Characterization of PM-Bound Heavy Metal at Road Environment in Tianjin: Size Distribution and Source Identification

To determine the size distribution and source identification of PM-bound heavy metals in roadside environments, four different particle size (<0.2 μm, 0.2–0.5 μm, 0.5–1.0 μm and 1.0–2.5 μm) samples were collected and analyzed from four different types of roads during the summer of 2015 in Tianjin...

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Main Authors: Qijun Zhang, Hongjun Mao, Yanjie Zhang, Lin Wu
Format: Article
Language:English
Published: MDPI AG 2021-09-01
Series:Atmosphere
Subjects:
Online Access:https://www.mdpi.com/2073-4433/12/9/1130
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spelling doaj-391b72aa36bc4a399000c19e78e87a962021-09-25T23:43:13ZengMDPI AGAtmosphere2073-44332021-09-01121130113010.3390/atmos12091130Characterization of PM-Bound Heavy Metal at Road Environment in Tianjin: Size Distribution and Source IdentificationQijun Zhang0Hongjun Mao1Yanjie Zhang2Lin Wu3Tianjin Key Laboratory of Urban Transport Emission Research, College of Environmental Science and Engineering, Nankai University, Tianjin 300071, ChinaTianjin Key Laboratory of Urban Transport Emission Research, College of Environmental Science and Engineering, Nankai University, Tianjin 300071, ChinaTianjin Key Laboratory of Urban Transport Emission Research, College of Environmental Science and Engineering, Nankai University, Tianjin 300071, ChinaTianjin Key Laboratory of Urban Transport Emission Research, College of Environmental Science and Engineering, Nankai University, Tianjin 300071, ChinaTo determine the size distribution and source identification of PM-bound heavy metals in roadside environments, four different particle size (<0.2 μm, 0.2–0.5 μm, 0.5–1.0 μm and 1.0–2.5 μm) samples were collected and analyzed from four different types of roads during the summer of 2015 in Tianjin. The results showed that the concentrations of PM-bound heavy metal from the roadside environment sampling sites were 597 ± 251 ng/m<sup>3</sup> (BD), 546 ± 316 ng/m<sup>3</sup> (FK), 518 ± 310 ng/m<sup>3</sup> (JY) and 640 ± 237 ng/m<sup>3</sup> (WH). There were differences in the concentrations of the heavy metal elements in the four different particle size fractions. The concentrations of Cu, Zn, Cd, Sn and Pb were the highest in the larger particle size fraction (0.5–2.5 μm). Cd, Cu, Zn and Pb were the elements that indicated emissions from tire wear and brake pad wear. The concentrations of Cr, Co and Ni were the highest in the smallest particle size fraction (<0.5 μm), indicating that motor vehicle exhaust was their main source. The correlation analysis results showed that there are differences in the concentration, distribution and correlation of different PM-bound heavy metals in different particle size fractions. The PCA results show that the accumulative interpretation variances of PM<sub>0.2</sub>, PM<sub>0.2–0.5</sub>, PM<sub>0.5–1.0</sub> and PM<sub>1.0–2.5</sub> reached 80.29%, 79.56%, 79.57% and 71.42%, respectively. Vehicle exhaust was the primary source of PM-bound heavy metal collected from the roadside sampling sites, while brake pad wear and tire wear were the second most common sources of the heavy metal.https://www.mdpi.com/2073-4433/12/9/1130roadside environmentPM-bound heavy metalsize distributionsource identification
collection DOAJ
language English
format Article
sources DOAJ
author Qijun Zhang
Hongjun Mao
Yanjie Zhang
Lin Wu
spellingShingle Qijun Zhang
Hongjun Mao
Yanjie Zhang
Lin Wu
Characterization of PM-Bound Heavy Metal at Road Environment in Tianjin: Size Distribution and Source Identification
Atmosphere
roadside environment
PM-bound heavy metal
size distribution
source identification
author_facet Qijun Zhang
Hongjun Mao
Yanjie Zhang
Lin Wu
author_sort Qijun Zhang
title Characterization of PM-Bound Heavy Metal at Road Environment in Tianjin: Size Distribution and Source Identification
title_short Characterization of PM-Bound Heavy Metal at Road Environment in Tianjin: Size Distribution and Source Identification
title_full Characterization of PM-Bound Heavy Metal at Road Environment in Tianjin: Size Distribution and Source Identification
title_fullStr Characterization of PM-Bound Heavy Metal at Road Environment in Tianjin: Size Distribution and Source Identification
title_full_unstemmed Characterization of PM-Bound Heavy Metal at Road Environment in Tianjin: Size Distribution and Source Identification
title_sort characterization of pm-bound heavy metal at road environment in tianjin: size distribution and source identification
publisher MDPI AG
series Atmosphere
issn 2073-4433
publishDate 2021-09-01
description To determine the size distribution and source identification of PM-bound heavy metals in roadside environments, four different particle size (<0.2 μm, 0.2–0.5 μm, 0.5–1.0 μm and 1.0–2.5 μm) samples were collected and analyzed from four different types of roads during the summer of 2015 in Tianjin. The results showed that the concentrations of PM-bound heavy metal from the roadside environment sampling sites were 597 ± 251 ng/m<sup>3</sup> (BD), 546 ± 316 ng/m<sup>3</sup> (FK), 518 ± 310 ng/m<sup>3</sup> (JY) and 640 ± 237 ng/m<sup>3</sup> (WH). There were differences in the concentrations of the heavy metal elements in the four different particle size fractions. The concentrations of Cu, Zn, Cd, Sn and Pb were the highest in the larger particle size fraction (0.5–2.5 μm). Cd, Cu, Zn and Pb were the elements that indicated emissions from tire wear and brake pad wear. The concentrations of Cr, Co and Ni were the highest in the smallest particle size fraction (<0.5 μm), indicating that motor vehicle exhaust was their main source. The correlation analysis results showed that there are differences in the concentration, distribution and correlation of different PM-bound heavy metals in different particle size fractions. The PCA results show that the accumulative interpretation variances of PM<sub>0.2</sub>, PM<sub>0.2–0.5</sub>, PM<sub>0.5–1.0</sub> and PM<sub>1.0–2.5</sub> reached 80.29%, 79.56%, 79.57% and 71.42%, respectively. Vehicle exhaust was the primary source of PM-bound heavy metal collected from the roadside sampling sites, while brake pad wear and tire wear were the second most common sources of the heavy metal.
topic roadside environment
PM-bound heavy metal
size distribution
source identification
url https://www.mdpi.com/2073-4433/12/9/1130
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