Short CommunicationEffect of metal and glycol on mechanochemical dechlorination of polychlorinated biphenyls (PCBs)
Introduction
Polychlorinated biphenyls (PCBs) are very stable industrial chemicals. They are produced by chlorination (2 < ncl < 10) of biphenyl (C12H10); the two-ring structure allows the formation of 209 congeners (Hutzinger et al., 1974). The PCB mixtures of congeners are ubiquitous and persistent pollutants in the global ecosystem (Lang, 1992). Their well known physical and chemical stability, along with their excellent dielectric properties, has led to a widespread industrial application as insulating materials for the electric industry, in capacitors and transformers. Destruction of these toxic chemicals has centered on incineration, plasma incineration, and other chemical methods such as wet oxidation and sodium-based reduction. Each of these methods has limitations. For example, incineration as well as chemical methods can generate HCl or Cl2 or small traces of PCDD/PCDF. Other chemical methods can require inert atmospheres and sensitive reagents. Thus, it is desirable to develop ways to rapidly dehalogenate organic molecules prior to their safe incineration. Recently, much attention has been paid to the mechanochemical treatment of toxic substances, due to its easy operation and practicability regarding the vast amounts of contaminated samples at low concentrations and the toxic chemical itself (Cocco et al., 1999). It is known that grinding plays a significant role in causing mechanochemical effects on solid particles as well as being a simple operation to reduce particle size (Birke et al., 2004). One of the unique phenomena of this effect is the ability to dissociate the material by rupturing the bonds (Birke et al., 2004). Mechanochemical dechlorinations of persistent organic pollutants (POPs) by milling with metals, alkali, and certain hydrogen donors like alcohols, ethers and so forth are discussed (Birke et al., 2004).
In this work, we examined the effect of metals and glycols on mechanochemical dechlorination of PCBs.
Section snippets
Experimental work
Aluminum, magnesium, iron and zinc powder of 99% purity and of range from 100 to 200 mesh were purchased from Junsei and Kanto and used without any pretreatment. Potassium hydroxide (KOH), ethylene glycol (EG), triethylene glycol (TEG) and polyethylene glycol 200 (PEG 200) were manufactured by Junsei and Yakuri. Attrition mill apparatus was composed of 1 l tank, impeller, 3 mm-zirconia ball, motor, and rpm controller.
Present investigation was carried out in batch mode. Predetermined quantities of
Effect of metals on the reaction
The general reaction of hydrogenation/dechlorination of PCBs occurring during the mechanochemical treatment is given in Eq. (1) (Aresta et al., 2003).where
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C12HxCly: polychlorobiphenyl with 0 < x < 8 and 2 < y < 10;
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M: zero-valent metal;
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E: energy transferred by milling;
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C12Hx: hydrocarbon; and
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MCl: chloride salts.
The milling energy had a fundamental role in the PCBs’ dechlorination process (Aresta et al., 2003). The transferred energy caused the nucleophilic substitution of Cl− with H−
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2022, Science of the Total EnvironmentCitation Excerpt :Over the last two decades, mechanochemistry has been used successfully to remediate environmental waste; notably, this has included other recalcitrant organic pollutants, such as dichlorodiphenyltrichloroethane (DDT) (Hall et al., 1996), hexachlorobenzene (HCB) (Cao et al., 1999; Korolev et al., 2003; Monagheddu et al., 1999; Zhang et al., 2014a), polychlorinated biphenyls (PCBs) (Aresta et al., 2003, 2004; Birke et al., 2006; Intini et al., 2007), polychlorinated dibenzo-p-dioxins (PCDDs) and polychlorinated dibenzofurans (PCDFs) (Yan et al., 2007), and tetrabromobisphenol A (Zhang et al., 2012). Mechanochemistry utilizes mechanical force to initiate chemical reactions that lead to the destruction of contaminants (Loiselle et al., 1997; Nah et al., 2008; Sui et al., 2018). This method stands out when considering both effectiveness and environmental benefits; it can be performed at ambient temperatures and pressures, and does not require the use of solvents, which allows it to be classified as a green technology (Wieczorek-Ciurowa and Gamrat, 2007).
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2022, Chemical Engineering JournalCitation Excerpt :The ratio of impact/shear depending on the type of milling device can largely change the removal efficiency of HOPs [15,36]. For instance, Birke et al. found that PCBs can be more effectively dechlorinated by zero valent Mg than Zn in a planetary ball mill, while Nah et al. observed that metallic Zn was more favorable than Mg and Al for PCBs destruction in an attritor mill [37,38]. Since the effect of different milling device on MC treatment of HOPs has not been addressed yet [15], it is of great importance to match co-milling agents with suitable device.