IP Library Granted Patent US 8,802,043
Granted Patent B2
US 8,802,043 · App. 13/929,971 · Granted Aug 12, 2014

Method for controlling acidic compounds produced for oxy-combustion processes

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Quick Facts
Patent No.
US 8,802,043
App. No.
13/929,971
Granted
Aug 12, 2014
Kind
B2
Abstract

The present invention relates generally to the field of emissions control and, in particular to a new and useful method and/or system by which to control, treat and/or mitigate various liquid-based acidic compounds that are produced during oxy-combustion (e.g., during a compression step and/or cooling step) from various gaseous acid compounds and/or gaseous acid precursor compounds (e.g., SO x , NO x , etc.). In one embodiment, the present invention relates to a method and/or system by which such one or more liquid-based acid compounds are recycled into the flue gases and/or into one or more of the emissions control and/or flue gas treatment equipment of an oxy-combustion power generation system.

Claims (51)

1. A method for treating one or more acidic compounds generated during an oxy-combustion process, the method comprising the steps of:

(i) generating a flue gas stream as a result of the oxy-combustion of at least one carbonaceous fuel, wherein the flue gas stream contains at least one type of gaseous acid compound and/or gaseous acid precursor compound;

(ii) treating the flue gas stream to remove at least a portion of at least one gaseous acid compound and/or gaseous acid precursor compound present therein via the use of at least one flue gas treatment device;

(iii) subjecting at least a portion of the flue gas stream from Step (ii) to at least one compression step and/or cooling step so as to remove at least one additional gaseous acid compound and/or gaseous acid precursor compound present therein, wherein the compression step and/or cooling step yields a liquid-based acidic waste stream generated as a result of the removal of the at least one additional gaseous acid compound and/or gaseous acid precursor compound and an acid-depleted, or acid-lean, flue gas stream;

(iv) recycling at least a portion of the liquid-based acidic waste stream to the at least one flue gas treatment device of Step (ii) for treatment, or neutralization, therein; and

(v) subjecting the acid-depleted, or acid-lean, flue gas stream to carbon dioxide recovery so as to recover a majority of the carbon dioxide present in the acid-depleted, or acid-lean, flue gas stream prior to the release of a portion of the remaining acid-depleted, or acid-lean, flue gas stream to the atmosphere.

2. The method of claim 1 , wherein the oxy-combustion process is a coal-based oxy combustion process.

3. The method of claim 1 , wherein the oxy-combustion process is a low sulfur coal-based oxy-combustion process.

4. The method of claim 1 , wherein Step (ii) comprises removing SO x via one or more devices selected from wet flue gas desulfurization processes, dry flue gas desulfurization processes, spray-dry scrubbing processes, wet sulfuric acid processes designed to recover commercial quality sulfuric acid, SNOX flue gas desulfurization processes that are designed to remove sulfur dioxide, nitrogen oxides and particulates from flue gases, direct contact cooler-polishing scrubber processes, or a combination of any two or more thereof.

5. The method of claim 1 , wherein the pH of the liquid-based acidic waste stream is between about −1 to about 3.5.

6. The method of claim 1 , wherein the amount of the one or more additional gaseous acid compounds and/or gaseous acid precursor compounds removed in Step (iii) is at least about 50 percent by weight of the total amount of the one or more gaseous acid compounds and/or gaseous acid precursor compounds present in the flue gas stream prior to Step (iii).

7. The method of claim 1 , wherein the at least one additional gaseous acid compound and/or gaseous acid precursor compound removed in Step (iii) is selected from SO x , NO x , hydrogen fluoride, hydrogen chloride, hydrogen bromide, carbon dioxide, sulfur-based acids, hydrochloric acid, hydrofluoric acid, hydrobromic acid, nitric acid, carbonic acid, or mixtures of any two or more thereof.

8. The method of claim 1 , wherein Step (iv) involves recycling at least 50 percent by weight of the liquid-based acidic waste stream from Step (iii) to the at least one flue gas treatment device of Step (ii) for treatment, or neutralization, therein.

9. The method of claim 1 , wherein Step (iv) involves recycling at least 90 percent by weight of the liquid-based acidic waste stream from Step (iii) to the at least one flue gas treatment device of Step (ii) for treatment, or neutralization, therein.

10. The method of claim 1 , wherein the method further comprises send the remaining portion of the liquid-based acidic waste stream from Step (iii) to at least one waste water treatment process via at least one by-pass, or overflow, line.

