Abstract

In this study, the 60,000-km durability tests were performed on two diesel engines (EURO IV and EURO II) by using B10 (10% waste cooking oil + 90% diesel) and B8 (8% waste cooking oil + 92% diesel), respectively, to determine the impacts on the emissions of polycyclic aromatic hydrocarbons (PAHs) and polychlorinated dibenzo-p-dioxins and dibenzofurans (PCCD/Fs). The above emissions were measured per 20,000-km testing intervals. The highest total PAH mass concentrations were 38.2 and 25.6 μg Nm^(-3) before durability test by operating the EURO IV and II engines, respectively, and decreased 51-55% after 60,000-km operation. The dominant congeners of PAH emissions were naphthalene (> 45%), pyrene, and phenanthrene, which belonged to the LM-PAHs. The total PAH BaP_(eq) had different emission trends between the two engines during the durability tests. The highest level was 2.17 μg BaP_(eq) Nm^(-3) from EURO II engine before the test and reduced 84% after a 60,000-km cycle, when the total-BaP_(eq) emissions of EURO IV tended to increase from 0.0894 to 0.154 μg BaP_(eq) Nm^(-3) after the same test. The most dominant congener to the toxicity emissions was benzo(a)pyrene (~70%). Additionally, the PCDD/F emissions were tested in EURO IV engine by using B10. The PCDD/F concentrations of mass and toxicity approached the highest levels, 167 ng Nm^(-3) and 3.69 pg WHO-TEQ Nm^(-3), after 60,000-km and 20,000-km running cycles, respectively. The main dominant congeners were OCDD (> 50%) for mass, 2,3,7,8-TeCDD (> 35%) and 1,2,3,7,8- PeCDD (> 18%) for toxicity. Consequently, the use of WCO-biodiesel might reduce the PAH mass and toxicity emissions in older engine but had no significant effect in PAH and PCDD/F emissions during the deterioration of a newer engine.

Highlights

  • Diesel Engines and Their Emissions As the fossil fuel crisis is getting more and more global attention, the demand for alternative fuel or green energy is becoming even stronger than before

  • The polychlorinated dibenzop-dioxins and dibenzofurans (PCDD/Fs) emissions were tested in EURO IV engine by using B10

  • The two engines were fuelled with B10 and B8, respectively, when the emissions of polycyclic aromatic hydrocarbons (PAHs) and PCDD/Fs were compared to verify the emission differences of the two engines at the beginning (0 km) and the end (80,000 km for only EURO IV for PAHs) and (60,000 km for EURO II for both PAHs and PCDD/Fs) of mileage accumulation

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Summary

Introduction

Diesel Engines and Their Emissions As the fossil fuel crisis is getting more and more global attention, the demand for alternative fuel or green energy is becoming even stronger than before. Several toxic chemicals, such as polycyclic aromatic hydrocarbons (PAHs), polychlorinated dibenzop-dioxins and dibenzofurans (PCDD/Fs), and brominated persistent organic compounds, are found in diesel engine operation (Lloyd and Cackette, 2001; Shah et al, 2005; Lin et al, 2010; Laroo et al, 2012; Mwangi et al, 2015b; Chen et al, 2017). These emissions are well known to pose higher risk of human health (Scheepers, 2015). Diesel engines have higher PM emissions, which provide large surface area and carbon sources to adsorb and generate the organic

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