US2002100367A1PendingUtilityA1

Process to prepare adsorbents from organic fertilizer and their applications for removal of acidic gases from wet air streams

Assignee: UNIV CITYPriority: Nov 29, 2000Filed: Nov 29, 2001Published: Aug 1, 2002
Est. expiryNov 29, 2020(expired)· nominal 20-yr term from priority
B01J 20/24B01D 2257/408B01D 2257/302B01J 20/28057B01J 2220/42B01J 20/0229Y10T428/2982B01D 2253/10B01J 20/20B01D 53/8612B01D 2257/404B01J 20/28071B01J 20/3078B01J 20/28069B01J 20/0237B01J 20/08B01J 20/30B01J 20/041B01D 2253/102B01D 53/1456B01D 53/02B01D 2257/304B01J 20/103B01J 20/22B01J 20/28061B01J 20/2808B01J 2220/4887B01J 20/0244
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Claims

Abstract

The invention is directed to an adsorbent comprising: a) 20-30% porous carbon with incorporated organic nitrogen species; and b) 70-80% inorganic matter. The invention is directed to a method of making an adsorbent which comprises: a) thermally drying dewatered sewage sludge to form granulated organic fertilizer; and b) pyrolyzing said the organic fertilizer at temperatures between 600 and 1000° C. The invention is additionally directed to the process of removing acidic gases from wet air streams comprising putting an adsorbent in contact with the wet air stream and allowing the adsorbent to adsorb the acidic gases.

Claims

exact text as granted — not AI-modified
What is claimed is:  
     
         1 . An adsorbent comprising: 
 a) 20-30% porous carbon with incorporated organic nitrogen species; and    b) 70-80% inorganic matter.    
     
     
         2 . The adsorbent of  claim 1 , wherein the inorganic matter includes highly dispersed catalytic oxides.  
     
     
         3 . The adsorbent of  claim 2 , wherein the catalytic oxides are one or more of copper oxide, zinc oxide, iron oxide, calcium oxide, silica and alumina.  
     
     
         4 . The adsorbent of  claim 1 , wherein the nitrogen species comprises amine or pyridine groups.  
     
     
         5 . The adsorbent of  claim 1 , wherein the surface area of the adsorbent is 100-500 m 2 /g.  
     
     
         6 . The adsorbent of  claim 5 , wherein the surface area of the adsorbent is 100-200 m 2 /g.  
     
     
         7 . The adsorbent of  claim 1 , wherein the adsorbent contains micropores and the volume of the micropores are at least 0.03 cm 3 /g.  
     
     
         8 . The adsorbent of  claim 1 , wherein the pH of the adsorbent is greater than 10.  
     
     
         9 . The adsorbent of  claim 1 , wherein the pH of the adsorbent is between 7 and 10.  
     
     
         10 . The adsorbent of  claim 1 , wherein the pH of the adsorbent is between 4 and 7.  
     
     
         11 . A method of making an adsorbent which comprises: 
 a) thermally drying dewatered sewage sludge to form granulated organic fertilizer; and    b) pyrolyzing said the organic fertilizer at temperatures between 600 and 1000° C.    
     
     
         12 . The method of  claim 11 , wherein the heating rate is between 5 and 10° C./minute and the hold time is between 60 and 90 minutes.  
     
     
         13 . The method of  claim 11 , wherein the temperature of pyrolysis is between 800 and 1000° C.  
     
     
         14 . The method of  claim 13 , wherein the temperature of pyrolysis is between 900 and 1000° C.  
     
     
         15 . The method of  claim 11 , wherein the temperature of pyrolysis is between 600 and 900° C. and the adsorbent is further treated with 15-20% HCl.  
     
     
         16 . The method of  claim 15 , wherein the temperature of pyrolysis is between 800 and 900° C.  
     
     
         17 . An adsorbent formed by the method of  claim 11 .  
     
     
         18 . The process of removing acidic gases from wet air streams comprising putting an adsorbent comprising 20-30% porous carbon with incorporated organic nitrogen species and 70-80% inorganic matter in contact with the wet air stream and allowing the adsorbent to adsorb the acidic gases.  
     
     
         19 . The process of  claim 18 , wherein the acidic gases are one or more of hydrogen sulfide, sulfur dioxide, hydrogen cyanide, and nitrogen dioxide.  
     
     
         20 . The process of  claim 18 , wherein the acidic gas is hydrogen sulfide which reacts with inorganic matter to be oxidized to sulfur dioxide or elemental sulfur and salt forms thereof.  
     
     
         21 . The process of  claim 18 , wherein the wet air stream is effluent from a sewage treatment plant, gaseous fuel, or gases from hydrothermal vents.  
     
     
         22 . The process of removing acidic gases from wet air streams comprising forming an adsorbent by thermally drying dewatered sewage sludge to form granulated organic fertilizer and pyrolyzing said organic fertilizer at temperatures between 600-1000° C., putting said adsorbent in contact with the wet air stream, and allowing the adsorbent to adsorb the acidic gases.  
     
     
         23 . The process of  claim 22 , wherein the acidic gases are one or more of hydrogen sulfide, sulfur dioxide, hydrogen cyanide, and nitrogen dioxide.  
     
     
         24 . The process of  claim 22 , wherein the temperature of pyrolysis is between 800 and 1000° C.  
     
     
         25 . The process of  claim 24 , wherein the temperature of pyrolysis is between 900 and 1000° C.  
     
     
         26 . The process of  claim 22 , wherein the temperature of pyrolysis is between 600 and 900° C. and the adsorbent is further treated with 15-20% HCl.  
     
     
         27 . The process of  claim 26 , wherein the temperature of pyrolysis is between 800 and 900° C.  
     
     
         28 . The process of  claim 22 , wherein the adsorbent may be regenerated by heating to 300-500° C. to remove elemental sulfur and sulfur dioxide.

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