Chemical oxidation of volatile organic compounds

• US 6,019,548 A
• Filed: 05/05/1998
• Issued: 02/01/2000
• Est. Priority Date: 05/05/1998
• Status: Expired due to Term

• Current Assignee: United Technologies Corporation (Raytheon Technologies Corporation d/b/a RTX)
• Original Assignee: United Technologies Corporation (Raytheon Technologies Corporation d/b/a RTX), University of Connecticut (State of Connecticut)
• Inventors: Chheda, Pradeep Vishanji, Woody, Bernard Allen, Dobbs, Gregory Melville, Hoag, George Edward
• Primary Examiner(s): Lillis, Eileen Dunn
• Assistant Examiner(s): LEE, JONG SUK
• Application Number:
  US09/073,049
• Time in Patent Office: 637 Days
• Field of Search: 405/52, 405/128, 405/263, 405/264, 588/205, 588/249, 210/747, 210/758, 210/759, 210/766, 210/908
• US Class Current: 210/747.8
• CPC Class Codes: B09C 1/08 chemically
• CPC Class Codes: Y10S 210/908 Organic

Abstract

Volatile organic compounds are removed from contaminated soil by introducing one or both a water soluble peroxygen compound, such as a persulfate, and a permanganate into the soil, either in situ or ex situ, in amounts and under conditions wherein both the soil oxidant demand is satisfied and volatile organic compounds in the soil are oxidized. In a preferred embodiment, when both are used the peroxygen satisfies the soil oxidant demand and the permanganate oxidizes the volatile organic compounds. Sodium persulfate is the preferred persulfate and potassium permanganate is the preferred permanganate. The persulfate and the permanganate may be added to the soil sequentially, or may be mixed together and added as an aqueous solution.

Claims

1. A method for oxidizing volatile organic compounds in soil comprising the steps of:

a. Introducing solid phase water soluble peroxygen compound to the soil to satisfy at least most of the soil oxidant demand;

b. Introducing a permanganate into the soil; and

c. Oxidizing volatile organic compounds in the soil with the permanganate.

2. The method as in claim 1, wherein the permanganate is potassium permanganate and the peroxygen compound is a persulfate.

3. The method as in claim 2 wherein the persulfate is sodium base, ammonia base, or potassium base.

4. The method as in claim 3 wherein the persulfate is sodium persulfate.

5. The method as in claim 2 wherein the permanganate is potassium permanganate.

6. The method as in claim 5 wherein the persulfate is sodium persulfate.

7. The method as in claim 2, wherein the permanganate is introduced in sufficient quantities and under conditions to oxidize substantially all the volatile organic compounds in an identified volume of soil being treated.

8. The method as in claim 2 wherein the persulfate and the potassium permanganate are simultaneously introduced to the soil.

9. The method as in claim 8, wherein the persulfate and potassium permanganate are mixed together prior to being introduced into the soil.

10. The method as in claim 2 wherein the persulfate and the potassium permanganate are sequentially introduced to the soil.

11. The method as in claim 10 wherein the persulfate and the potassium permanganate are repeatedly and alternately introduced to the soil until substantially all the volatile organic compounds in the volume of soil being treated are oxidized.

12. The method as in claim 10 wherein the potassium permanganate is introduced to the soil prior to the introduction of the persulfate in amounts and under conditions that generate and leave behind a quantity of manganese dioxide precipitate in the soil as a barrier zone.

13. The method as in claim 2, wherein the potassium permanganate and the persulfate are introduced to the soil sequentially at predetermined time intervals, alternating between the introduction of the potassium permanganate and the introduction of the persulfate.

14. A method for oxidizing volatile organic compounds in a volume of soil in situ in the presence of divalent metal cations within the soil comprising the step of introducing persulfate into the soil to react with the metal cations to form sulfate free radicals that oxidize volatile organic compounds in the soil.

15. The method as in claim 14, including the step of adding a quantity of divalent metal cations to the volume of soil.

16. The method as in claim 15, wherein the added divalent metal ions are ferrous ions.

17. The method as in claim 16, wherein the ferrous ions are introduced into the soil by the addition of ferrous sulfate.

18. A method for oxidizing volatile organic compounds in an identified volume of soil comprising the steps of introducing oxidizing agent to the soil in amounts and under conditions sufficient a) to satisfy substantially all the soil oxidant demand and, b) to oxidize at least most of the volatile organic compounds in the soil volume.

