく漂白定
着処理)、個別に行われてもよい。更に、処理の迅速化
を図るため、漂白処理後に漂白定着処理する処理方法で
もよい。更に二種の連続した漂白定着浴で処理すること
、漂白定着処理の前に定着処理すること、又は漂白定着
処理後に漂白処理することも目的に応じ任意に実施でき
る。
漂白剤としては、例えば鉄(■)、コバルト(■)、ク
ロム(■)、銅(II)などの多価金属の化合物、過酸
類、キノン類、ニトロ化合物等が用いられる。代表的漂
白剤としてはフェリシアン化物;重クロム酸塩;鉄(1
)もしくはコバルト(1)の有機錯塩、例えばエチレン
ジアミン四酢酸、ジエチレントリアミン五酢酸、シクロ
ヘキサンジアミン四酢酸、メチルイミノニ酢酸、1,3
−ジアミノプロパン四酢酸、グリコールエーテルジアミ
ン四酢酸、などのアミノポリカルボン酸類もしくはクエ
ン酸、酒石酸、リンゴ酸などの錯塩;過硫酸塩;臭素酸
塩;過マンガン酸塩;ニトロベンゼン類などを用いるこ
とができる。これらのうちエチレンジアミン四酢酸鉄(
III)錯塩を始めとするアミノポリカルボン酸鉄(I
[[)錯塩及び過硫酸塩は迅速処理と環境汚染防止の観
点から好ましい。
更にアミノポリカルボン酸鉄(m)ti塩は、漂白液に
おいても漂白定着液においても特に有用である。これら
のアミノポリカルボン酸鉄(nnt=塩を用いた漂白液
又は漂白定着液のpHは通常5.5〜8であるが、処理
の迅速化のために、更に低いpHで処理することもでき
る。
漂白液、漂白定着液及びそれらの前浴には、必要に応じ
て漂白促進剤を使用することができる。
有用な漂白促進剤の具体例は、次の明細書に記載されて
いる:米国特許第 3,893,858号、西独特許第
1.290,812号、特開昭53−95.630号、
リサーチ・ディスクロージャー17,129号(197
8年7月)などに記載のメルカプト基またはジスルフィ
ド結合を有する化合物;特開昭50−140.129号
に記載のチアゾリジン誘導体;米国特許第3,706,
561号に記載の千オ尿素誘導体;特開昭58−16.
235号に記載の沃化物塩;西独特許第2,748,4
30号に記載のポリオキシエチレン化合物頚;特公昭4
5−8836号記載のポリアミン化合物;臭化物イオン
等が使用できる。なかでもメルカプト基またはジスルフ
ィド基を有する化合物が促進効果が大きい観点で好まし
く、特に米国特許第 3,893,858号、西独特許
第1290.812号、特開昭53−95.630号に
記載の化合物が好ましい。更に、米国特許第4,552
,834号に記載の化合物も好ましい。これらの漂白促
進剤は感光材料中に添加してもよい。撮影用のカラー感
光材料を漂白定着するときにこれらの漂白促進剤は特に
有効である。
定着剤としてはチオ硫酸塩、チオシアン酸塩、チオエー
テル系化合物、チオ尿素類、多量の沃化物塩等を挙げる
ことができるが、チオ硫酸塩の使用が一般的であり、特
にチオ硫酸アンモニウムが最も広範に使用できる。漂白
定着後の保恒剤としては、亜硫酸塩、重亜硫酸塩、スル
フィン酸類あるいはカルボニル重亜硫酸付加物が好まし
い。
ハロゲン化銀カラー写真感光材料は、脱銀処理後、水洗
及び/又は安定工程を経るのが一般的である。水洗工程
での水洗水量は、感光材料の特性(例えばカプラー等使
用素材による)、用途、更には水洗水温、水洗タンクの
数(段数)、向流、順流等の補充方式、その他種々の条
件によって広範囲に設定し得る。このうち、多段向流方
式における水洗タンク数と水量の関係は、ジャーナルオ
プ ザ ソサエティ オブ モーション ピクチャー
アンド テレヴィジョン エンジニアズ(Journa
l of the 5ociety of Motio
n Picture andTelevision E
ngineers)第64巻、第248−253頁(1
955年5月号)に記載の方法で求めることができる。
前記文献に記載の多段向流方式によれば、水洗水量を大
幅に減少し得るが、タンク内における水の滞留時間の増
加により、バクテリアが繁殖し、生成した浮遊物が感光
材料に付着する等の問題が生じる。前記カラー感光材料
の処理において、このような問題の解決策として、特開
昭62−288.838号に記載のカルシウムイオン、
マグネシウムイオンを低減させる方法を極めて有効に用
いることができる。また、特開昭57−8,542号に
記載のイソチアゾロン化合物やサイアベンダゾール類、
塩素化イソシアヌール酸ナトリウム等の塩素系殺菌剤、
その他ベンゾトリアゾール等、堀口博著「防菌防黴剤の
化学」、衛生技術会場「微生物の滅菌、殺菌、防黴技術
J、日本防菌防黴学会編「防菌防黴剤事典」に記載の殺
菌剤を用いることもできる。
上記感光材料の処理における水洗水のpHは、4〜9で
あり、好ましくは5〜8である。水洗水温、水洗時間も
、感光材料の特性、用途等で種々設定し得るが、−aに
は15〜45°Cで20秒〜10分、好ましくは25〜
40°Cで30秒〜5分の範囲が選択される。
更に、前記感光材料は、上記水洗に代り、直接安定液に
よって処理することもできる。このような安定化処理に
おいては、特開昭57−8,543号、同58−14,
834号、同60−220.345号に記載の公知の方
法はすべて用いることができる。
又、前記水洗処理に続いて、更に安定化処理する場合も
あり、その例として、撮影用カラー感光材料の最終浴と
して使用される、ホルマリンと界面活性剤を含有する安
定浴を挙げることができる。
この安定浴にも各種キレート剤や防黴剤を加えることも
できる。
上記水洗及び/又は安定液の補充に伴うオーバーフロー
液は脱恨工程等他の工程において再利用することもでき
る。
上記ハロゲン化銀カラー感光材料には処理の簡略化及び
迅速化の目的で発色現像主薬を内蔵しても良い。内蔵す
るためには、発色現像主薬の各種プレカーサーを用いる
のが好ましい。例えば米国特許第3.342,597号
記載のインドアニリン系化合物、同第3,342.59
9号、リサーチ・ディスクロージャー14,850号及
び同15.159号記載のシッフ塩基型化合物、同13
,924号記載のアルドール化合物、米国特許第3.7
19.492号記載の金属塩錯体、特開昭53−135
.628号記載のウレタン系化合物を挙げることができ
る。
上記ハロゲン化銀カラー感光材料は、必要に応じて、発
色現像を促進する目的で、各種の1−フェニル−3−ビ
ラプリトン類を内蔵しても良い。典型的な化合物は特開
昭56−64,339号、同5714.4547号、お
よび同58−115,438号等に記載されている。
上記感光材料に内蔵された化合物は感光材料の処理中に
