Abstract

This work considers dust deposition and the heavy metal (HM) content on leaves of urban trees (Acer platanoides L. ‘Globosum,’ Fraxinus excelsior L. ‘Westhof’s Glorie’ and Tilia tomentosa Moench.) in order to estimate the trees’ capacity to remove dust and HM from the air. Leaves were collected from the Buda Arboretum and from different streets of heavy traffic in Budapest, Hungary, during 2015 and 2016. At each site, five trees were sampled by collecting 6 leaves from each tree from the height of 2–3 m. Dust deposits on the leaves were removed by soaking the fresh foliage in distilled water for 20 h and then washed with ultrasound shaking. Afterward, the leaves were dried to constant weight and then they were digested in nitric acid–hydrogen peroxide treatment, and their Pb, Fe, Ni, Zn and Cu contents were measured using an inductively coupled plasma (ICP AS) spectrometer. The removed dust deposit was dried, and after a similar digestion treatment the Pb, Fe, Ni, Zn and Cu contents were measured using an AURORA AI 1200 AAS appliance. The HM deposit was calculated in mg m–2 leaf surface area. In 2015, the amount of foliar dust deposit from spring to autumn increased from 86.3 to 270.2 mg m–2. The most efficient tree species in trapping dust on their leaves was the silver linden (98.5–123.5 mg m−2), followed by the Norway maple (74.2–84.8 mg m−2) and the common ash (62.8–74.6 mg m−2). The deposit of HM elements showed seasonal differences: the quantity of Fe and Pb deposit on autumnal leaves increased five- to tenfold, while other heavy metals did not show accumulation. Silver linden with its pubescent (hairy) leaf surface proved to be most efficient in entrapping and retaining dust and heavy metals. The 60–100% higher Pb and Fe content of autumnal leaves indicate that over the season leaves may absorb Fe and Pb from the foliar dust. Our results confirmed that the foliar dust is a potential indicator for monitoring the HM content in the air. We also show that foliar dust deposits should be considered when estimating the capacity of urban trees to clean the air.

Highlights

  • Atmospheric pollution causes serious human health problems in many urban communities; related effects such as discomfort and smog can lead to economical and societal complications

  • Metals are associated with higher road traffic in both urban and rural areas (Hosker and Lindbergh 1982; Apeagyei et al 2010; Lu et al 2010; Simon et al 2011; Moreira et al 2016; Badamasi 2017), and elevated levels of heavy metals (HM) in urban atmosphere are reported by Apeagyei et al (2010) and Lu et al (2010)

  • The foliar dust contains a wider range of particular matter sizes, we focused on the PM10 data as an indicator of the actual air pollution

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Summary

Introduction

Atmospheric pollution causes serious human health problems in many urban communities; related effects such as discomfort and smog can lead to economical and societal complications. Studies suggest that one of major sources of urban air pollution is due to traffic emitting CO2, CO, NOx, other gaseous compounds as well as dust and soot particulate matter (PM). This pollution causes significant environmental damages on vegetation, buildings and human health (Hosker and Lindbergh 1982; Davidson et al 2005; Yang et al 2005; Kampa and Castanas 2008; Apeagyei et al 2010; Lu et al 2010; Zupancic et al 2015; Badamasi 2017). Vehicles are major sources of HM (Pb, Zn, Cu, Ni and Fe) particles (Christoforidis and Stamatis 2009, Apeagyei et al 2010; Lu et al 2010; Moreira et al 2016); HM pollution under urban conditions is strongly associated with PM and traffic. The ten most important elements in atmospheric heavy metal pollution are in ranking: Fe, Al, Pb, Zn, Ti, Mn, Cu, V, Ni, Cr (Hoodaji et al 2012)

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