Effect of vehicle exhaust on the quantity of polycyclic aromatic hydrocarbons (PAHs) in soil

2007 ◽  
Vol 137 (1-3) ◽  
pp. 363-369 ◽  
Author(s):  
Amin Khan ◽  
Mohammad Ishaq ◽  
Murad Ali Khan
2012 ◽  
Vol 214 (2) ◽  
pp. 131-136 ◽  
Author(s):  
Hsiao-Chi Chuang ◽  
Ching-Wen Fan ◽  
Kuan-Yu Chen ◽  
Guo-Ping Chang-Chien ◽  
Chang-Chuan Chan

2012 ◽  
Vol 610-613 ◽  
pp. 2989-2994 ◽  
Author(s):  
Jing Ma ◽  
Ji San Zheng ◽  
Zu Yi Chen ◽  
Ming Hong Wu ◽  
Yuichi Horii ◽  
...  

Chlorinated polycyclic aromatic hydrocarbons (ClPAHs) are a group of halogenated contaminants found in the urban environment with a toxic potential similar to dioxins. Little is well-known on the distribution and characteristics of ClPAHs on urban surfaces. In this study, concentrations of 20 ClPAH congeners were measured in road dust and soil from crossroads along arterial traffic, park and lake areas, a chemical industrial complex, waste incineration power plants nearby, and a steel factory in Shanghai. ClPAHs are ubiquitous and log-normally distribute in urban surface with a range from 0.27 to 206 ng/g dw for dust, and with a range from 0.05 to 94.3 ng/g dw for soils. The highest mean concentration of total 20 ClPAHs is found in floor dust from a steel factory. ClPyr and ClPhe are predominant in road dust, which infers that ClPAHs detected in the urban surface dust samples originate from vehicle exhaust.


2005 ◽  
Vol 51 (3-4) ◽  
pp. 169-175 ◽  
Author(s):  
P. Pengchai ◽  
F. Nakajima ◽  
H. Furumai

This study aimed to estimate the origins of polycyclic aromatic hydrocarbons (PAHs) in size-fractionated road dust in Tokyo. First, seven categories of PAHs sources were defined: diesel vehicle exhaust, gasoline vehicle exhaust, tire, pavement, asphalt or bitumen, petroleum products excluding tire and asphalt, and combustion products except for those in vehicle engines. The 189 source data of 12-PAHs profiles were classified into 11 groups based on cluster analysis combined with principal component analysis. Next, 18 road dust samples were collected from eight streets in Tokyo and fractionated into four different particle-size-fractions: 0.1–45, 45–106, 106–250, and 250–2,000 μm. In order to estimate the contributions of the classified source groups (S1–S11) to PAHs in the road dust, multiple regression analysis was performed with 12-PAH profile of the road dust as dependent variable and average 12-PAHs profiles of the 11 source groups as 11 explanatory variables. Diesel vehicle exhaust, tire and pavement were the major contributors of PAHs in the fractionated road dust. Although the estimated contributions of the 11 source groups varied among the particle-size-fractions, there was no clear and consistent relationship between particle size and the major PAH contributor.


2008 ◽  
Vol 134 (3) ◽  
pp. 34-39
Author(s):  
Anna JANICKA ◽  
Wojciech WALKOWIAK ◽  
Włodzimierz SZCZEPANIAK

Polycyclic aromatic hydrocarbons (PAHs) are known to be mutagenic and carcinogenic group of substances. One of the most important anthropogenic source of these hydrocarbons is motorization (especially diesel engines). The most effective method of PAHs removal from exhaust gasses is using catalytic converters in vehicle exhaust systems. This paper presents results of measurements of polycyclic aromatic hydrocarbons emissions from self-ignition engine with platinum-rhodium active coating application inside.


Atmosphere ◽  
2021 ◽  
Vol 12 (3) ◽  
pp. 297
Author(s):  
Haitao Liu ◽  
Bo Li ◽  
Hong Qi ◽  
Lixin Ma ◽  
Jianzhong Xu ◽  
...  

A total of 68 PUF samples were collected seasonally from 17 sampling sites in Harbin, China from May 2016 to April 2017 for analyzing 15 congeners of gaseous polycyclic aromatic hydrocarbons (Σ15PAHs). An improved non-negative matrix (NMF) model and a positive matrix factorization (PMF) model were used to apportion the sources of PAHs. The carcinogenic risk due to exposure to PAHs was estimated by the toxicity equivalent of BaP (BaPeq). The results showed that the average concentration of Σ15PAHs was 68.3 ± 22.3 ng/m3, and the proportions of 3-ring, 4-ring, 5-ring, and 6-ring PAHs were 64.4%, 32.6%, 2.10%, and 0.89%, respectively. Among the six typical functional areas in Harbin, the Σ15PAHs concentrations were 98.1 ± 76.7 ng/m3, 91.2 ± 76.2 ng/m3, 71.4 ± 75.6 ng/m3, 67.9 ± 65.6 ng/m3, 42.6 ± 34.7 ng/m3, and 38.5 ± 38.0 ng/m3 in the wastewater treatment plant, industrial zone, business district, residential area, school, and suburb, respectively. During the sampling period, the highest concentration of Σ15PAHs was in winter. The improved NMF model and PMF model apportioned the PAHs into three sources including coal combustion, biomass burning, and vehicle exhaust. The contributions of coal combustion, biomass burning, and vehicle exhausts were 34.6 ± 3.22%, 48.6 ± 4.03%, and 16.8 ± 5.06%, respectively. Biomass burning was the largest contributor of Σ15PAHs concentrations in winter and coal combustion contributed significantly to the concentrations in summer. The average ΣBaPeq concentration was 0.54 ± 0.23 ng/m3 during the sampling period, high concentrations occurred in the cold season and low levels presented in the warm period. Vehicle exhaust was the largest contributor to the ΣBaPeq concentration of PAHs in Harbin.


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