REGENERATION OF SPENT FIXER SOLUTION

Abstract: A process for regenerating spent fixer solution which includes the steps of adding finely particulate zinc, such as zinc dust, to the solution to cause silver dissolved therein to precipitate and removing the precipitate from the solution thereby producing a regenerated fixer solution.

Description: REGENERATION OF SPENT FIXER SOLUTION BACKGROUND OF THE INVENTION The present invention relates to the regeneration of spent fixer solution resulting from the processing of black-and-white films. The photographic processing of various types of films, including lithographic and x-ray films involves the development of an image by reduction of silver halide crystals to metallic silver and the removal of the unused silver halides from the film. Various photographic fixer solutions are used in the industry to dissolve the residual silver halide. The most common form of photographic fixer solution is one which contains a thiosulphate such as sodium thiosulphate or ammonium thiosulphate as active ingredient. A spent fixer solution is one which has been used for fixing film and in this specification and claims this is the meaning which will be given to the term "spent fixer solution". Silver recovery from spent fixer solution is customarily done by electrolysis. Such processes suffer from a number of disadvantages. Apart from the relatively high capital and maintenance costs, and the relatively low rate of throughput, the process is also relatively inefficient. As full recovery is being approached, side reactions become increasingly important, leading to the precipitation of sulphur. Usually it is possible to recover only of the order of 97 to 99 percent of the silver originally present. Although it is possible to recover the residual silver, e.g. with steel wool, such silver is considered by many not to be worthwhile. The barren fixer, with or without residual silver (which is highly toxic to lower forms of life), is usually disposed of into the sewer, annually adding tonnage quantities of barren fιxeτ solution, an environmentally unfriendly material, to the electrolyte load of urban wastewater. In general, spent fixer solution which has been subjected to electrolysis is unsuitable for re-use. For not only is part of the thiosulphate ion oxidised at the anode while the silver is being deposited at the cathode, but other sulphur species are also formed, and their presence in the electrolysed fixer solution tends to lead to the deposition of harmful deposits in the processing equipment. Electrolysis produces a relatively dark colour in the fixer solution (probably by electrolytic oxidation of some of the additives), and both ammonium thiosulphate and some of the additives require replenishment if the use of the fixer is to be extended. Another small-scale method for silver recovery comprises passing the spent fixer solution through a column packed with a cartridge of an alloy fabricated into a fibrous foπn resembling steel wool. Recovery is however usually incomplete and the treated fixer solution is unsuitable for re-use. Moreover, the method adds heavy metals to the effluent, which customarily goes straight down the drain. South African Patent No. 90/7735 teaches precipitation of the silver as silver sulphide with a solution of the sulphide or hydrosulphide of an alkali metal or ammonium. The mother liquor drawn off after the silver sulphide has settled out is claimed to be regenerated and suitable for re-use. But the method suffers from a number of disadvantages. Addition of the sulphide or hydrosulphide has to be carefully controlled, for excess sulphide leads to precipitation of sulphur. The spent fixer solution cannot be regenerated at source (e.g. in large hospitals), in the first instance because there is always the accompanying risk of foul-smelling, highly toxic hydrogen sulphide gas being released during processing, particularly if the pH of the fixer solution is at the lower end of the typical operating range. The reagent itself is characterised by a smell of hydrogen sulphide. Also, the recovered silver sulphide has to be roasted before the silver may be smelted out, in the process sending the sulphide into the atmosphere as sulphur dioxide (the "acid rain" gas), unless steps are taken to scrub it out from the gases given off. SUMMARY OF THE INVENTION According to the present invention, a process for regenerating spent fixer solution includes the steps of adding finely paniculate zinc to the solution to cause silver dissolved therein to precipitate and removing the precipitate from the solution thereby producing a regenerated fixer