Abstract

The effects of thermal treatment temperature and CaO addition on polychlorinated dibenzo-p-dioxins and dibenzofurans (PCDD/Fs) content in the fly ashes from a medical waste incinerator with high chlorine content (7.5%) were investigated. Two kinds of batch mode were examined: without CaO addition under the temperature range of 50–850°C, and with CaO addition at various Ca/Cl molar ratios (CCR = 0.8–44.3) at 250°C. The results show that the PCDD/F content in raw fly ash was 6.20 ng I-TEQ/g. When elevating the temperature from 50 to 400°Cwithout CaO addition, the PCDD/F content dramatically increased from 5.38 to 575 ng I-TEQ/g. Even at 850°C, the PCDD/Fs were not destructed apparently and were still with a concentration of 401 ng I-TEQ/g. However, with the addition of CaO at CCR = 17.7 at only 250°C, the removal ratio of PCDD/Fs reached to 87.2% and the PCDD/F content was significantly reduced to 0.889 ng I-TEQ/g, which meets the soil pollution standard of Taiwan EPA (1 ng I-TEQ/g) and could be considered as backfill. CaO addition was proven efficiently to enhance the reduction rate of PCDD/Fs in fly ashes during the thermal treatment at a low temperature, as well as inhibit the formation of PCDD/Fs.

Highlights

  • Polychlorinated dibenzo-p-dioxins and dibenzofurans (PCDD/Fs) have become a concern due to their adverse health effects (US EPA, 2000)

  • With the addition of calcium oxide (CaO) at Ca/Cl molar ratio (CCR) = 17.7 at only 250°C, the removal ratio of PCDD/Fs reached to 87.2% and the PCDD/F content was significantly reduced to 0.889 ng I-TEQ/g, which meets the soil pollution standard of Taiwan EPA (1 ng I-TEQ/g) and could be considered as backfill

  • From the thermal gravimetric analysis (Fig. 1), the patterns indicate the weight loss of fly ashes are apparently found at the intervals of room temperature-100°C, and 400–550°C, indicating the water and volatile matter are the major compositions in the fly ashes

Read more

Summary

Introduction

Polychlorinated dibenzo-p-dioxins and dibenzofurans (PCDD/Fs) have become a concern due to their adverse health effects (US EPA, 2000). The combustion temperature and chlorine content of raw materials plays an important role in PCDD/F formation (Lee et al, 2003; Wang et al, 2003b; Li et al, 2007; Wang et al, 2010). High concentrations of PCDD/Fs were formed, deposited (Wang et al, 2010; Huang et al, 2011) and found in small fly ash particles with large amounts of chlorine (Cobo et al, 2009). Three major mechanisms for PCDD/F emission from incinerators are: (1) high-temperature gas phase formation (300°C–600°C) (Everaert and Baeyens, 2002); (2) precursors transformation: such as chlorophenols, polychlorinated diphenyl ethers and chlorobenzenes (Lustenhouwer et al, 1980; Hutzinger and Blumich, 1985); and, (3) production via de novo synthesis in the low-

Methods
Results
Conclusion
Full Text
Published version (Free)

Talk to us

Join us for a 30 min session where you can share your feedback and ask us any queries you have

Schedule a call