Abstract

Mining activities are acknowledged to introduce contaminants into localised environments and cause wider spread diffuse pollution. The concentration, distribution and fate of arsenic (As) and antimony (Sb) were studied at the former metalliferous Louisa Mine at Glendinning, Scotland. Soils and surface water were sampled and subsequently analysed to map the distribution of contamination and identify pollution sources. The maximum concentrations of As and Sb of 15,490 and 1504.2 mg kg−1, respectively, were determined in soils associated with the ore processing area and spoil heaps. The fractions of dissolved As and Sb in soils were < 1 and < 5% of total soil content, respectively, confirming findings of previous studies that As and Sb are relatively immobile. Yet, the concentrations of As and Sb released by soils exceeded regulatory limits. Concentrations of As and Sb in surface water in the immediate vicinity of the mine were impacted by a gully discharge, but rapidly diluted. While the concentrations affected by the run-off waters did not exceed EU environmental standards for freshwater, the concentrations of both, As and Sb, sharply increased above the said environmental standards approximately 100 m downstream of the mine site. The unaltered As-to-Sb ratio in water samples suggests a geogenic source. While there is a justifiable concern about the soil pollution caused by the historic mining in the area, the Glenshanna Burn is affected more by indigenous geochemical processes than the derelict mine.

Highlights

  • Mining activities are acknowledged to introduce contaminants into localised environments and cause wider spread diffuse pollution

  • Total soil As concentrations associated with the main site ranged from 108.33 to 15,490.74 mg kg-1

  • While the As concentrations of ore processing area were, on average, 8 times higher, the highest As concentrations were associated with spoils (5768.14 ± 811.92 mg kg-1, 16 times higher than the surrounding soils)

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Summary

Introduction

Mining activities are acknowledged to introduce contaminants into localised environments and cause wider spread diffuse pollution. As and Sb can be mobilised from soils to surface waters and groundwater (Nannoni et al 2011; Hiller et al 2012) This pathway represents another serious environmental problem, because it may cause a deterioration of water quality and introduce these contaminants to the food chain with risks to both human health and ecosystems (Abad-Valle et al 2018; Fei et al 2017; Protano and Nannoni 2018). Given that relatively low concentrations of As and Sb can have detrimental effects on human and environmental health, it is of utmost importance to characterise their spatial distribution and exposure profiles in the areas highlighted as potentially contaminated (Protano and Nannoni 2018)

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