solution. DESCRIPTION OF THE DRAWING The drawing illustrates graphically the effect of varying quantities of solid zinc bromide dissolved in fixer solution on the performance thereof. DESCRIPTION OF EMBODIMENTS The spent fixer solution will always contain dissolved silver and may be any described above. Generally the spent fixer solution will be a thiosulphate solution, e.g. an ammonium or sodium thiosulphate solution. The invention has particular application to the regeneration of spent fixer solutions resulting from the processing of black-and-white films. Since the role of fixer solution in the processing of exposed film is to Leach out all silver halide particles from the emulsion that had not been reduced to elemental silver by the developer - since they had not been activated by photons during exposure of the film - the spent fixer contains the silver ions usually as a thiosulphate complex, as well as bromide ions. Fixer solution regeneration and silver recovery with paniculate zinc therefore effectively comprises replacing the silver halide in the fixer solution with zinc halide: 2 Ag + + Zn(s) - 2 Ag(s) + Zn 2 * The amount of paniculate zinc used, particularly if of the fraction known in the industry as ultrafme zinc dust, should not be in too large an excess. For the excess will first reduce any dissolved air derived oxygen and thereafter may slowly react with the water to release bubbles of hydrogen gas, which may adhere to silver panicles and give them sufficient buoyancy to prevent their ready settling out. The stoichiometric amount of zinc metal required to precipitate one gram of silver is just over 0,3g. In practice, the amount of zinc dust required may be conveniently taken as about lg of Zn per every 3 of Ag present in the fixer solution to be regenerated. At the completion of this heterogeneous reaction, residual zinc metal is not expected to react with any of the ingredients of the fixer solution. Thus, the mass of zinc added will typically be 0,30 to 0,35 the mass of silver present in the spent fixer solution. The paniculate zinc preferably has a panicle size less than 10 microns, more preferably a particle size less than about 8 microns, most preferably a particle size less than about 4 microns. A suitable fraction is that known in the an as the fme zinc fraction or zinc mining dust, of paniculate size range 4 to 8 microns; but more suitable is that known in the an as ultrafme zinc dust, of panicle size range 2 to 4 microns. An important advantage of the process of the invention is that the finely divided silver displaced by the zinc dust carries down with it the bulk of the gelatin released into the spent fixer solution as the silver halide is dissolved. As a result, there is no appreciable build-up of gelatin in repeatedly regenerated fixer solution and, as consequence, no problems of sludge formation in storage tanks or in the fixer tank of the processing equipment are experienced. Also absent are slimy deposits on film or on the rollers of processors. Removal of the precipitated silver from the solution may be achieved by meύiods known in the an. One such method is filtration. Alternatively, and preferably, the precipitated zinc forms a sludge, me sludge is allowed to settle out of the solution forming a supernatant and the supernatant is separated from the sludge. - 6 - When a silver sludge is formed and separated, it may be washed with water only before drying. The product is obtained as fairly hard lumps, which require milling down before mixing with a flux and smelting can proceed. However, mixing the sludge with a hot, moderately concentrated sodium hydroxide solution and setting the mixtuie aside for a few minutes, dissolves and/or destroys the gelatin. Residual zinc and zinc oxide are also dissolved. Subsequent washing with water and drying produces a powder consisting of essentially pure silver. Treatment of the recovered solids substantially to eliminate co-separated gelatin may be done by suspending the solids in a solution, preferably a hot solution, of caustic soda, for example, a 10 percent (m/v) caustic soda solution at a temperature of about 60° C, decanting the liquid after the solids have settled out, washing the solids two or three times by decantation with water, and drying. The regenerated fixer solution may be used as such. If pH adjustment is desired or necessary, then this may be achieved by addition of a suitable acid such as acetic acid. An example of a suitable acid is glacial acetic acid. Anti-oxidant additives such as sodium sulphite may also have to be replenished. Advantages of the process of the invention include the