Abstract

Abstract. An in situ bioremediation experiment of a deep vadose zone ( ∼ 40 m) contaminated with a high concentration of perchlorate (> 25 000 mg L−1) was conducted through a full-scale field operation. Favourable environmental conditions for microbiological reduction of perchlorate were sought by infiltrating an electron donor-enriched water solution using drip irrigation underlying an airtight sealing liner. A vadose zone monitoring system (VMS) was used for real-time tracking of the percolation process, the penetration depth of dissolved organic carbon (DOC), and the variation in perchlorate concentration across the entire soil depth. The experimental conditions for each infiltration event were adjusted according to insight gained from data obtained by the VMS in previous stages. Continuous monitoring of the vadose zone indicated that in the top 13 m of the cross section, perchlorate concentration is dramatically reduced from thousands of milligrams per litre to near-detection limits with a concurrent increase in chloride concentration. Nevertheless, in the deeper parts of the vadose zone (< 17 m), perchlorate concentration increased, suggesting its mobilization down through the cross section. Breakthrough of DOC and bromide at different depths across the unsaturated zone showed limited migration capacity of biologically consumable carbon and energy sources due to their enhanced biodegradation in the upper soil layers. Nevertheless, the increased DOC concentration with concurrent reduction in perchlorate and increase in the chloride-to-perchlorate ratio in the top 13 m indicate partial degradation of perchlorate in this zone. There was no evidence of improved degradation conditions in the deeper parts where the initial concentrations of perchlorate were significantly higher.

Highlights

  • In situ bioremediation of a contaminated unsaturated zone depends mainly on the ability to control the hydrological, physical and chemical conditions in the subsurface (Bombach et al, 2010; EPA, 2015; Höhener and Ponsin, 2014)

  • The infiltration experiments were primarily aimed at improving the environmental conditions for perchlorate-reducing bacteria across the vadose zone

  • This included an increase in water content along the soil profile and amendment of the electron donor

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Summary

Introduction

In situ bioremediation of a contaminated unsaturated zone ( termed vadose zone) depends mainly on the ability to control the hydrological, physical and chemical conditions in the subsurface (Bombach et al, 2010; EPA, 2015; Höhener and Ponsin, 2014). Implementation of desired biodegradation conditions in the deep vadose zone through full-scale field setups requires control of the vadose zone hydrogeochemical conditions. This is often achieved through either infiltration of water enriched with electron donors or nutrients (Battey et al, 2007; EPA, 2004; Frankel and Owsianiak, 2005), or injection of a gaseous mixture capable of promoting optimal biogeochemical conditions for microbial pollutant degradation (Evans et al, 2011; Evans and Trute, 2006). Due to the complex nature of flow and transport processes in the unsaturated zone, application of water with specific chemical conditions near land surface does not necessarily result in promoting the desired geochemical and hydraulic conditions in deeper parts of the vadose zone

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