Abstract

Road-deposited sediments (RDS) are major sources of heavy metal contamination in urban areas and adversely affect surrounding environments and human health. Multi-isotope combinations (Cu, Zn, and Pb), which serve as environmental tracers, enable the identification and management of metal contaminants in RDS. Here, we present Cu, Zn, and Pb isotopic data for the first time in size-fractionated RDS samples collected from industrial areas to describe the relationship between the RDS and total suspended solids (TSS) in runoff, and to explore the feasibility of using multi-isotopes to identify sources of metal contamination. RDS in the industrial study areas had high concentrations of Cu, Zn, and Pb, and their δ65CuAE647, δ66ZnIRMM3702, and 206Pb/207Pb values ranged from − 0.33 to + 0.73‰, − 0.36 to + 0.01‰, and 1.1418 to 1.1616, respectively. The variation in δ65CuAE647 (δ65Cumax-min) was larger than that of δ66ZnIRMM3702 (i.e., δ66Znmax-min), and the isotope values of Zn and Pb (206Pb/207Pb) tended to increase with the concentrations of these elements. Meanwhile, the fine RDS particles (< 63 µm) had similar Cu, Zn, and Pb isotopic compositions to those of TSS. Hierarchical cluster analyses revealed that the < 63 µm RDS fractions were associated with the TSS. Our results also showed that a combination of Pb and either Cu or Zn could be used to distinguish between RDS and non-exhaust emissions (e.g., brake pads, tires, etc.). Multi-isotope approaches utilizing Cu, Zn, and Pb and more robust isotopic data on individual sources of metal contamination could be useful for identifying pollution sources and understanding their environmental impacts.

Highlights

  • Road surfaces are hot spots for heavy metal pollution because of the accumulation of road-deposited sediments (RDS) via human activities

  • We found that the mean concentrations of Cu in RDS were in the following order by particle size: below 63 μm (20,089 mg/kg) > 63–125 μm (8245 mg/kg) > 125–250 μm (4056 mg/kg) > 250–500 μm (2340 mg/kg) > 500–1000 μm (1273 mg/kg) > above 1000 μm (353 mg/kg)

  • Li showed no difference in concentrations according to the RDS sizes, indicating that the metal concentrations in the RDS were significantly affected by anthropogenic sources

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Summary

Introduction

Road surfaces are hot spots for heavy metal pollution because of the accumulation of road-deposited sediments (RDS) via human activities. Road-deposited sediments in urban environments are highly polluted with Cu, Zn, and Pb due to traffic-related activities, such as tire, and brake pad wear and engine emissions (Adamiec et al 2016; Amato et al 2011; Iijima et al 2007; Jeong et al 2020a; Lanzerstorfer 2020). They are a major source of metal pollution in surrounding atmospheric particles, roadside. Multi-isotope approaches have been applied to identify and discriminate among individual metal sources in urban aerosols (Souto-Oliveira et al 2018, 2019; Schleicher et al 2020) and coastal sediments (Araújo et al 2019b)

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