following: (a) No bad or noxious odours are generated by the process. (b) Because of the above, and the fact that the reaction is completed in such a relatively shon interval, regeneration of the spent fixer solution may be conveniently done at source, such as at hospitals, e.g. by carrying out the processing in, for example, 210 litre plastic drums or larger plastic tanks each mounted on a stand to facilitate drawing off of the regenerated fixer solution. Expensive transportation between source and a central processing facility may therefore be avoided. (c) Throughput of the process of the invention is determined by the size of the containers used. With plastic drums and relatively small processing tanks, hand-stiπing is adequate. Capital investment in equipment is therefore modest. (d) The fixer solution may be safely regenerated and re-used over at least 5 to 10 cycles or more, depending on the degree of developer carryover. (e) The shelf-life of film (e.g. x-ray film) processed using inter alia the regenerated fixer o the invention is comparable with that of film processed with the use of virgin fixer, as is shown in die Examples. After the last cycle of use, and silver recovery, the "exhausted" fixer solution may be passed on to a producer of liquid fertiliser to utilise the fertiliser values of the ammonium thiosulphate and zinc. Use of the process ofthe invendon will, of course, lead to a large reduction in the volume for disposal of this environmentally unfriendly material, and its use in fertiliser mixtures will eliminate spent fixer solution as a source of pollution. The invention will now be illustrated by die following examples. EXAMPLE I In 50ml aliquots of ready-to-use virgin fixer solution were dissolved varying quantities of solid zinc bromide, and die solutions each diluted to 100ml. A strip of green x-ray film was immersed in each of these zinc bromide containing fixer solutions, one at a time. While d e strip of green film was gendy agitated, the time was observed for die silver bromide to be cleared away from the film. Curve A of Figure 1 shows that, provided the zinc bromide in me fixer solution did not exceed about 2 percent, there was no significant increase in die time taken for the solution to dissolve away completely the silver bromide over that where no zinc bromide was dissolved into die fixer solution before the two-fold dilution. EXAMPLE 2 The set of experiments in Example 1 was repeated, this time using aliquots of fixer concentrate (from me same supplier), and diluting to the concentration of ready-to-use fixer solution after die varying quantities of solid zinc bromide had been dissolved in the various aliquots. Curve B of Figure 1 shows dm me time taken to clear strips of green x-ray film was (a) about 5 seconds with no dissolved zinc bromide, (b) still about 5 seconds with 5 percent zinc bromide, and (c) about 7 to 8 seconds with 10 percent dissolved zinc bromide. Calculations show that 2, 5 and 10 percent of dissolved zinc bromide would translate into respectively about 4, 10 and 20 cycles of regeneraύon/re-use if the mean silver content of die fixer is taken as 4,5g/l at d e end of a cycle. EXAMPLE 3 A field trial was conducted in the radiology department of the Clinic of die Columbus Stainless Steel Joint Venture in Middelburg, Mpumalanga Province. Seventy-five litres of spent fixer solution were treated in a 100 litre plastic tank by addition of portions of zinc dust (of the ultra-fine dust fraction, supplied by Zinchem (Pty) Limited, of Benoni) and hand-stirring for 15 minutes at a time until a small amount of filtrate of the mixture gave a white (as opposed to a brown to black) precipitate when treated with a few drops of a 10 percent sodium sulphide solution. This showed that silver precipitation was complete. The clear mother liquid was siphoned off after allowing the mixture to stand overnight thus producing a regenerated fixer solution. The regenerated fixer solution was thereafter separately re-used four times, with regeneration after each cycle, but wi i no attempt being made to adjust me pH or replenish any of die additives. The silver content of the spent fixer during the trial varied between about 4 and 5g/l. No change in the action of the repeatedly re-cycled fixer solution or the quality of the x-ray film images over the entire course of the 7 month trial was reported. EXAMPLE 4 A similar field trial to that described in Example 3 was conducted over a three month period at Rand Mutual Hospital, the principal Johannesburg hospital serving the South African mining industry. A quantity of 125 litres of fixer solution was used