感光材料から処理液中に溶出するものであり、したがっ
てこのような感光材料を処理した場合に生ずる廃液中に
はこれらの化合物も含まれている。
上記各種処理液は10°C〜50°Cにおいて使用され
る。通常は33°C〜38°Cの温度が標準的であるが
、より高温にして処理を促進し処理時間を短縮したり、
逆により低温にして画質の向上や処理液の安定性の改良
を達成することができる。また、感光材料の節銀のため
西独特許第2,226,770号又は米国特許第3,6
74,499号に記載のコバルト補力もしくは過酸化水
素補力を用いた処理を行ってもよい。」
(2)同書第11頁10〜11行目、第12頁5〜6行
目及び第13頁第1〜2行目の「15〜30°C1好ま
しくは20〜25°C」を[10〜40°C1好ましく
は15〜30゛C1更に好ましくは20〜25°C」と
補正する。
(3)同書第18頁16〜17行目、第19頁7〜8行
目及び第20頁第4〜5行目の[15〜30°C1好ま
しくは20〜25°C」を「10〜40°C1好ましく
は15〜30°C1更に好ましくは20〜25°C」と
補正する。Fig. 1 is a schematic side view of an embodiment of the photographic processing waste liquid processing apparatus of the present invention, Fig. 2 is a sectional view of a container, Fig. 3 is a sectional view of a modified example of the container, and Fig. 4 is a photographic processing waste liquid processing A schematic side view of the second embodiment of the apparatus, and FIGS. 5 and 6 are cross-sectional views of modified examples of the evaporation section. Symbols in the figure: 2 Main body case 3 Waste liquid tank 4 Endless belt 5 Evaporation fan 6 Auxiliary heater 8 Air cooler 9 Receiver 11 First heat radiation section 12 - Circulation fan 25 Temperature sensor 28 Controller 31.31a, 34.34a , 40 Piping 32 Pump 33 Container 35.41 - Valve 37a, 37b, 37c Storage part 38 Lid 43 Endless belt for pumping 44 Endless belt for evaporation 71 - Compressor 72 Second heat dissipation part Fig. 1 Fig. 3 Fig. Procedure Amended Horoscope 1.1 Timber Cattle 1999 Patent Application No. 163795 2 Name of the Invention Photographic Processing Waste Liquid Treatment Device 3-8-1 Kasumigaseki, Chiyoda-ku, Tokyo Toranomon Mitsui Building 14th Floor Telephone (581) - 9601(
B. 5. Date of amendment order: (Voluntary) 8. Contents of amendment The "Detailed description of the invention" column is amended as follows. (1) On page 8, lines 9 to 12 of the specification, "The photographic processing waste liquid in the present invention may also be waste liquid." shall be amended as follows. [Also, the atmospheric pressure inside the main body case is lower than 760 mmHg, preferably 1 to 700 nnnHg, more preferably 5
~400 mmHg, more preferably lO~30 mml (
The water may be evaporated from the waste liquid by reducing the pressure to 100 g, and the evaporated water may be condensed. Further, the photographic processing waste liquid in the present invention may be any waste liquid after performing photographic processing such as development (color, black and white), bleaching, bleach-fixing, fixing, water washing, stabilization, etc. All of these treated waste liquids may be treated as a mixture, or may be treated individually. Furthermore, the waste liquids from the water washing process and the stabilizing process may be mixed, the waste liquids from the developing process, fixing process and bleaching process may be mixed and processed individually, or they may be mixed and