Abstract

Petroleum hydrocarbon (PHC) contamination is a global environmental issue. Understanding the key factors and mechanisms controlling the fate and mobility of PHCs in soils and aquifers is critical for environmental risk assessment, the development of remediation strategies, and policy decisions. This study focuses on the effects of soil composition and temperature on the sorption and desorption of two representative aromatic PHC compounds: benzene and naphthalene. The experiments were carried out using artificial sandy loam soil mixtures with temperatures ranging from 3 to 25℃. As expected, the sorption capacities of the soils were primarily controlled by the organic carbon (OC) content, while barely affected by the clay content. The sorption data for benzene and naphthalene followed linear to near-linear isotherms. Naphthalene sorption further increased with decreasing temperature, whereas temperature had little effect on benzene sorption. The latter was consistent with the very small magnitude of the sorption enthalpy of benzene. Under imposed dynamic temperature fluctuations, naphthalene sorption and desorption were shown to be reversible: model simulations demonstrated minimal kinetic limitation of the temperature-dependent soil-water partitioning. Our results imply that even in simple artificial soil systems, temperature variations can have complex, but predictable, effects on the soil-pore water partitioning of PHCs and, hence, on their mobility and bioavailability. Understanding the role of temperature is thus a prerequisite to unraveling the coupled abiotic and biotic processes that modulate the fate of PHCs in real-world soils.

Highlights

  • Hydrocarbon extraction and storage are increasing all over the world, large and medium oil-spilling events have been decreasing since the 1970s (ITOPF, 2019)

  • The fate of Petroleum hydrocarbon (PHC) and the associated contamination risks depend on the actual compounds, as well as their migration and degradation

  • The fate of PHC contaminants is controlled by various environmental factors, including soil geochemistry and hydrology, climatic conditions, and the resident microbial community

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Summary

Introduction

Hydrocarbon extraction and storage are increasing all over the world, large and medium oil-spilling events have been decreasing since the 1970s (ITOPF, 2019). Spills continue to occur during extraction, transport, storage and refining of petroleum. These spills can have severe impacts on terrestrial, freshwater and marine ecosystems, because of the high toxicity of many petroleum hydrocarbons (PHCs) (Onwurah et al, 2007; Varjani, 2017). The fate of PHCs and the associated contamination risks depend on the actual compounds, as well as their migration and degradation. Spilled PHCs can penetrate the soil profile due to gravity, sorb on and desorb from minerals and soil organic matter (OM), migrate with groundwater as a dissolved or free phase, be emitted to the atmosphere through volatilization, and transformed into other compounds through abiotic and biotic reactions. The fate of PHC contaminants is controlled by various environmental factors, including soil geochemistry and hydrology, climatic conditions, and the resident microbial community

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