IP Library Granted Patent US 8,480,983
Granted Patent B1
US 8,480,983 · App. 13/421,413 · Granted Jul 9, 2013

Mercury capture system and method for a wet flue gas desulfurization system

View Patent ↗
Loading inventors, assignments & file history…
Monitor This Case
Get email alerts when status or documents change.
Order Certified Copies
Most orders are placed with the USPTO same day — all within 24 business hours.
Order via The Patent Place →
Pre-filled with this patent's details
Quick Facts
Patent No.
US 8,480,983
App. No.
13/421,413
Granted
Jul 9, 2013
Kind
B1
Abstract

A wet flue gas desulfurization (WFGD) system includes an absorber vessel operable to remove pollutants from flue gas supplied thereto. The absorber vessel defines a slurry section for containing a reagent slurry therein and an outlet in fluid communication with the slurry section. The WFGD system includes a mercury removal vessel in fluid communication with outlet. The mercury removal vessel has activated carbon disposed therein.

Claims (39)

1. A wet flue gas desulfurization system comprising:

an absorber vessel operable to remove pollutants from flue gas supplied thereto, the absorber vessel defining a slurry section for containing a reagent slurry and an outlet in fluid communication with the slurry section; and

a mercury removal vessel in fluid communication with the outlet and the mercury removal vessel having activated carbon disposed therein.

2. The wet flue gas desulfurization system of claim 1 , wherein the activated carbon is disposed in the mercury removal vessel in at least one of a pile, a moving bed, a fluidized bed, and mixed in with the mercury-rich effluent.

3. The wet flue gas desulfurization system of claim 1 , wherein the activated carbon is operable to remove substantially all mercury from the reagent slurry received in the mercury removal vessel.

4. The wet flue gas desulfurization system of claim 1 , wherein the activated carbon is in at least one of pebble and granular form.

5. The wet flue gas desulfurization system of claim 1 , wherein the mercury removal vessel is removably positioned in the wet flue gas desulfurization system.

6. The wet flue gas desulfurization system of claim 1 , wherein the mercury removal vessel defines an outlet, which is in fluid communication with the absorber vessel.

7. A method of operating a wet flue gas desulfurization system, including:

providing an absorber vessel defining a slurry section for containing a reagent slurry and an outlet in fluid communication with the slurry section, the outlet in fluid communication with a mercury removal vessel, the mercury removal vessel having activated carbon disposed therein;

supplying a reagent and water to the absorber vessel;

flowing flue gas containing mercury into the absorber vessel;

the reagent slurry absorbing the mercury creating a mercury-rich reagent slurry;

supplying a portion of the mercury-rich reagent slurry to the mercury removal vessel; and

adsorbing the mercury from the mercury-rich reagent with the activated carbon disposed in the mercury removal vessel thereby producing treated reagent slurry.

8. The method of claim 7 , wherein the treated reagent slurry is supplied to the absorber vessel.

9. The method of claim 7 , wherein the activated carbon is disposed in the mercury removal vessel in at least one of a pile, a moving bed, a fluidized bed, and mixed in with the mercury-rich effluent.

10. A wet flue gas desulfurization system comprising:

an absorber vessel operable to remove pollutants from flue gas supplied thereto, the absorber vessel defining a slurry section for containing a reagent slurry and an outlet in fluid communication with the slurry section;

a dewatering system in fluid communication with the outlet; and

a mercury removal vessel in fluid communication with and positioned downstream of the dewatering system, the mercury removal vessel having activated carbon disposed therein.

11. The wet flue gas desulfurization system of claim 10 , wherein the activated carbon is disposed in the mercury removal vessel in at least one of a pile, a moving bed, a fluidized bed and mixed in with the mercury-rich effluent.

12. The wet flue gas desulfurization system of claim 10 , wherein the activated carbon is operable to remove substantially all mercury from the reagent slurry received in the mercury removal vessel.

13. The wet flue gas desulfurization system of claim 10 , wherein the activated carbon is in at least one of pebble and granular form.

14. The wet flue gas desulfurization system of claim 10 , wherein the mercury removal vessel is removably positioned in the wet flue gas desulfurization system.

15. The wet flue gas desulfurization system of claim 10 , wherein the mercury removal vessel defines an outlet, which is in fluid communication with the absorber vessel.

16. The wet flue gas desulfurization system of claim 10 , wherein the dewatering system includes a dewatering classifier, a solids transfer vessel, an effluent vessel and a filter, the dewatering classifier is positioned downstream of and is in fluid communication with the absorber vessel, the solids transfer vessel is positioned downstream of and is in fluid communication with the dewatering classifier and the filter is positioned downstream of and is in fluid communication with the solids transfer vessel, the effluent vessel is positioned downstream of and is in fluid communication with the filter and the dewatering classifier and the mercury removal vessel is positioned downstream of and is in fluid communication with the effluent vessel and is in fluid communication with the absorber vessel.

17. A method of operating a wet flue gas desulfurization system, including:

providing an absorber vessel defining a slurry section for containing a reagent slurry and an outlet in fluid communication with the slurry section;

providing a dewatering system in fluid communication with the outlet;

providing a mercury removal vessel in fluid communication with and positioned downstream of the dewatering system, the mercury removal vessel having activated carbon disposed therein;

supplying a reagent and water to the absorber vessel;

flowing flue gas containing mercury into the absorber vessel;

absorption of the mercury to produce a mercury-rich reagent slurry;

supplying a portion of the mercury-rich reagent slurry to the dewatering system to separate solids from the mercury-rich slurry and to produce a mercury-rich effluent;

supplying the mercury-rich effluent to the mercury removal vessel; and

adsorbing the mercury from the mercury-rich effluent by the activated carbon in the mercury removal vessel thereby producing treated effluent.

18. The method of claim 17 , wherein the treated effluent is supplied to the absorber vessel.

19. The method of claim 17 , wherein the activated carbon is disposed in the mercury removal vessel in at least one of a pile, a moving bed, a fluidized bed, and mixed in with the mercury-rich effluent.

Assignments (2)
CHANGE OF NAME Recorded Aug 17, 2016
From: ALSTOM TECHNOLOGY LTD
To: GENERAL ELECTRIC TECHNOLOGY GMBH
Reel/Frame 039714/0578 →
ASSIGNMENT OF ASSIGNOR'S INTEREST Recorded Jun 1, 2012
From: LASLO, DENNIS JAMES; GANSLEY, RAYMOND RAULFS
To: ALSTOM TECHNOLOGY LTD.
Reel/Frame 028301/0105 →