11. A method for treating one or more acidic compounds generated during an oxy-combustion process, the method comprising the steps of:

(a) generating a flue gas stream as a result of the oxy-combustion of at least one carbonaceous fuel, wherein the flue gas stream contains at least one type of gaseous acid compound and/or gaseous acid precursor compound;

(b) treating the flue gas stream to remove at least a portion of at least one gaseous acid compound and/or gaseous acid precursor compound present therein via the use of at least one flue gas treatment device;

(c) subjecting at least a portion of the flue gas stream from Step (b) to at least one compression step and/or cooling step so as to remove at least one additional gaseous acid compound and/or gaseous acid precursor compound, present therein, wherein the compression step and/or cooling step yields a liquid-based acidic waste stream generated as a result of the removal of the at least one additional gaseous acid compound and/or gaseous acid precursor compound and an acid-depleted, or acid-lean, flue gas stream;

(d) recycling at least a portion of the liquid-based acidic waste stream to the at least one flue gas treatment device of Step (b) for treatment, or neutralization, therein;

(e) subjecting the acid-depleted, or acid-lean, flue gas stream to at least one additional emissions control and/or flue gas treatment technology; and

(f) subjecting the acid-depleted, or acid-lean, flue gas stream to carbon dioxide recovery so as to recover a majority of the carbon dioxide present in the acid-depleted, or acid-lean, flue gas stream prior to the release of a portion of the remaining acid-depleted, or acid-lean, flue gas stream to the atmosphere.

12. The method of claim 11 , wherein the oxy-combustion process is a coal-based oxy combustion process.

13. The method of claim 11 , wherein the oxy-combustion process is a low sulfur coal-based oxy-combustion process.

14. The method of claim 11 , wherein Step (b) comprises removing SO x via one or more devices selected from wet flue gas desulfurization processes, dry flue gas desulfurization processes, spray-dry scrubbing processes, wet sulfuric acid processes designed to recover commercial quality sulfuric acid, SNOX flue gas desulfurization processes that are designed to remove sulfur dioxide, nitrogen oxides and particulates from flue gases, direct contact cooler-polishing scrubber processes, or a combination of any two or more thereof.

15. The method of claim 11 , wherein the pH of the liquid-based acidic waste stream is between about −1 to about 3.5.

16. The method of claim 11 , wherein the amount of the one or more additional gaseous acid compound and/or gaseous acid precursor compound removed in Step (c) is at least about 50 percent by weight of the total amount of the one or more gaseous acid compound and/or gaseous acid precursor compound present in the flue gas stream prior to Step (c).

17. The method of claim 11 , wherein the at least one additional gaseous acid compound and/or gaseous acid precursor compound removed in Step (c) is selected from SO x , NO x , hydrogen fluoride, hydrogen chloride, hydrogen bromide, carbon dioxide, sulfur-based acids, hydrochloric acid, hydrofluoric acid, hydrobromic acid, nitric acid, carbonic acid, or mixtures of any two or more thereof.

18. The method of claim 11 , wherein Step (d) involves recycling at least 50 percent by weight of the liquid-based acidic waste stream from Step (c) to the at least one flue gas treatment device of Step (b) for treatment, or neutralization, therein.

19. The method of claim 11 , wherein the method further comprises send the remaining portion of the liquid-based acidic waste stream from Step (c) to at least one waste water treatment process via at least one by-pass, or overflow, line.

20. The method of claim 11 , wherein the at least one additional emissions control and/or flue gas treatment technology of Step (e) comprises mercury capture via a mercury capture process.

21. A method for treating one or more acidic compounds generated during an oxy-combustion process, the method comprising the steps of:

(I) generating a flue gas stream as a result of the oxy-combustion of at least one carbonaceous fuel, wherein the flue gas stream contains at least one type of gaseous acid compound and/or gaseous acid precursor compound;

(II) treating the flue gas stream to remove at least a portion of at least one gaseous acid compound and/or gaseous acid precursor compound present therein via the use of at least one flue gas treatment device;

(III) subjecting the flue gas stream from Step (II) to at least one compression step and/or cooling step so as to remove at least one additional gaseous acid compound and/or gaseous acid precursor compound present therein, wherein the compression step and/or cooling step yields a liquid-based acidic waste stream generated as a result of the removal of the at least one gaseous acid compound and/or gaseous acid precursor compound and an acid-depleted, or acid-lean, flue gas stream;

