A PILOT TEST OF PASSIVE OXYGEN RELEASE FOR ENHANCEMENT OF IN-SITU BIOREMEDIATION OF BTEX-CONTAMINATED GROUND-WATER

Citation
Sw. Chapman et al., A PILOT TEST OF PASSIVE OXYGEN RELEASE FOR ENHANCEMENT OF IN-SITU BIOREMEDIATION OF BTEX-CONTAMINATED GROUND-WATER, Ground water monitoring & remediation, 17(2), 1997, pp. 93-105
Citations number
17
Categorie Soggetti
Water Resources
ISSN journal
10693629
Volume
17
Issue
2
Year of publication
1997
Pages
93 - 105
Database
ISI
SICI code
1069-3629(1997)17:2<93:APTOPO>2.0.ZU;2-3
Abstract
A pilot-scale field demonstration of the use of Oxygen Release Compoun d(TM) (ORC) was conducted at the site of a former gasoline service sta tion. ORC was installed into a barrier consisting of a tight pattern o f ''treatment wells'' located relatively near the apparent source of h ydrocarbon contamination (20 to 30 m downgradient). The purpose of the barrier was to enhance in situ biodegradation of BTEX in ground water by the passive release of oxygen from the unpumped treatment wells pl aced across the migration path of the plume. Detailed monitoring was c arried out using fencelines of multilevel monitoring wells located up- and downgradient of the barrier. Total BTEX concentrations influent t o the barrier were found to be highly variable in space (nondetect to greater than 60 mg/L) and time. Total influent BTEX concentrations ave raged on a cross section transverse to flow were less variable over ti me, ranging from 10 to 16 mg/L. Significant decreases in BTEX mass flu x through the zone impacted by the treatment wells were observed. For the entire portion of the plume impacted by the treatment wells, estim ated BTEX treatment efficiency was approximately 70 percent on Day 51 of the test and declined thereafter. The decrease in efficiency was li kely due to the observed increase in the influent BTEX load as the tri al progressed along viith an apparent decline of the oxygen release ra te from the ORC. However, along flow-paths in which influent total BTE X concentrations were below about 5 mg/L, nearly complete removal of B TEX occurred for the entire trial (132 days). Mass flux estimates of B TEX and dissolved oxygen indicated that less than 10 percent of the ox ygen estimated to have been released from the treatment wells contribu ted to BTEX degradation or was observed as ''excess'' oxygen. NonBTEX components of the organic contamination appeared to exert a significan t oxygen demand and account for at least part of this discrepancy.