Abstract

Sources of contamination in a subsurface environment are petrol, diesel fuel, gasoline at oil refineries, underground storage tanks, transmission pipelines, and different industries. The permeable reactive barrier (PRB) is a promising technology to remediate groundwater in-situ. In this study, synthetic groundwater samples containing toluene are treated in three reactor columns by biological processes. PRB-1 consisted of sand and gravel as reactor media, microbial inoculum (bioaugmentation—BA), and nutrients (biostimulation—BS); PRB-2 consisted of sand and gravel as reactor media, microbial inoculum, nutrients, and 12 layers of nonwoven geotextile fabrics; and PRB-3 consisted of only sand and gravel as reactor media (natural attenuation—NA). This study was conducted to assess the impact of geotextile fabric filter, bioaugmentation, and biostimulation on toluene degradation efficiency. After 167 days of treatment, toluene biodegradation efficiencies varied between 88.2% and 93.8% for PRB 1, between 98.0% and 99.3% for PRB 2, and between 14.2% and 68.6% for PRB 3. The effluent toluene concentrations for PRB-2 were less than the guideline value (0.7 mg/L) of the World Health Organization. Reaction rate data were fitted with a first-order kinetic reaction rate model. This study showed that the toluene removal efficiency in the geotextile layered PRB combined with BA and BS process was significantly higher compared to the other processes tested. This lab-scale study introduced a new PRB configuration suitable for the remediation of sites contaminated with toluene.

Highlights

  • One of the most commonly used technologies for in-situ groundwater treatment is permeable reactive barriers (PRBs)

  • Pore volume, hydraulic conductivity, porosity, flow rate, and hydraulic residence time were calculated for each PRB reactor (Table 5)

  • Hydraulic testes resulted in similar values for porosity, pore volume, hydraulic conductivity, and hydraulic residence times for the three PRB reactors

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Summary

Introduction

One of the most commonly used technologies for in-situ groundwater treatment is permeable reactive barriers (PRBs). PRBs are filled with reactive materials which must be more permeable than the surrounding aquifer material. The other benefit of PRBs is that replacement of the PRB material is always possible [1]. The mechanisms of interaction in PRBs are degradation, precipitation, and sorption. The types of reactive materials used in PRBs serve different purposes: Some change pH or redox potential, other cause precipitation, some PRB materials have high sorption capacity, and some release nutrients and oxygen to enhance degradation. Reactive materials used in PRBs include activated carbon (AC), Al, ferric oxide, peat, zeolite, lignite, zero valent metals, fly ash, lime, limestone, sand, and clay

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