Abstract

Concern over the behavior and remediation of dissolved hydrophobic organic contaminants in groundwater at oil and gas facilities has led to this research investigation. In this study, sorption of PAHs, PCBs, Phenols, benzene, ethylbenzene, toluene and xylenes (BTEX) hydrocarbon from groundwater onto a subsoil core sample was examined as well as their destruction in ClO2/UV solution systems whereby methanol was the carrier solvent. All sorbate-sorbent systems yielded the S-type isotherms indicating co-operative interactions among sorbed organic species. Sorption of the sorbates could be best represented mathematically by the Freundlich equation with 1/n values ranging from 0.4338 to 2.226. Empirical Kf values ranged from 0.89 to 3.049. It is postulated that sorption of sorbates occurs through a combination of hydrogen bonding, dipole-dipole and hydrophobic interactions. Off site travel time for the sorbates ranged from 145 to 80,817 years. Destruction of solutes in UV/ClO2 solution systems is believed to occur through UV quantum vibration enhancement in molecules and free radical processes. Under the most efficient treatment system, 76 to 98% of the chemicals of concern were destroyed. No dioxins or furans were formed as by-products in any of the treatment systems investigated.This highly effective ClO2/UV destructive method has the potential to be applied as a new risk management approach for remediating recalcitrant organic contaminants in impacted groundwater.

Highlights

  • The groundwater environment at many petroleum industry facilities in Alberta, gasworks and around the world has been impacted by the management of hydrophobic organic contaminants

  • It has been recognized at such sites, the contaminated groundwater will consist of two contamination zones: a non-aqueous phase zone (NAPZ), and a dissolved contamination zone (DCZ)

  • The composition of a NAP matrix will contain benzene, ethylbenzene, toluene, xylenes, polycyclic aromatic hydrocarbons (PAHs), polychlorinated biphenyls (PCBs), phenols, alcohols, aldehydes, ketones, gasoline,heavy metals, polymers, acids, bases, and other type of inorganic chemicals commonly detected at oil and gas facilities[1]

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Summary

Introduction

The groundwater environment at many petroleum industry facilities in Alberta, gasworks and around the world has been impacted by the management of hydrophobic organic contaminants. It has been recognized at such sites, the contaminated groundwater will consist of two contamination zones: a non-aqueous phase zone (NAPZ), and a dissolved contamination zone (DCZ). The zone of dissolved contamination is formed by moving groundwater that comes into contact with the NAPZ which is predominantly originated from anthropogenic sources. Sorption is one of the key processes which determine the mobility and bioavailability of hydrophobic organic contaminants[2,3,4]. DNAP contamination source will consist of intermixing compounds having intrinsically different physicochemical and toxicity properties. Co-solvation may affect their advective transport by groundwater

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