United States Patent ['19] [11] 3,929,968 Taub _ I I [451 Dec. 30, 1975 [54] DRY COLLECTION OF WASTE 3,785,119 l/l974 Mcllvaine ......................... .. 423/242 MATERIALS FOREIGN PATENTS OR APPLICATIONS [75] Inventor: Steven I. Taub, Claymont, Del. 510,415 4/1952 Belgium ............................ .. 423/242 [73] Assignee: E. I. Du Pont de Nemours & Co., Wilmington, Del. Primary Examiner-Oscar R. Vertiz Assistant Examiner—-Gregory A. Heller [22] Filed: on. 10, 1973 [21] Appl. No.: 405,054 [57] ABSTRACT The noxious components of hot, gaseous ef?uents, [52] U.S. Cl ................................ .. 423/242; 423/240 e.g., the ef?uent from an incinerator, can be elimi [51] Int. Cl.2 ........................................ .. C01B 17/00 nated by a process which does not require an aqueous [58] Field of Search .......................... .. 423/242-244, discharge. In the process the gaseous ef?uent is cooled 423/240, 241 in an evaporative cooler, particulates are then re moved in a baghouse or other dry collecting device, [56] References Cited the acid or basic gases in the effluent are then ab UNITED STATES PATENTS sorbed and converted to a salt solution or slurry in a 2,333,193 11/1943 Persson et al ..................... .. 423/242 scrubber, and the salt solution or slurry is recycled to 2,375,560 5/1945 Hutchinson et al . .. 423/242 the evaporative cooler. 3,343,908 9/1967 Wickert . .. 423/244 3,687,623 8/1972 Terrana et al. ................... .. 423/242 7 Claims, 2 Drawing Figures 3,929,968 1 2 DRY COLLECTION or WASTE-MATERIALS DESCRIPTION OF THE DRAWINGS FIG. 1 is a flow diagram of an embodiment of the BACKGROUND OF THE INVENTION process of the invention. The removal of undesirable components from the 5 FIG. 2 illustrates an alternate embodiment particu environment is of considerable importance to our soci larly designed for the recovery of a gaseous compo ety. Many industries and municipalities employ inciner nent, e.g., S0,, from the hot gas stream. ators to eliminate undesired organics, organo-metallic compounds, halogenated organics, etc. However, the DESCRIPTION OF THE INVENTION noxious materials formed as a result of incineration or The process of the invention is useful to treat any hot other hot gaseous processes must be eliminated by ?ue process gases, i.e., gases at temperatures above gas cleaning techniques. These techniques employ bag 250°—350°F., which contain particulate and gaseous filters, electrostatic precipitators, scrubbers, cyclones, acidic or basic pollutants. and packed beds to remove the particulate’ pollutants The particulates can be anything collectable by a dry from the flue gases and scrubbers to minimize the nox collector, e.g., dust, ?y ash, carbon, salts, metal oxides ious gaseous effluents. and the like. The ‘gaseous acidic pollutants include the A problem has arisen with respect to the use of scrub following acid gases, e.g., gases containing HCl, 80;, bers as a pollution control tool. The scrubber liquid HBr, N02, HNO3, HF, Cl2, Brz or P205. The gaseous blow-down can cause serious water pollution problems. gasic pollutants can include NH3, or metallic fumes If the scrubber effluent contains solid particulates, they 20 such as NaOH, Mg(OH )2 and the like. can be filtered and removed. Some metallic wastes may The process will now be explained with reference to settle out or they may be precipitated from solution by FIG. 1. q pH adjustment. However, these treatments are expen The hot process gas 1 containing the gaseous acidic sive and water discharge can become a problem when or basic components and the particulates is fed into an soluble salts or acids in addition to solids are entrained 25 evaporative cooler 2 wherein the gas is cooled to a in the scrubber effluent. temperature above the dew point, generally between SUMMARY OF THE INVENTION 250° and l,0O0°F., preferably 400° and 450°F. The evaporative cooler acts to cool the hot gas and I have discovered a total waste disposal system which also evaporate the purge 3 of adjusted scrubbing solu will eliminate the usual problems caused with the use of tion from the scrubber 4. In operation the hot gases scrubbers to cleanse gases. entering the cooler entrain the liquid droplets and solid The process of the invention is useful for treating hot particulates in the purge and the liquid is evaporated. gas streams to eliminate undesirable components and The evaporative cooler could be a spray dryer or a gas involves the following steps: 1 cooler wherein the liquid is atomized by a rotating disc 'a. feeding a hot gas stream containing particulates 35 or a spray nozzle or other means. Some solids may and gaseous acidic or basic components into an evapo collect in the bottom of the cooler and they can be rative