CHEMICAL OXIDATION Poster Session


Ozone-Peroxide Advanced Oxidation Water Treatment System for Treatment of Chlorinated Solvents and 1,4-Dioxane

Dr. Reid H. Bowman, Chief Technical Officer, Applied Process Technology, Inc., 3333 Vincent Road, Suite 222, Pleasant Hill, CA 94523, Tel: 925-977-1811, Fax: 925-977-1818
Philip Miller, England Geosystem, Inc., 15375 Barranca Parkway, Suite F-106, Irvine, CA 92618-2207, Tel: 949-453-8085, Fax: 949-453-0733
Michael Purchase, Orion Environmental, Inc., 3450 E. Spring St., Suite 212, Long Beach, CA 90806, Tel: 562-988-2755 Fax: 562-988-2759
Randy Schoellerman, San Gabriel Basin Water Quality Authority, 858 Oak Park Road, Suite 200, Covina, CA 91724, Tel: 626-859-777, ext. 26, Fax: 626-859-7788

A suspected carcinogen, 1,4-dioxane is an industrial solvent and an acid scavenger frequently added to chlorinated solvents to neutralize hydrochloric acid.  Common analytical methods used in groundwater quality investigations, such as EPA Method 8260, either do not include 1,4-dioxane or achieve relatively high detection levels, on the order of 100 µg/l.  Detection of 1,4-dioxane to 3 µg/l requires EPA Method 8270M.  The State of California recently adopted a drinking water “action level” of 3 µg/l, prompting more intensive monitoring for 1,4-dioxane in groundwater.  As a result of this monitoring, 1,4-dioxane has been discovered in groundwater wells where pump and treat remediation systems are in place to remove chlorinated solvents. Commonly used groundwater treatment technologies, such as air stripping and liquid-phase granular activated carbon (LGAC), have been shown to be ineffective in removing 1,4-dioxane.    A line pressure advanced oxidation process (AOP) using ozone and hydrogen peroxide has been shown to effectively remove 1,4-dioxane to below the 3 µg/l.  This AOP technology has been integrated into existing remediation systems, both air stripping and LGAC, as a pretreatment for the removal of 1,4-dioxane.  In addition to removing 1,4-dioxane to below 3 µg/l, the concentrations of most of the other chlorinated solvents present were significantly reduced.  The concentration of 1,4-dioxane treated ranged from 7 to 600 µg/l.  The scalability of line pressure advanced oxidation of 1,4-dioxane and chlorinated solvents has been demonstrated from pilot tests of 10 GPM to commercial installations of 1,000 GPM.

Implementation of an In Situ Chemical Oxidation Program for Remediation of Saturated Zone Petroleum Hydrocarbons at the Navy Exchange Service Station Naval Air Station, Brunswick, Maine

Alexander C. Easterday, EA Engineering, Science, and Technology, 175 Middlesex Turnpike, 3rd Floor, Bedford, MA 01730, Tel: 781-275-8846
Curtis J. Varner, EA Engineering, Science, and Technology, 3 Washington Center, Newburgh, NY 12550, Tel: 845-565-8100

A full-scale in situ chemical oxidation program utilizing hydrogen peroxide (H2O2) to remediate residual dissolved-phase and sorbed-phase petroleum hydrocarbons was applied at the Navy Exchange Service Station, Naval Air Station, Brunswick, Maine.  In situ chemical oxidation was selected as a final remedial technology to achieve site closure following several years of active soil vapor extraction/air sparging operations, which successfully treated vadose zone contamination and significantly reduced saturated zone petroleum hydrocarbon concentrations.  In situ chemical oxidation was utilized to mitigate residual saturated zone petroleum hydrocarbons that were found to be recalcitrant to ongoing soil vapor extraction/air sparging operations.

To assess the site-specific effectiveness of in situ chemical oxidation and to provide necessary data for design of the full-scale in situ chemical oxidation injection program, bench-scale testing was completed using ground-water and saturated zone soil samples collected from the remedial target area.  The bench-scale tests evaluated percent oxidation of benzene, toluene, ethylbenzene, and total xylenes; methyl tertiary-butyl ether; and total petroleum hydrocarbons against applied doses of hydrogen peroxide and ferrous-iron chelating agent solutions.  Bench-scale testing and in situ chemical oxidation injection procedures were completed by ISOTEC Inc., of West Windsor, New Jersey, under subcontract to EA.

The full-scale in situ chemical oxidation injection program was designed and implemented using the bench-scale testing results.  To evaluate the effectiveness of the full-scale in situ chemical oxidation program, ground-water and saturated zone soil samples were collected prior to and following each injection event.

This presentation will detail the results of the bench-scale testing and full-scale in situ chemical oxidation program with an emphasis on the correlation of the bench-scale testing to the full-scale in situ chemical oxidation effectiveness.  The presentation will also discuss the overall effectiveness of the in situ chemical oxidation remedial program for reducing dissolved-phase and sorbed-phase petroleum hydrocarbon concentrations as required to achieve conditions necessary for proceeding to site closure.