(IV) recycling at least a portion of the liquid-based acidic waste stream to the at least one flue gas treatment device of Step (II) for treatment, or neutralization, therein;

(V) subjecting the acid-depleted, or acid-lean, flue gas stream to at least one additional emissions control and/or flue gas treatment technology; and

(VI) subjecting the acid-depleted, or acid-lean, flue gas stream to carbon dioxide recovery so as to recover a majority of the carbon dioxide present in the acid-depleted, or acid-lean, flue gas stream prior to the release of a portion of the remaining acid-depleted, or acid-lean, flue gas stream to the atmosphere,

wherein the liquid-based acidic waste stream is split into at least two liquid-based acidic waste streams, a portion of each split liquid-based waste stream then being subjected to recycling in the at least one flue gas treatment device of Step (II) for treatment, or neutralization, therein.

22. The method of claim 21 , wherein the oxy-combustion process is a coal-based oxy combustion process.

23. The method of claim 21 , wherein the oxy-combustion process is a low sulfur coal-based oxy-combustion process.

24. The method of claim 21 , wherein Step (II) comprises removing SO x via one or more devices selected from wet flue gas desulfurization processes, dry flue gas desulfurization processes, spray-dry scrubbing processes, wet sulfuric acid processes designed to recover commercial quality sulfuric acid, SNOX flue gas desulfurization processes that are designed to remove sulfur dioxide, nitrogen oxides and particulates from flue gases, direct contact cooler-polishing scrubber processes, or a combination of any two or more thereof.

25. The method of claim 21 , wherein the pH of the liquid-based acidic waste stream is between about −1 to about 3.5.

26. The method of claim 21 , wherein the amount of the one or more additional gaseous acid compound and/or gaseous acid precursor compound removed in Step (III) is at least about 50 percent by weight of the total amount of the one or more gaseous acid compound and/or gaseous acid precursor compound present in the flue gas stream prior to Step (III).

27. The method of claim 21 , wherein the at least one additional gaseous acid compound and/or gaseous acid precursor compound removed in Step (III) is selected from SO x , NO x , hydrogen fluoride, hydrogen chloride, hydrogen bromide, carbon dioxide, sulfur-based acids, hydrochloric acid, hydrofluoric acid, hydrobromic acid, nitric acid, carbonic acid, or mixtures of any two or more thereof.

28. The method of claim 21 , wherein Step (IV) involves recycling at least 50 percent by weight of the liquid-based acidic waste stream from Step (III) to the at least one flue gas treatment device of Step (II) for treatment, or neutralization, therein.

29. The method of claim 21 , wherein the method further comprises send the remaining portion of the liquid-based acidic waste stream from Step (III) to at least one waste water treatment process via at least one by-pass, or overflow, line.

30. The method of claim 21 , wherein the at least one additional emissions control and/or flue gas treatment technology of Step (V) comprises mercury capture via a mercury capture process.

31. The method of claim 21 , wherein at least one of the at least two liquid-based acidic waste streams is a low pH stream and at least one of the at least two liquid-based acidic waste streams is a high pH stream.

32. The method of claim 31 , wherein the at least one low pH liquid-based acidic waste stream has a pH of less than about 1.

33. The method of claim 31 , wherein the at least one high pH liquid-based acidic waste stream has a pH of at least about 3.