cooler wherein the gas is cooled to a temperature discharged at appropriate times as stream 18. above the dew point, generally between 250° and The operating conditions for the evaporative cooler 1,000°F.; ' ' > Y will vary depending upon the nature of the hot gas and b. feeding the cooled gas stream into a collection v40 purge‘ feeds. One critical feature is that the hot gas is means for the dry collection of the particulates present maintained at a temperature above the dew point. in the gas stream; It is important that the evaporative cooler be able to c. feeding the gas stream from step (b) into a scrub control outlet gas temperature very effectively. If it ber wherein the stream is contacted with an aqueous cannot, serious damage to process equipment down scrubbing solution to absorb the acidic or basic compo 45 stream of the cooler’ may occur. For example, if the nents, the scrubber will also remove any particulates process of the invention was to control the discharge of that passed through the collection means; a waste incinerator and a baghouse was chosen as the d. removing the scrubbed gas stream from the scrub particulate collection means, damage to the baghouse ‘oer; ’ could take place if the evaporative cooler is not able to e. adjusting the pH of the scrubbing solution by the 50 respond quickly to changes in burning rate, gas temper addition of sufficient salt forming chemical to form a ature, or both. If the temperature of the inlet gas stream salt, either water soluble or insoluble, with the ab~ were to suddenly drop and the evaporative cooler was sorbed acidic or basic component; and slow in responding, the baghouse bag ?lters could be f. feeding ‘the adjusted scrubbing solution or slurry come coated with mud. If the temperature were to containing the salt to the evaporative cooler where it is 55 increase suddenly, and the evaporative cooler was not combined and heated with the hot gas, the salt subse able to respond quickly, the bag filters in the baghouse quently being collected as a dry solid in the evaporative could be burned. For these: reasons, the evaporative cooler or the collection means of step (b), most or all of cooler must be capable of fast response. the salt being collected in means (b). , The cooled gas stream 5 leaving the cooler 2 contains Preferably, the process of the invention is used to the original gaseous acidic or basic components and treat hot, acidic gases and the salt produced is water essentially all of the particulates and also the salt, as a soluble. particulate, released by the evaporation of the adjusted The principal advantage of the process of the inven scrubbing solution 3. The cooled gas stream is fed into tion is that it does not involve any aqueous discharge, a dry collection means 6 wherein the particulates are i.e., the scrubber effluent is fed to the evaporative 65 removed. The dry collection means can be any of those cooler where the water vaporizes and theparticulates commercially used, i.e., a baghouse containing bag are collected as dry solids. Thus, the only non-gaseous filters, electrostatic precipitators, cyclones or packed discharge from the process is a dry solid. beds. This collection means will be operated in the 3,929,968 3 4 conventional manner. The solids collected in this fed into the evaporative cooler 2 as previously de means are discharged as stream 19. _ scribed. In the cooler the water in the purge 3 is vapor The essentially particulate free gas 7 is then fed into ized and the saltis collected in the bottom of the cooler a scrubber 4 wherein the water soluble acidic and basic 2 or the dry collector 6. components of the gas are absorbed in an aqueous In the embodiment illustrated in FIG. 2, two alterna scrubbing solution. This scrubber will also collect any tives are employed. particulates that passed through the dry collection The recycling scrubbing solution 8 does not contain means. The operating conditions in the scrubber as to any s'alt former; the salt former 12 is added only to the temperatures, pressures and contact time will vary purge and in an amount sufficient to convert all the depending upon the makeup of the gas stream 7. How water soluble acidic or basic material present in the ever, these conditions will be conventional and appar purge into a ‘salt; however, if desired, an excess of salt ent to those skilled in the art. former can be employed. In the scrubber illustrated in FIG. 1, the gas 7 is fed Furthermore, this embodiment permits the recovery into the scrubber 4 wherein it flows either- countercur of gaseous components that are not absorbed by the rent, cocurrent or cross flow to the aqueous scrubbing 15 water in the scrubber, i.e., under most operating condi solution 8 which is fed into the scrubber.