19. The method as in claim 18, wherein the oxidizing agent includes potassium permanganate.

20. The method as in claim 18, wherein the identified volume of soil is treated ex situ, and wherein the potassium permanganate oxidizes substantially all the organic and inorganic soil constituents reactive with potassium permanganate and at least most of the volatile organic compounds in the volume of soil.

21. The method as in claim 20, wherein the potassium permanganate oxidizes substantially all the volatile organic compounds in the volume of soil.

22. A method for oxidizing subsurface volatile organic compounds in groundwater, comprising creating one or more zones of material in the path of the groundwater, the zones having sufficient permeability to allow the groundwater to pass through the zones, wherein the step of creating the zones of material includes forming manganese dioxide precipitate within the material of the zones to react with and oxidize the volatile organic compounds within the groundwater passing through the zones, the manganese dioxide precipitate being formed in sufficient quantity to reduce the quantity of the volatile organic compounds in the groundwater passing through the zones to acceptable levels before the groundwater leaves all of the zones.

23. The method as in claim 22, wherein the step of generating the manganese dioxide precipitate includes introducing permanganate into the material forming the zones.

24. The method as in claim 23, wherein the permanganate introduced into the material is potassium permanganate.

25. A method for the in situ clean up of site of land contaminated with volatile organic compounds comprising the steps of

a) identifying a volume of contaminated soil at the site;

b) using a first oxidant to oxidize most of the oxidant demand of the soil constituents in the identified volume by introducing the first oxidant into the identified volume; and

c) using a second oxidant, different from the first oxidant, to oxidize most of the volatile organic compounds in the identified volume by introducing the second oxidant into the identified volume.

26. The method as in claim 25, wherein the first oxidant is a peroxygen compound.

27. The method as in claim 26, wherein the second oxidant is a permanganate.

28. The method as in claim 27, wherein the peroxygen is a persulfate and the permanganate is potassium permanganate.

29. The method as in claim 28, wherein the persulfate is sodium persulfate.

30. The method as in claim 28, wherein the second oxidant oxidizes substantially all the volatile organic compounds of the identified volume.

31. The method as in claim 30, wherein the first oxidant satisfies substantially all the soil constituent oxidant demand of the identified volume.

32. The method as in claim 31, wherein the first oxidant is a persulfate selected from the group consisting of sodium persulfate, potassium persulfate and ammonium persulfate, and wherein the second oxidant is a permanganate selected from the group consisting of potassium permanganate, sodium permanganate and calcium permanganate.

33. The method as in claim 32, wherein the first and second oxidants are introduced simultaneously into the identified volume.

34. The method as in claim 32, wherein the first and second oxidants are introduced into the soil sequentially.

35. The method as in claim 34, wherein the second oxidant oxidizes substantially all the volatile organic compounds in the identified volume.

36. The method as in claim 35, wherein the first oxidant satisfies substantially all the oxidant demand of the oxidizable soil constituents in the identified volume.

37. A method for the in situ oxidizing of volatile organic compounds in a volume of soil by introducing persulfate into the volume of soil, followed by heating the soil to a temperature of from 40°

C. to 99°

C. to form sulfate free radicals in sufficient quantities to oxidize substantially all the volatile organic compounds in the volume of soil.

38. The method as in claim 37, including the step of adding divalent metal cations to the volume of soil to catalytically decompose the persulfate.

39. The method as in claim 38, wherein the step of adding metal cations includes adding metal sulfate to the soil volume to create reducing conditions.

40. A method for oxidizing volatile organic compounds in a volume of soil by introducing into the volume of soil an aqueous solution of permanganate and persulfate and heating the soil to a temperature of between 40°

C. to 99°

C. to form sulfate free radicals, wherein substantially all the volatile organic compounds in the soil are oxidized by the permanganate and the sulfate free radicals.

41. A method as in claim 40, wherein the volume of soil is treated with the solution of permanganate and persulfate, ex situ.