Assignments (12)
SECURITY INTEREST Recorded Jul 18, 2025
From: BABCOCK & WILCOX ENTERPRISES, INC.; THE BABCOCK & WILCOX COMPANY; DIAMOND POWER INTERNATIONAL, LLC; BABCOCK & WILCOX SPIG, INC.; BABCOCK & WILCOX CANADA CORP.; BABCOCK & WILCOX FPS INC.
To: B. RILEY FINANCIAL, INC.
Reel/Frame 072053/0943 →
SECURITY INTEREST Recorded Mar 3, 2025
From: BABCOCK & WILCOX ENTERPRISES, INC.; THE BABCOCK & WILCOX COMPANY; DIAMOND POWER INTERNATIONAL, LLC; BABCOCK & WILCOX SPIG, INC.; BABCOCK & WILCOX CANADA CORP.; BABCOCK & WILCOX FPS INC.
To: PENSION BENEFIT GUARANTY CORPORATION
Reel/Frame 070380/0647 →
RELEASE OF SECURITY INTEREST Recorded Sep 13, 2024
From: MSD PCOF PARTNERS XLV, LLC
To: THE BABCOCK & WILCOX COMPANY; DIAMOND POWER INTERNATIONAL, LLC; AMERICON LLC
Reel/Frame 069017/0362 →
SECURITY INTEREST Recorded Jan 19, 2024
From: BABCOCK & WILCOX ENTERPRISES, INC.; THE BABCOCK & WILCOX COMPANY; DIAMOND POWER INTERNATIONAL, LLC; BABCOCK & WILCOX SPIG, INC.; BABCOCK & WILCOX CANADA CORP.; BABCOCK & WILCOX FPS INC.
To: AXOS BANK, AS ADMINISTRATIVE AGENT
Reel/Frame 066354/0765 →
SECURITY INTEREST Recorded Jul 22, 2021
From: THE BABCOCK & WILCOX COMPANY (F/K/A BABCOCK & WILCOX POWER GENERATION GROUP, INC.); BABCOCK & WILCOX SPIG, INC.; BABCOCK & WILCOX TECHNOLOGY, LLC; DIAMOND POWER INTERNATIONAL, LLC (F/K/A DIAMOND POWER INTERNATIONAL, INC.)
To: MSD PCOF PARTNERS XLV, LLC, AS AGENT
Reel/Frame 056962/0486 →
RELEASE OF SECURITY INTEREST Recorded Jul 1, 2021
From: BANK OF AMERICA, N.A.
To: DIAMOND POWER INTERNATIONAL, LLC (F/K/A DIAMOND POWER INTERNATIONAL, INC.); MEGTEC TURBOSONIC TECHNOLOGIES, INC.; THE BABCOCK & WILCOX COMPANY (F/K/A BABCOCK & WILCOX POWER GENERATION GROUP, INC.); BABCOCK & WILCOX SPIG, INC.; BABCOCK & WILCOX TECHNOLOGY, LLC (F/K/A MCDERMOTT TECHNOLOGY, INC.); SOFCO-EFS HOLDINGS LLC; BABCOCK & WILCOX MEGTEC, LLC
Reel/Frame 057337/0823 →
RELEASE OF SECURITY INTEREST Recorded May 17, 2018
From: LIGHTSHIP CAPITAL LLC
To: BABCOCK & WILCOX ENTERPRISES, INC.; THE BABCOCK & WILCOX COMPANY; DIAMOND POWER INTERNATIONAL, LLC; BABCOCK & WILCOX MEGTEC, LLC; MEGTEC TURBOSONIC TECHNOLOGIES, INC.; BABCOCK & WILCOX UNIVERSAL, INC.; BABCOCK & WILCOX TECHNOLOGY, LLC
Reel/Frame 046182/0829 →
SECURITY INTEREST Recorded Aug 10, 2017
From: THE BABCOCK & WILCOX COMPANY; DIAMOND POWER INTERNATIONAL, LLC; BABCOCK & WILCOX MEGTEC, LLC; MEGTEC TURBOSONIC TECHNOLOGIES, INC.; BABCOCK & WILCOX UNIVERSAL, INC.; BABCOCK & WILCOX TECHNOLOGY, LLC
To: LIGHTSHIP CAPITAL LLC
Reel/Frame 043515/0001 →
CHANGE OF NAME Recorded Sep 24, 2015
From: BABCOCK & WILCOX POWER GENERATION GROUP, INC.
To: THE BABCOCK & WILCOX COMPANY
Reel/Frame 036675/0434 →
SECURITY INTEREST Recorded Jul 28, 2015
From: BABCOCK & WILCOX POWER GENERATION GROUP, INC. (TO BE RENAMED THE BABCOCK AND WILCOX COMPANY)
To: BANK OF AMERICA, N.A., AS ADMINISTRATIVE AGENT
Reel/Frame 036201/0598 →
SECURITY INTEREST Recorded Jul 22, 2014
From: BABCOCK & WILCOX POWER GENERATION GROUP, INC.
To: BANK OF AMERICA, N.A., AS ADMINISTRATIVE AGENT
Reel/Frame 033380/0744 →
ASSIGNMENT OF ASSIGNOR'S INTEREST Recorded Jul 1, 2014
From: MCDONALD, DENNIS K
To: BABCOCK & WILCOX POWER GENERATION GROUP, INC.
Reel/Frame 033222/0878 →