Engineered in situ anaerobic reactive zones

• US 6,143,177 A
• Filed: 09/21/1998
• Issued: 11/07/2000
• Est. Priority Date: 04/11/1995
• Status: Expired due to Term

• Current Assignee: Arcadis Geraghty & Miller Inc. (Arcadis N.V.)
• Original Assignee: Arcadis Geraghty & Miller Inc. (Arcadis N.V.)
• Inventors: Suthersan, Suthan S.
• Primary Examiner(s): Upton, Christopher
• Application Number:
  US09/157,819
• Time in Patent Office: 778 Days
• Field of Search: 210/610, 210/611, 210/605, 210/747, 210/903, 210/603, 210/908, 210/912, 210/913, 435/262.5
• US Class Current: 210/610
• CPC Class Codes: B09C 1/002 involving in-situ ground water treatment
• CPC Class Codes: B09C 1/10 microbiologically, biologically or by using enzymes
• CPC Class Codes: B09C 2101/00 In situ
• CPC Class Codes: C02F 2101/20 Heavy metals or heavy metal compounds
• CPC Class Codes: C02F 2101/322 Volatile compounds, e.g. benzene
• CPC Class Codes: C02F 2101/36 containing halogen
• CPC Class Codes: C02F 3/306 Denitrification of water in soil
• CPC Class Codes: Y10S 210/903 Nitrogenous
• CPC Class Codes: Y10S 210/908 Organic
• CPC Class Codes: Y10S 210/912 Heavy metal
• CPC Class Codes: Y10S 210/913 Chromium

Abstract

An in situ method and system for reductive dechlorination, the precipitation of chromium, the precipitation of heavy metals, and microbial denitrification. The invention comprises the formation of in situ anaerobic reactive zones to precipitate and filter out dissolved heavy metals as metallic sulfides, to degrade nitrate to nitrogen gas, to reduce chlorinated hydrocarbons to ethene, and to precipitate and filter out chromium. The invention is comprised of an injection well or wells that extend into a contaminated saturated zone. A conduit located within the injection well conveys carbohydrates and sulfates to the contaminated saturated zone. Microbes digest the carbohydrates to produce sulfate reducing and methanogenic conditions within the reactive zone that include a dissolved oxygen level less than about 0.5 mg/l, a redox potential less than about -250 mv, and a dissolved organic carbon to contaminant ratio of greater than about 50:1. These biogeochemical conditions lead to the reduction of PCE to TCE to DCE to VC and eventually to ethene. These biogeochemical conditions also lead to the precipitation of heavy metals, the precipitation of chromium, and microbial denitrification.

Claims

1. A method for removing contaminants dissolved in groundwater, said method comprising the steps of:

providing at least one injection well extending from the ground surface to a contaminated saturated zone;

supplying carbohydrates and sulfates to said at least one injection well such that said carbohydrates and sulfates are introduced into said contaminated saturated zone, whereby microorganisms in said contaminated saturated zone metabolize said carbohydrates creating sulfate reducing and methanogenic conditions; and

maintaining said sulfate reducing and methanogenic conditions for a sufficient period of time such that chlorinated hydrocarbons present in said contaminated saturated zone are reduced to ethene.

2. The method of claim 1 wherein said sulfate reducing and methanogenic conditions further lead to the reduction of hexavalent chromium to trivalent chromium which is eventually precipitated as chromic hydroxide.

3. The method of claim 1 wherein said sulfate reducing and methanogenic conditions further lead to the precipitation of metal compounds.

4. The method of claim 1 wherein said sulfate reducing and methanogenic conditions further lead to microbial denitrification.

5. The method of claim 1 wherein said microorganisms are catalysts of the reduction of PCE to TCE to DCE to VC and eventually to ethene.

6. The method of claim 1 wherein, under said sulfate reducing and methanogenic conditions, said microorganisms are catalysts for the reduction of hexavalent chromium to trivalent chromium which is eventually precipitated as chromic hydroxide.

7. The method of claim 1 wherein, under said sulfate reducing and methanogenic conditions, said microorganisms are catalysts for the precipitation of metal compounds.

8. The method of claim 1 wherein, under said sulfate reducing and methanogenic conditions, said microorganisms are catalysts of microbial denitrification.

9. The method of claim 1 wherein said microorganisms are adapted to metabolize said carbohydrates and said sulfates to produce sulfide ions.

10. The method of claim 9 wherein said microorganisms are catalysts of the reduction of PCE to TCE to DCE to VC and eventually to ethene.

11. The method of claim 9 wherein, under said sulfate reducing and methanogenic conditions, said microorganisms are catalysts of the reduction of hexavalent chromium to trivalent chromium which is eventually precipitated as chromic hydroxide.

12. The method of claim 9 wherein, under said sulfate reducing and methanogenic conditions, said microorganisms are catalysts of the precipitation of metal compounds.

13. The method of claim 9 wherein, under said sulfate reducing and methanogenic conditions, said microorganisms are catalysts of microbial denitrification.

14. The method of claim 1 wherein at least a portion of said microorganisms are supplied to said contaminated saturated zone.

15. The method of claim 1 wherein the step of supplying said carbohydrates and said sulfates comprises:

placing a pump in fluid communication with said at least one injection well; and

operating said pump to force said carbohydrates and said sulfates into said contaminated saturation zone.

