Method for producing oxide layer material in landfill field for treating methane gas by using household refuse
US-2017266616-A1 · Sep 21, 2017 · US
US10195564B2 · US · B2
| Field | Value |
|---|---|
| Publication number | US-10195564-B2 |
| Application number | US-201615088094-A |
| Country | US |
| Kind code | B2 |
| Filing date | Mar 31, 2016 |
| Priority date | Apr 8, 2015 |
| Publication date | Feb 5, 2019 |
| Grant date | Feb 5, 2019 |
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The present invention relates to a process of conversion of waste streams of petroleum refinery into industrially useful products.
Opening claim text (preview).
We claim: 1. A process of converting refinery waste streams comprising spent caustic into nano-sized carbonates, comprising the steps of: (a) mixing the refinery waste stream comprising spent caustic in a stirred reactor containing carbonic anhydrase, which is obtained from the microbe selected from Enterobacter aerogenes (MTCC 25016), Lysinibacillus sp. (MTCC 25029), Bacillus thermoleovorans (MTCC 25023), Bacillus stearothermophilus (MTCC 25030) or Arthrobacter sp. (MTCC 25028); (b) adding a brine solution to the mixture of step (a); (c) sparging a carbon dioxide rich gas to the mixture of step (b); (d) allowing the components introduced in (a)-(c) to react for a sufficient time and at a sufficient concentration to form a nano-sized carbonate precipitate; (e) separating the aqueous/liquid phase to obtain precipitated nano-sized carbonate; (f) treating the aqueous/liquid phase with a microbial consortia selected from a mixture of any one of Pseudomonas putida (MTCC 5869), Bacillus substilis (MTCC 5386), Pseudomonas aeruginosa (MTCC 5389), Peudomonas aerugiosa (MTCC 5388) and Lysinibacillus sp. (MTCC 5666) for a sufficient time and at a sufficient concentration to remove contaminants; and (g) obtaining a aqueous phase free of contaminants. 2. The process as claimed in claim 1 , wherein the carbonic anhydrase is at a concentration in the range of 2-20 units/ml of the reaction mixture and is capable of withstanding: i) a pH above 10, ii) salinity in the range of 0.1-10% and iii) temperatures above 80° C. 3. The process as claimed in claim 1 , wherein the source of carbon dioxide rich gas is selected from flue gas or bio-gas plant exhaust. 4. The process as claimed in claim 1 , wherein the brine solution is obtained from sources selected from crude oil-desalter unit, produced water, reverse osmosis plant reject, or cooling tower blow down. 5. The process as claimed in claim 1 , wherein the ratio of spent caustic in the refinery waste stream and brine solution is in the range of 1:1 to 1:0.10. 6. The process as claimed in claim 1 , wherein the process in steps (a) to (d) are carried out at a temperature in the range of 25-85° C. for 0.5-30 minutes. 7. The process as claimed in claim 1 , wherein the carbonic anhydrase may be immobilized in the immobilization agents selected from carbon nanotubes, metal organic framework, zeolites, Zinc-ferrite, nickel ferrite, Zinc-nickel (Zn—Ni) ferrite, polyurethane, glass beads or any other suitable matrixes. 8. The process as claimed in claim 1 , wherein step (f) is carried out at a temperature in the range of 20-60° C. and stirring of the reaction is carried in range of 200-600 rpm. 9. The process as claimed in claim 1 , wherein the total dissolved solids in brine solution in the range of 10 ppm to 100000 ppm. 10. The process as claimed in claim 1 , wherein the nano-sized carbonate has a particle size in the range of 50-100 nm. 11. The process as claimed in claim 1 , wherein the treated aqueous/liquid phase or the spent caustic has more than 98% reduction in sulphides, phenols, hydrocarbons, naphthenic acid, thiols, mercaptans or other contaminants. 12. A process of converting refinery waste streams comprising spent caustic into nano-sized carbonates, said process comprising the steps of: (a) mixing the refinery waste in a stirred reactor containing carbonic anhydrase, wherein the carbonic anhydrase is obtained from microbes selected from Enterobacter aerogenes (MTCC 25016), Lysinibacillus sp. (MTCC 25029), Bacillus thermoleovorans (MTCC 25023), Bacillus stearothermophilus (MTCC 25030) or Arthrobacter sp. (MTCC 25028); (b) adding a brine solution to the mixture of step (a); (c) sparging a carbon dioxide rich gas to the mixture of step (b); (d) allowing the components introduced in (a)-(c) to react for a sufficient time and at a sufficient concentration to form a nano-sized carbonate precipitate; and (e) recovering precipitated nano-sized carbonates. 13. The process as claimed in claim 12 , wherein the carbonic anhydrase is at a concentration in the range of 2-20 units/ml of the reaction mixture and is capable of withstanding: i) a pH above 10, ii) salinity in the range of 0.1-10% and iii) temperatures above 80° C. 14. The process as claimed in claim 12 , wherein the source of carbon dioxide rich gas is selected from flue gas or bio-gas plant exhaust. 15. The process as claimed in claim 12 , wherein the brine solution is obtained from sources selected from crude oil-desalter unit, produced water, reverse osmosis plant reject or cooling tower blow down. 16. The process as claimed in claim 12 , wherein the ratio of spent caustic in the refinery waste stream and brine solution is in the range of 1:1 to 1:0.10. 17. The process as claimed in claim 12 , wherein the process in steps (a)-(d) are carried out at a temperature in the range of 25-85° C. for 0.5-30 minutes. 18. The process as claimed in claim 12 , wherein the biocatalyst in steps (a)-(d) may be immobilized in the immobilization agents selected from carbon nanotubes, metal organic framework, zeolites, Zinc-ferrite, nickel ferrite, Zinc-nickel (Zn—Ni) ferrite, polyurethane, glass beads or any other suitable matrixes.
Recovery of used refining agents · CPC title
from quarries or from mining activities · CPC title
characterised by the enzymes used · CPC title
Specific microorganisms · CPC title
Enzymatic · CPC title
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