processed in other combinations. The waste liquid may contain various processing liquids used in photographic processing of light-sensitive materials, and these processing liquids will be explained below. The color developing solution used for developing the photosensitive material is preferably an alkaline aqueous solution containing an aromatic primary amine color developing agent as a main component. Aminophenol compounds are also useful as color developing agents, but p-phenylenediamine compounds are preferably used, representative examples of which include 3-methyl-4-amino-N, N-diethylaniline, 3- Methyl-4-amino-N-ethyl-N-β-hydroxyethylaniline, 3-methyl-4-amino-N
-ethyl-N-β-methanesulfonamidoethylaniline, 3-methyl-4-amino-N-ethyl-N-β-methoxyethylaniline, and their sulfates, hydrochlorides, or p-toluenesulfonates. It will be done. Two or more of these compounds can be used in combination depending on the purpose. The color developer may contain p++ buffers such as alkali metal carbonates, borates or phosphates, development inhibitors or fogging agents such as bromide salts, iodide salts, benzimidazoles, benzothiazoles or mercapto compounds. It generally contains an inhibitor. In addition, as necessary, hydroxylamine, diethylhydroxylamine, sulfite hydrazines, phenyl semicarbazides, triethanolamine, catechol sulfonic acids, triethylenediamine (1,4-diazabicyclo[2,2,2]
Octane) various preservatives such as neck, ethylene glycol,
Organic solvents such as diethylene glycol, benzyl alcohol, polyethylene glycol, quaternary ammonium salts, development accelerators such as amines, dye-forming couplers, competitive couplers, fogging agents such as sodium boron hydride, 1-phenyl-3-pyrazolidone. Auxiliary developing agents, viscosity imparting agents, various chelating agents such as aminopolycarboxylic acids, aminopolyphosphonic acids, alkylphosphonic acids, phosphonocarboxylic acids, such as ethylenediaminetetraacetic acid, nitrilotriacetic acid, diethylenetriamine Pentaacetic acid, cyclohexanediaminetetraacetic acid, hydroxyethyliminodiacetic acid, 1-hydroxyethylidene-1,1-diphosphonic acid, nitrilo-N, N, N-
trimethylene phosphonic acid, ethylenediamine-N, N,
Representative examples include N',N'-tetramethylenephosphonic acid, ethylene glycol (0-hydroxyphenylacetic acid), and salts thereof. Further, when performing reversal processing, black and white development is usually performed and then color development is performed. In this black and white developer, known black and white developing agents such as dihydroxybenzenes such as hydroquinone, 3-pyrazolidones such as -phenyl-3-pyrazolidone, or aminophenols such as N-methyl-p-aminophenol are used alone or Can be used in combination. The pH of these color developing solutions and black and white developing solutions is generally 9 to 12. The amount of replenishment of these developing solutions depends on the color photographic light-sensitive material to be processed, but -i is 31 or less per 1 square meter of light-sensitive material, and by reducing the bromide ion concentration in the replenisher, 500 m