in isolation with one of its x-ray film processors and repeatedly regenerated, about 60 litres at a time, until the mean number of cycles of regeneration and re-use amounted to between 4 and 5. The silver sludge was left at the bottom of the processing tank throughout the trials. The silver content of the spent fixer solution processed varied between about 4 and 7g/l. The fixer soluuon in ie circuit gradually picked up a light yellow-brown colour. No attempt was made throughout these trials to replenish any of die fixer additives. The pH required adjustment with glacial acetic acid on one occasion. Again, during die entire course of the trials no difference between the performance of the regenerated fixer solution or ie quality of die x-ray film images and those of the adjacent line using only virgin fixer solution could be detected. EXAMPLE 5 To test the shelf-life of the film treated inter alia with repeatedly regenerated fixer solution, an x-ray film processed with regenerated fixer solution at me end of the trials described in Example 4 was subjected to the standard "Light Fastness Test" , STM 405, by die Souϋi African Bureau of Standards, using film processed with virgin fixer solution as the control. The test comprises irradiating portions of film with die UV light from a Xenon lamp in a chamber at 63 °C and a relative humidity of 30 percent. After about 200 hours' irradiation bom samples started to show a very slight yellow coloration. At the end of die test, i.e. after 300 hours' irradiation. the yellow colouring had not noticeably intensified and was similar for test sample and control. The colouring was adjudged as "not significant". The SABS repon described the accelerated ageing test as equivalent to at least 5 years of natural ageing. EXAMPLE 6 A similar field trial to Uiat described in Example 4 was conducted at d e H.F. Verwoerd Hospital in Pretoria. The fixer from three processing units was combined as an isolated unit and repeatedly regenerated in accordance wid the process of die invention, using a 210 litre plastic drum with an open top. The volume of fixer in the system was about 275 litres. Over the 14 week trial about 2 525 litres of regenerated fixer were produced, representing about 9 cycles of regeneration and re-use. Again, no additives other than die anti-oxidant sodium sulphite were replenished, and die pH was adjusted wi i acetic acid on only two occasions in the course of me trials. No deterioration in fixer solution performance or quality of film images was observed wid ordinary double-coated medical x-ray film. The silver sludge was again left in d e processing tank ύiroughout the trials. The silver content of die fixer solution varied between about 3 and 6g/l and, after the equipment was serviced, between about 4 and 6g/l.

Claims: CLAIMS 1. A process for regenerating spent fixer solution includes die steps of adding finely paniculate zinc to the solution to cause silver dissolved therein to precipitate and removing the precipitate from the solution thereby producing a regenerated fixer solution. 2. A process according to claim 1 wherein d e finely paniculate zinc forms a mixture with the solution and the mixture is agitated. 3. A process according to claim 1 or claim 2 wherein die zinc precipitate is separated from die solution by filtration. 4. A process according to claim 1 or claim 2 wherein the precipitated zinc forms a sludge, the sludge is allowed to settle out of the solution forming a supernatant and the supernatant is separated from the sludge. 5. A process according to any one of die preceding claims wherein die paniculate zinc has a panicle size less dun 10 microns. 6. A process according to any one of claims 1 to 4 wherein the paniculate zinc has a pa icle size of less dian 8 microns. 7. A process according to any one of claims 1 to 4 wherein the zinc dust has a size in die range 4 to 8 microns. 8. A process according to any one of claims 1 to 4 wherein the paniculate zinc has a size in die range 2 to 4 microns. 9. A process according to any one of die preceding claims wherein the mass of zinc added is 0,3 to 0,35 die mass of silver present in the spent fixer solution. 10. A process according to any one of the preceding claims wherein he spent fixer solution is a thiosulphate solution. 11. A process according to claim 1 substantially as herein described with reference to any one of die Examples.

Inventors: SMIT JAKOB VAN ROUENDAL, SMIT, JAKOB VAN ROUENDAL
Applicants: SCIARONE MARCEL, SMIT JAKOB VAN ROUENDAL, SCIARONE, MARCEL, SMIT, JAKOB VAN ROUENDAL
Application year: 1997
Main classification: G03C5
IPC codes: C22B3, C22B11, G03C5