In-situ groundwater remediation by selective colloid mobilization

• US 5,846,434 A
• Filed: 02/28/1997
• Issued: 12/08/1998
• Est. Priority Date: 03/01/1996
• Status: Expired due to Fees

• Current Assignee: University of Georgia Research Corporation
• Original Assignee: The University of Georgia Research Foundation, Inc.
• Inventors: Seaman, John C., Bertch, Paul M.
• Primary Examiner(s): Woo, Jay H.
• Assistant Examiner(s): HOEY, BETSEY MORRISON
• Application Number:
  US08/808,253
• Time in Patent Office: 648 Days
• Field of Search: 210/665, 210/712, 210/724, 210/725, 210/727, 210/729, 210/747, 210/754
• US Class Current: 210/724
• CPC Class Codes: C02F 1/547 Tensides

Abstract

An in-situ groundwater remediation pump and treat technique effective for reclamation of aquifers that have been contaminated with a mixed, metal-containing waste, which promotes selective mobilization of metal oxide colloids with a cationic surfactant, preferably a quaternary alkylammonium surfactant, without significantly reducing formation permeability that often accompanies large-scale colloid dispersion, thus increasing the efficiency of the remediation effort by enhancing the capture of strongly sorbing contaminants associated with the oxide phases. The resulting suspension can be separated from the bulk solution with controlled pH adjustments to destabilize the oxide colloids, and a clear supernatant which results that can be recycled through the injection well without further waste treatment.

Claims

1. A method of aqueous solution remediation by selectively mobilizing metal oxides in colloidal form having a net-positive surface charge in the aqueous solution which comprises metal oxide colloids and phyllosilicate clays, comprising the steps of:

(a) adding a cationic surfactant to the aqueous solution, thereby shielding said metal oxide colloids from at least a portion of the negatively charged sites associated with said phyllosilicate clays present in the aqueous solution, resulting in a stable suspension of the metal oxides in the aqueous solution;

(b) flocculating the resulting suspension, resulting in a sediment of metal oxides and a supernatant liquid; and

(c) separating the resulting sediment from the supernatant liquid, resulting in the removal of the sediment and the remediation of the aqueous solution.

2. A method as claimed in claim 1, further comprising the step of returning said supernatant liquid to the aqueous solution.

3. A method as claimed in claim 1, wherein the cationic surfactant is selected from the group consisting of quaternary alkylammoniums and salts of quaternary alkylammoniums.

4. A method as claimed in claim 3, wherein the cationic surfactant is selected from the group consisting of trimethylphenylammonium, tetramethylammonium, tetraethylammonium, tetradecyltrimethylammonium, benzyltrimethylammonium, benzyltrimethylammonium, benzyldimethyltetradecylamonium, and salts thereof.

5. A method as claimed in claim 3, wherein the metal oxides are selected from the group consisting of iron oxides, aluminum oxides, and manganese oxides.

6. A method as claimed in claim 1, wherein the step of flocculating comprises modifying the pH of the aqueous solution to between about 7 and 8.

7. A method as claimed in claim 6, wherein the step of modifying the pH comprises adding an alkaline or alkaline earth hydroxide to the aqueous solution.

8. A method as claimed in claim 7, wherein the metal hydroxide is selected from the group consisting of sodium hydroxide, calcium hydroxide and potassium hydroxide.

9. A method as claimed in claim 1, wherein the aqueous solution is groundwater.

10. A method for in-situ remediation of groundwater by selectively mobilizing metal oxides in colloidal form having a net positive surface charge in the groundwater which comprises the metal oxide colloids and phyllosilicate clays, comprising the steps of:

(a) injecting a cationic surfactant to the groundwater;

(b) capturing groundwater containing the cationic surfactant;

(c) flocculating the captured groundwater to settle colloids, resulting in a precipitate of metal oxides and a supernatant liquid; and

(d) returning the now remediated supernatant liquid to the groundwater.

11. A method as claimed in claim 10 further comprising the step of repeating steps (a) through (d) a number of times sufficient to remediate the groundwater.

12. A method as claimed in claim 10, wherein said step of injecting occurs at a position upgradient from said groundwater sought to be remediated.

13. A method as claimed in claim 12, wherein said step of extracting occurs at a position downgradient from said groundwater sought to be remediated.

14. A method as claimed in claim 10, further comprising the step of stabilizing any remaining polyvalent anionic solids in the groundwater.

15. A method as claimed in claim 14, wherein the step of stabilizing comprises leaching the groundwater with calcium chloride.

16. A method as claimed in claim 10, further comprising the step of removing the cationic surfactant from the groundwater.

17. A method as claimed in claim 10, wherein the cationic surfactant is selected from the group consisting of quaternary alkylammoniums and salts of quaternary alkylammoniums.

18. A method as claimed in claim 17, wherein the cationic surfactant is selected from the group consisting of trimethylphenylammonium, tetramethylammonium, tetraethylammonium, tetradecyltrimethylammonium, benzyltrimethylammonium, benzyltrimethylammonium, benzyldimethyltetradecylamonium, and salts thereof.

19. A method as claimed in claim 10, wherein the step of flocculating is comprised of modifying the pH of the groundwater to between 7 and 8.

20. A method as claimed in claim 19, wherein the step of modifying the pH comprises adding a metal hydroxide to the ground water.

21. A method as claimed in claim 20, wherein the metal hydroxide is selected from the group consisting of sodium hydroxide, calcium hydroxide and potassium hydroxide.