It can also be less than ji. When reducing the amount of replenishment, it is preferable to prevent evaporation of the liquid and air oxidation by reducing the contact area between the air and the processing tank. Furthermore, the amount of replenishment can be reduced by using means for suppressing the accumulation of bromide ions in the developer. After color development, the photographic emulsion layer is usually bleached. The bleaching process may be performed simultaneously with the fixing process (bleach-fixing process), or may be performed separately. Furthermore, in order to speed up the processing, a bleach-fixing treatment may be performed after the bleaching treatment. Furthermore, treatment with two consecutive bleach-fixing baths, fixing treatment before bleach-fixing treatment, or bleaching treatment after bleach-fixing treatment can be carried out as desired depending on the purpose. Examples of bleaching agents that can be used include compounds of polyvalent metals such as iron (■), cobalt (■), chromium (■), and copper (II), peracids, quinones, and nitro compounds. Typical bleaching agents include ferricyanide; dichromate; iron (1
) or organic complex salts of cobalt (1), such as ethylenediaminetetraacetic acid, diethylenetriaminepentaacetic acid, cyclohexanediaminetetraacetic acid, methyliminodiacetic acid, 1,3
- Aminopolycarboxylic acids such as diaminopropanetetraacetic acid, glycol ether diamine tetraacetic acid, or complex salts of citric acid, tartaric acid, malic acid, etc.; persulfates; bromates; permanganates; nitrobenzenes, etc. may be used. can. Of these, iron ethylenediaminetetraacetate (
III) Aminopolycarboxylic acid iron(I) including complex salts
[[) Complex salts and persulfates are preferred from the viewpoint of rapid processing and prevention of environmental pollution. Additionally, aminopolycarboxylic acid iron(m)ti salts are particularly useful in both bleach and bleach-fix solutions. The pH of the bleach or bleach-fix solution using these aminopolycarboxylic acid iron (nnt = salts) is usually 5.5 to 8, but it can also be processed at an even lower pH to speed up the processing. Bleach accelerators can optionally be used in the bleach, bleach-fix and pre-baths thereof. Specific examples of useful bleach accelerators are described in the following specification: US Pat. Patent No. 3,893,858, West German Patent No. 1.290,812, Japanese Patent Application Publication No. 1983-95.630,
Research Disclosure No. 17,129 (197
Compounds having a mercapto group or disulfide bond as described in JP-A-50-140-129; U.S. Patent No. 3,706;
1,000 urea derivatives described in No. 561; JP-A-58-16.
