A Method for Removing Brine Spills in Soil Using Electrokinetics

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A Method for Removing Brine Spills in Soil Using Electrokinetics Christopher Athmer, PE Brent Huntsman, CPG Terran Corporation, Beavercreek, OH www.terrancorp.com International Petroleum Environmental Conference - Houston, TX October 15, 2014

Current Remediation Technologies for Brine Spills Amend and/or Flush Protective of an aquifer? Dig and Haul Cap

Electrokinetic Remediation? Application of direct current (DC) electricity to the soil Polarized electrodes invoke movement of pore water and ions contained in the pore water, even in low permeability soils

Electrokinetics Electroosmosis Movement of pore water and contaminants toward the cathode Electromigration Migration of ionic species toward respective electrodes (anions toward anode, cations toward cathode) by electrical attraction

Principles of Electrokinetics Electroosmosis = Water Transport from anode to cathode Electromigration = Ion Transport to the opposite electrode + Anode Soil Particle Soil Particle - + - + - - - Soil Particle - - - - - - - + + + + + + + + Water - Velocity + - Profile + + + + + + + + + - - - - - - - Soil Particle + - - Cathode Soil Particle Soil Particle

Electrokinetic Applications Environmental Remediation Heavy Metals (lead, chrome) Organic Solvents (with in-situ ZVI) Others (arsenic, nitrate, ISCO, bio-amendments) Dewatering/Stabilization Desalinization EK works in saturated & unsaturated zones

How EK Desalinization Works Sodium ions migrate toward the cathode by electromigration and electroosmosis where they are removed Chloride ions migrate toward the anode by electromigration, where they are removed or oxidized to chorine The removed cathode and anode streams are combined as brine and disposed/injected or beneficially reused

Model Development Model developed to help develop appropriate installation and operation 2-Dimensional Cylindrical coordinates (cathode at center) Zero flux boundary at anodes, C = 0 at cathodes Estimates removal times based on electromigration + electroosmosis Excel based model developed by Terran & Dr. Robert Wilkens at University of Dayton

Electrode Pattern

EK Desalinization Application Electromigration Brine + - Electroosmosis Cl- Na+ Rate of ion migration (electromigration) is proportional to voltage gradient and ionic mobility plus electroosmosis flow and any bulk convectional flow. Anode + Cathode -

Pilot Test Work 4 feet 4 feet 1 foot Sodium loading = 500 mg/kg, kaolin clay

Operations DC power supply @ 10 volts, 1.6 to 0.3 amps Anode cathode spacing of 8 inches (~0.5 V/cm) Water supplied at anode to replace EO water EO water (+ sodium) removed at cathode Chloride accumulates and oxidizes to chlorine at anode Sodium was model compound (conservative tracer) Model predicted 4 + days to travel 8 Expected exponential decline as residuals bleed out

Sodium Trends

Soil Sampling Periodic Sampling D' B' Radial Profile Samples (1,3,5,7" from anode) F B C' C D' D Final Sampling C' D' B' G E' Bulk Soil Samples B' A E' A' F' E A' F' B' F A' Background Sampling Areas

Soil Segment Profiles Electroosmotic Flow Final bulk sampling results = 83% removal of sodium, 71% removal of chloride

Agricultural Field Soil Experiment was duplicated using a field soil from nearby farm (clay loam) Sodium migration was retarded by up to 50% Similar soil concentration profiles at end of test Bulk removal rates were slightly better than kaolin test but test was run longer Kaolin test removed 83% sodium, 71% chloride Ag soil test removed 84% sodium, 79% chloride Complete data presented in Journal of Hazardous, Toxic and Radiological Waste (January 2013, January 2014)

Field Scale Design Readily available equipment and parts (lowest costs) Electrodes are installed like miniature wells. Slotted 1 or 2-inch PVC well screen DSA wire wrapping as primary electrode Backfill annulus with cathodic backfill material (example-loresco SWS ) Installed with Geoprobe or small drill rig Extraction equipment can be a small SVE package unit operated on a timer Passive as possible operation Tuned to minimize water usage

EK Desalinization Process Knock-Out Tank Water Feed Tank 480 Volt Line Feed (AC) T X T X Vacuum Blower Brine Discharge Pump Siphon tubes Anode buss feed (DC) + - Cathode buss feed Rectifier Vacuum Extraction Equipment Cl- Na+ Electrodes arranged in hexagonal grid Pore Water Patent Pending Anode (multiple) Cathode (multiple)

Additional Options Green Power DC rectifier can be supplemented or replaced by: Solar Wind Re-use of Brine for road treatment In areas where road salt is used

Conclusions EK can be used to remove sodium and chloride from soil Costs may be competitive with hauling and landfilling Next step is field scale applications