16. The method of claim 1 further comprising the step of mixing said carbohydrates and said sulfates in said injection well.

17. The method of claim 1 wherein the steps of supplying said carbohydrates and said sulfates comprises the step of supplying molasses extract to said conduit.

18. The method of claim 1 further comprising:

placing a conduit within said at least one injection well, said conduit having a fluid-permeable section below the water table of said contaminated saturated zone;

wherein said carbohydrates and sulfates are forced out of said fluid-permeable section into said contaminated saturated zone.

19. The method of claim 18 wherein said carbohydrates and sulfates are supplied under pressure to said conduit, such that said carbohydrates and sulfates are forcibly expelled from said fluid-permeable section, thereby flowing outwardly from said at least one injection well with the natural flow of groundwater and creating a three-dimensional reactive zone within said contaminated saturated zone.

20. A method for removing contaminants dissolved in groundwater, said method comprising the steps of:

providing an injection well from the ground surface to a contaminated saturated zone; and

supplying carbohydrates and sulfates to said injection well such that said carbohydrates and sulfates are introduced into said contaminated saturated zone;

wherein microorganisms in said contaminated saturated zone metabolize said carbohydrates creating anaerobic conditions which lead to the reduction of hexavalent chromium or trivalent chromium and eventually the precipitation of chromic hydroxide.

21. The method of claim 20 further comprising:

placing a conduit within said injection well, said conduit having a fluid-permeable section below the water table of said contaminated saturated zone;

wherein said carbohydrates and sulfates are forced out of said fluid-permeable section into said contaminated saturated zone.

22. A method for removing contaminants dissolved in groundwater, said method comprising the steps of:

providing an injection well from the ground surface to a contaminated saturated zone; and

supplying carbohydrates and sulfates to said injection well such that said carbohydrates and sulfates are introduced into said contaminated saturated zone;

wherein microorganisms in said contaminated saturated zone metabolize said carbohydrates creating anaerobic conditions which lead to the precipitation of metal compounds.

23. The method of claim 22 further comprising:

placing a conduit within said injection well, said conduit having a fluid-permeable section below the water table of said contaminated saturated zone;

wherein said carbohydrates and sulfates are forced out of said fluid-permeable section into said contaminated saturated zone.

24. A method for removing contaminants dissolved in groundwater, said method comprising the steps of:

providing an injection well from the ground surface to a contaminated saturated zone; and

supplying carbohydrates and sulfates to said injection well such that said carbohydrates and sulfates are introduced into said contaminated saturated zone;

wherein microorganisms in said contaminated saturated zone are catalysts for the creation of anaerobic conditions which lead to the reduction of hexavalent chromium or trivalent chromium and eventually the precipitation of chromic hydroxide.

25. The method of claim 24 further comprising:

placing a conduit within said injection well, said conduit having a fluid-permeable section below the water table of said contaminated saturated zone;

wherein said carbohydrates and sulfates are forced out of said fluid-permeable section into said contaminated saturated zone.

26. A method for removing contaminants dissolved in groundwater, said method comprising the steps of:

providing an injection well from the ground surface to a contaminated saturated zone; and

supplying carbohydrates and sulfates to said injection well such that said carbohydrates and sulfates are introduced into said contaminated saturated zone;

wherein microorganisms in said contaminated saturated zone are catalysts for the creation of anaerobic conditions which lead to the precipitation of metal compounds.

27. The method of claim 26 further comprising:

placing a conduit within said injection well, said conduit having a fluid-permeable section below the water table of said contaminated saturated zone;

wherein said carbohydrates and sulfates are forced out of said fluid-permeable section into said contaminated saturated zone.

28. A method for removing contaminants dissolved in groundwater, said method comprising the steps of:

providing an injection well from the ground surface to a contaminated saturated zone; and

supplying carbohydrates and sulfates to said injection well such that said carbohydrates and sulfates are introduced into said contaminated saturated zone;

wherein microorganisms in said contaminated saturated zone are adapted to metabolize said carbohydrates and said sulfates to produce sulfide ions, said microorganisms thereby serving as catalysts for the reduction of hexavalent chromium or trivalent chromium and eventually the precipitation of chromic hydroxide.

29. The method of claim 28 further comprising:

placing a conduit within said injection well, said conduit having a fluid-permeable section below the water table of said contaminated saturated zone;

wherein said carbohydrates and sulfates are forced out of said fluid-permeable section into said contaminated saturated zone.

30. A method for removing contaminants dissolved in groundwater, said method comprising the steps of:

providing an injection well from the ground surface to a contaminated saturated zone; and

supplying carbohydrates and sulfates to said injection well such that said carbohydrates and sulfates are introduced into said contaminated saturated zone;

wherein microorganisms in said contaminated saturated zone are adapted to metabolize said carbohydrates and said sulfates to produce sulfide ions, said microorganisms thereby serving as catalysts for the precipitation of metal compounds.

31. The method of claim 30 further comprising:

placing a conduit within said injection well, said conduit having a fluid-permeable section below the water table of said contaminated saturated zone;

wherein said carbohydrates and sulfates are forced out of said fluid-permeable section into said contaminated saturated zone.