Iodide salts described in No. 235; West German Patent No. 2,748,4
Polyoxyethylene compound neck described in No. 30;
Polyamine compounds described in No. 5-8836; bromide ions, etc. can be used. Among these, compounds having a mercapto group or a disulfide group are preferred from the viewpoint of a large promoting effect, and in particular, compounds described in U.S. Pat. Compounds are preferred. Additionally, U.S. Patent No. 4,552
, 834 are also preferred. These bleach accelerators may be added to the light-sensitive material. These bleach accelerators are particularly effective when bleach-fixing color light-sensitive materials for photography. Examples of fixing agents include thiosulfates, thiocyanates, thioether compounds, thioureas, and large amounts of iodide salts, but thiosulfates are commonly used, with ammonium thiosulfate being the most widely used. Can be used for Preservatives used after bleach-fixing are preferably sulfites, bisulfites, sulfinic acids, or carbonyl bisulfite adducts. Silver halide color photographic materials are generally subjected to water washing and/or stabilization steps after desilvering treatment. The amount of water used in the washing process depends on the characteristics of the photosensitive material (for example, depending on the materials used such as couplers), the application, the temperature of the washing water, the number of washing tanks (number of stages), the replenishment method such as countercurrent or forward flow, and various other conditions. Can be set over a wide range. Among these, the relationship between the number of flushing tanks and the amount of water in the multistage countercurrent method is described in the Journal of the Society of Motion Pictures.
and Television Engineers (Journa)
l of the 5ociety of Motio
n Picture and Television E
ngineers) Vol. 64, pp. 248-253 (1
It can be determined by the method described in May 955 issue). According to the multi-stage countercurrent method described in the above-mentioned literature, the amount of water used for washing can be significantly reduced, but due to the increase in the residence time of water in the tank, bacteria will breed, and the generated suspended matter will adhere to the photosensitive material. The problem arises. As a solution to such problems in the processing of color photosensitive materials, calcium ions, as described in JP-A No. 62-288.838,
A method of reducing magnesium ions can be used very effectively. In addition, isothiazolone compounds and thiabendazoles described in JP-A No. 57-8,542,
Chlorine-based disinfectants such as chlorinated sodium isocyanurate,
Others, such as benzotriazole, are described in Hiroshi Horiguchi's ``Chemistry of Antibacterial and Antifungal Agents'', Hygiene Technology Forum ``Sterilization of Microorganisms, Disinfection, and Antifungal Technology J'', and ``Encyclopedia of Antibacterial and Antifungal Agents'' edited by the Japan Antibacterial and Antifungal Society. Fungicides can also be used. The pH of the washing water in the processing of the photosensitive material is 4 to 9, preferably 5 to 8. The washing water temperature and washing time can be set variously depending on the characteristics of the photosensitive material, its use, etc., but for -a, it is 20 seconds to 10 minutes at 15 to 45°C, preferably 25 to 10 minutes.
