Abstract

Remediation of groundwater from landfill contamination presents a serious challenge due to the complex mixture of contaminants discharged from landfills. Here, we show the significance of a nature-based solution to a landfill-contaminated aquifer in southeast Norway. Groundwater physicochemical parameters monitored for twenty-eight years were used as a proxy to infer natural remediation. Results show that concentrations of the major chemical variables decreased with time and distance until they tailed off. An exception to this was sulphate, which showed an increase, but apparently, exhibits a stationary phase. The water types were found to be most similar between samples from active landfill and post-closure stages, while samples from the stabilised stage showed a different water type. All the chemical parameters of samples from the stabilised stage were found to be within the Norwegian drinking water standards, except iron and manganese, which were only marginally above the limits, an indication of a possible recovery of this aquifer. The findings highlight the significance of natural attenuation processes in remediating contaminated aquifers and have significant consequences for future contamination management, where natural remediation can be viewed as an alternative worth exploring. This is promising in the wake of calls for sustainable remediation management strategies.

Highlights

  • Remediation of groundwater from landfill contamination presents a serious challenge due to the complex mixture of contaminants discharged from landfills

  • Long-term groundwater chemical data for a period of 28 years was used to analyse for changes in water quality as a function of time, distance, and the stage of landfill stabilisation

  • Distance in this case was used to ascertain the significance of natural attenuation, which was found to be substantial

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Summary

Introduction

Remediation of groundwater from landfill contamination presents a serious challenge due to the complex mixture of contaminants discharged from landfills. Landfills operated in the seventies and earlier, before waste segregation was adopted, were fill-up with a mix of nearly ­anything[11] Leachate composition from such landfills is highly variable and complex in nature, consisting of a mixture of ­contaminants[3,11,12,13,14]. The time frame is set by the regulatory body for pollution control and varies from country to country, with 30 years being common for non-hazardous ­wastes[15,24] Such long-term remediation perspectives have significant financial implications. The presence of chemical containers buried in landfills may undermine the perceived low ­risk[11], due to a delayed leaching of contaminants as a result of corrosion of containers

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