Cost Effective Application of Modified Fenton’s Reagent at an Operational Dry Cleaners Site 

Prasad K. Kakarla, In Situ Oxidative Technologies, Inc., 51 Everett Drive, A-10, West Windsor, NJ 08550, Tel: 609-275-8500, Fax: 609-275-9608, Email: prasad.kakarla@isotec-online.com
Richard S. Greenberg, In Situ Oxidative Technologies, Inc., 51 Everett Drive, A-10, West Windsor, NJ 08550, Tel: 609-275-8500, Fax: 609-275-9608, Email: richard.greenberg@ewma.com

Advanced oxidation techniques based on Fenton’s chemistry are increasingly surpassing traditional remediation treatments with respect to cost effectiveness, expediency, variety of contaminants mineralized, and the innocuous nature of the end products.  Despite its benefits, the field application of Fenton’s Reagent in its traditional form has historically been hindered by the instability of oxidizing and catalytic reagents when introduced into the subsurface, and the impracticality of lowering the native pH to acidic conditions.  Therefore, a modified Fenton’s reagent consisting of chelated iron catalyst and stabilized peroxide capable of functioning in the neutral pH range was developed by In-Situ Oxidative Technologies, Inc. (ISOTECSM).  The modified Fenton’s reagent delays formation of reactive hydroxyl radicals, allowing the oxidizing agent to thoroughly disperse in the subsurface first.  ISOTECSM implemented its patented process, which incorporates the modified reagent, to remediate a contaminated groundwater plume caused by an operational dry cleaners located in northeast Florida. The ground water was contaminated with up to 38 µg/l of Trichloroethene (TCE) and 54 µg/l of Tetrachloroethene (PCE) spread over an approximately 8,500-sq. ft area. The low chlorinated solvent concentrations render conventional treatment techniques more costly and less effective, despite the high capital, operation, and maintenance costs involved.  Initially, a laboratory bench scale and in-situ field experiments were performed to ascertain the subsurface characteristics, treatment stoichiometry, and process conditions.  The results of the laboratory bench scale indicated a 100% reduction in total VOCs found in the ground water sample.  A small portion of the groundwater plume was utilized for a field pilot program, which involved a 4-day injection event.  The pilot program yielded positive results; the concentrations of all VOC compounds in the treated area measured below Florida Department of Environmental Protection (FDEP) regulatory guidelines.  In the full-scale treatment program that followed, the majority of the plume was treated and all contaminant concentrations were reduced to below applicable FDEP groundwater quality criteria (3 µg/l for both TCE and PCE) after three two-week treatments over a six-month timeframe.  Closure of the site is expected in the summer of 2002, after 8 quarters of FDEP required post-treatment groundwater monitoring.  The entire treatment program was completed for an approximate cost of $18.00 per cubic yard of soil.

The Thermodynamics of Sodium Permanganate Oxidative Reactions

Brenda Veronda, Carus Chemical Company, 315 5th St., Peru, IL  61354, Tel: 815-224-6557, Fax: 815-224-6663
Ken Pisarczyk, Carus Chemical Company, 315 5th St., Peru, IL  61354, Tel: 815-224-6503, Fax: 815-224-6663
Erik Pedersen, Carus Chemical Company, 1500 8th St., LaSalle, IL  61301, Tel: 815-224-6869, Fax: 815-224-6841

According to the United States Environmental Protection Agency (USEPA), a significant number of the hazardous waste sites in the United States have contaminated groundwater.  Some of the most common contaminants are chlorinated organic solvents such as trichloroethylene (TCE) and perchloroethylene (PCE).  In-situ (ISCO) and ex-situ chemical oxidation techniques and technologies have been developed to quickly and effectively oxidize these types of chlorinated contaminants.  The key reacting element in these remediation techniques is the oxidant, and knowledge of how the oxidant reacts and the consequences of its reactions are critical factors that can affect the successful completion of a remediation project.

The use of permanganate ( MnO4- ) as the oxidant for in-situ or ex-situ chemical oxidation is characterized by fast reaction rates that result in the complete mineralization of TCE and PCE into carbon dioxide, water and chloride salts.  Sodium and potassium permanganate are strong oxidizing reagents, and the reactions need to be thoroughly understood and controlled in order to achieve optimum oxidation results.  The kinetics – or rate at which permanganate reactions occur, and the thermodynamics - amount of heat released during a reaction, are important safety factors that depend directly upon the concentration of the oxidant.

Data will be presented illustrating the effects of oxidant concentration on the amount of heat released during these reactions.  In addition to the reactions of interest, the presentation will also examine the reactions between the oxidant and other common reducing agents present at remediation sites.  How oxidant concentrations radically alter the reaction characteristics and directly affect the hazardous characteristics and conditions that surround the product will be discussed.

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