A range of 30 seconds to 5 minutes at 40°C is selected. Furthermore, instead of washing with water, the photosensitive material can be directly processed with a stabilizing solution. In such stabilization treatment, Japanese Patent Application Laid-Open Nos. 57-8,543, 58-14,
All known methods described in No. 834 and No. 60-220.345 can be used. Further, following the water washing treatment, a further stabilization treatment may be carried out, such as a stabilizing bath containing formalin and a surfactant, which is used as a final bath for color photosensitive materials for photography. . Various chelating agents and antifungal agents can also be added to this stabilizing bath. The overflow liquid resulting from the water washing and/or replenishment of the stabilizing liquid can also be reused in other processes such as the grudge removal process. The silver halide color light-sensitive material may contain a color developing agent for the purpose of simplifying and speeding up processing. In order to incorporate the color developing agent, it is preferable to use various precursors of the color developing agent. For example, indoaniline compounds described in U.S. Pat. No. 3,342,597, U.S. Pat. No. 3,342.59
No. 9, Schiff base-type compounds described in Research Disclosure No. 14,850 and Research Disclosure No. 15.159, Research Disclosure No. 13
, 924, U.S. Patent No. 3.7
Metal salt complex described in No. 19.492, JP-A-53-135
.. Examples include urethane compounds described in No. 628. The above-mentioned silver halide color light-sensitive material may contain various 1-phenyl-3-birapritones, if necessary, for the purpose of promoting color development. Typical compounds are described in JP-A Nos. 56-64,339, 5714.4547, and 58-115,438. The compounds contained in the above-mentioned photosensitive materials are eluted from the photosensitive materials into the processing solution during processing of the photosensitive materials, and therefore these compounds are not included in the waste solution generated when such photosensitive materials are processed. ing. The above-mentioned various processing liquids are used at 10°C to 50°C. Normally, the standard temperature is 33°C to 38°C, but higher temperatures can be used to accelerate the processing and shorten the processing time.
Conversely, it is possible to improve the image quality and the stability of the processing solution by lowering the temperature. In addition, for saving silver in photosensitive materials, West German Patent No. 2,226,770 or U.S. Patent No. 3,6
A treatment using cobalt intensification or hydrogen peroxide intensification as described in No. 74,499 may be performed. (2) "15 to 30°C, preferably 20 to 25°C" on page 11, lines 10 to 11, page 12, lines 5 to 6, and page 13, lines 1 to 2 of the same book. to 40°C, preferably 15 to 30°C, more preferably 20 to 25°C. (3) In the same book, page 18, lines 16-17, page 19, lines 7-8, and page 20, lines 4-5, [15-30°C1 preferably 20-25°C] is replaced with "10-30°C, preferably 20-25°C". The temperature is corrected to 40°C, preferably 15 to 30°C, and more preferably 20 to 25°C.
Claims (1)
して回収する写真処理廃液処理装置において、写真処理
廃液、凝縮水、濃縮廃液の少なくとも2種の液をそれぞ
れ収容可能に、可撓性隔壁により分割した複数の収容部
を有する容器と、第1収容部に収容される廃液を蒸発部
に供給する廃液供給手段と、凝縮部により凝縮された水
分及び濃縮廃液の少なくとも一方を第2収容部へ回収す
る回収手段とを備えた写真処理廃液処理装置In a photographic processing waste liquid processing device that evaporates water in photographic processing waste liquid and condenses and recovers the evaporated water, it is flexible and can accommodate at least two types of liquids: photographic processing waste liquid, condensed water, and concentrated waste liquid. a container having a plurality of storage sections divided by partition walls, a waste liquid supply means for supplying the waste liquid contained in the first storage section to the evaporation section, and a second storage section for storing at least one of the water condensed by the condensation section and the concentrated waste liquid. A photographic processing waste liquid processing device equipped with a collection means for recovering the waste liquid to the
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP16379589A JPH0330888A (en) | 1989-06-28 | 1989-06-28 | Apparatus for treating waste photographic processing solution |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP16379589A JPH0330888A (en) | 1989-06-28 | 1989-06-28 | Apparatus for treating waste photographic processing solution |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH0330888A true JPH0330888A (en) | 1991-02-08 |
Family
ID=15780847
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
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JP16379589A Pending JPH0330888A (en) | 1989-06-28 | 1989-06-28 | Apparatus for treating waste photographic processing solution |
Country Status (1)
Country | Link |
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JP (1) | JPH0330888A (en) |
-
1989
- 1989-06-28 JP JP16379589A patent/JPH0330888A/en active Pending
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