Elsevier

Chemosphere

Volume 59, Issue 10, June 2005, Pages 1497-1505
Chemosphere

The effect of copper speciation on the formation of chlorinated aromatics on real municipal solid waste incinerator fly ash

https://doi.org/10.1016/j.chemosphere.2004.12.049Get rights and content

Abstract

A limited amount of information exists regarding the relationship between the chemical form of copper and the formation of chlorinated aromatics in fly ash. To understand the effects of the various forms of copper on the formation of chlorinated aromatics in real fly ash, we determined the chemical forms of copper present in various types of real fly ash using X-ray absorption near edge structure (XANES) and evaluated the relationship between the chemical forms of copper and the formation of chlorinated aromatics. Copper chloride hydroxide (CuCl2 · 3Cu(OH)2) and cuprous chloride (CuCl) were the predominant copper species found in real fly ash. Although pure cupric chloride (CuCl2) is known to be the most active catalyst for the formation of chlorinated aromatics under experimental conditions with synthetic fly ash, CuCl2 was not found in every real fly ash sample. The amount of copper chloride hydroxide was positively correlated with the formation of chlorinated aromatics in real fly ash and is, consequently, considered to be one of the key species involved in the formation of chlorinated aromatics.

Introduction

Understanding the mechanisms involved in the formation of chlorinated aromatics in fly ash is necessary in order to control the emission of dioxins and other toxic organic compounds; such compounds are secondarily formed in a post-combustion zone which is considered to occur primarily on and in fly ash, as first described by Stieglitz and Vogg (1986).

According to many studies, copper compounds are regarded as influential catalysts; large amounts of polychlorinated dibenzo-p-dioxin/dibenzofuran (PCDD/DF) and related compounds have been found to be generated in experiments involving heat, synthetic fly ash, and copper chloride (Stieglitz et al., 1989, Luijk et al., 1994, Addink and Olie, 1995, Schoonenboom et al., 1995, Addink and Altwicker, 1998). On the other hand, some studies on the relationship between the amount of PCDD/DF generated and the changes in copper compounds in synthetic fly ash under conditions similar to those leading to the deactivation of catalysts have reported that the catalytic activities for the formation of chlorinated aromatics differed among copper compounds (Lippert et al., 1991, Gullett et al., 1992, Raghunathanm and Gullett, 1996). In a similar manner, much research has been performed using synthetic fly ash, but only limited information on the relationship between the chemical forms of copper in real fly ash and the formation of chlorinated aromatics is available from the literature. Although the results of experiments investigating the formation of PCDD/DF using synthetic fly ash have established that copper chloride acts as a catalyst in real fly ash, the presence and potential of copper chloride in real fly ash are yet to be confirmed.

Our purpose for this study was to investigate the effect of the chemical form of copper present in real fly ash on the formation of chlorinated aromatics. Chlorobenzene (CBz) and polychlorinated biphenyls (PCBs) were chosen as representative chlorinated aromatic compounds for this study because they have been found to react similarly to PCDDs and DFs in heating experiments involving fly ash (Stieglitz et al., 1989, Huang and Buekens, 1995), are well known precursors of dioxin (Kato et al., 2000, Heger et al., 2001), and are easily managed and analyzed. We determined the chemical forms of copper present in various types of real fly ash using X-ray absorption near edge structure (XANES) and evaluated the relationship between the formation of chlorinated aromatics and the chemical form of copper.

Section snippets

Samples

Samples of several types of fly ash were obtained from eight stoker-type municipal solid waste incinerators (MSWIs) as shown in Table 1. The composition of the fly ash was measured by using an inductively coupled plasma atomic emission spectrometer (ICP-AES; Shimadzu model ICPS-8000) or an X-ray fluorescence spectrometer (XRF; Shimadzu model XRF-1700). The total organic carbon (TOC) in the fly ash was analyzed using a TOC analyzer (Shimadzu model TOC-5000) after inorganic carbon was removed by

The relationships between the amounts of PCBs, CBzs, and elements in the fly ash

The results of the heating experiments are shown in Table 1. The amounts of CBzs and PCBs in the fly ash before the heating treatment ranged from 210–3100 ng/g to 8–110 ng/g, respectively. The relationship between the amounts of CBzs and PCBs was observed as shown in Fig. 1, with a correlation coefficient (r) of 0.74. If the data from MSWI 5 and 8 are omitted, the correlation coefficient tends closer toward 1; however, the features of MSWI 5 and 8, namely the element distribution and dust

Conclusions

Primarily, in the fly ash examined before the heating experiment, only the TOC content was closely related to the content of chlorinated aromatics. However, the TOC content was not related to the amounts of PCBs and CBzs in the fly ash after the heating experiment or to the increasing ratio. The contents of iron, copper, and zinc correlated with the increasing ratios of PCBs and CBzs. At 300 °C, heavy metal, acting as a catalyst or chlorine source, had a more serious influence on the increasing

Acknowledgements

The synchrotron radiation experiments were performed at the SPring-8 with approval of the Japan Synchrotron Radiation Research Institute (JASRI) (proposal no. 2001A0367-CX-np and 2003B0215-Nx-np). We warmly thank Dr. Tomoya Uruga for his technical assistances for XAFS measurements. A part of this research was conducted as a grant-in-aid for Waste treatment Research (proposal no. K1514) and financially supported by the Ministry of the Environment in Japan.

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