New Directions: Need for better understanding of plastic waste burning as inferred from high abundance of terephthalic acid in South Asian aerosols
New Directions: Need for better understanding of plastic waste burning as inferred from high abundance of terephthalic acid in South Asian aerosols
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DOI:
10.1016/j.atmosenv.2010.09.016
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发表时间:
2010-12
影响因子:
5
通讯作者:
K. Kawamura;C. Pavuluri
中科院分区:
文献类型:
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作者:
K. Kawamura;C. Pavuluri
Terephthalic acid (1, 4-benzenedicarboxylic acid; t-Ph) is an important industrial material used for making plastics such as polyester fibre and PET (polyethyleneterephthalate) thermoplastics. In term of public health, t-Ph promotes bladder cancer (Heck and Tyl, 1985). Global consumption of plastics reached 150 million tons per year in 2000, with an annual growth rate of 5.5%(Braun, 2004). Global production of polyester fibre alone was 24.5 million tons (65% of the world chemical fibre market) in 2004, 61% of which comes from Asia, followed by North America and Western Europe (Aizenshtein, 2006). Although plastic materials are increasingly recycled in developed countries, they are dumped as municipal solid wastes (MSW) in developing countries. The MSW are often burned under open-fire conditions to avoid the spread of mosquitoes that transmit malaria near the dumpsite, emitting plastic decomposition products to the atmosphere. t-Ph has been reported at elevated levels in smoke particles derived from open burning of new plastic bags (907 ng mg À1), roadside litter (5033 ng mg À1) and landfill trash (176 ng mg À1)(Simoneit et al., 2005). In addition, secondary formation by atmospheric oxidation reactions may also be significant. However, t-Ph has rarely been reported in ambient aerosols that are not derived from open-burning activities such as those listed above (Table 1). We have analyzed ambient aerosol samples (PM10) collected from the megacity Chennai, India (13.04 N 80.17 E) for molecular distributions of dicarboxylic acids using gas chromatography (GC) and GC/mass spectrometry. The details of the aerosol sampling and analytical procedures are described elsewhere (Pavuluri et al., 2010). Briefly, PM10 samples were collected on the rooftop of the Mechanical Sciences Building (18 m above the ground) at the Indian Institute of Technology Madras campus. The sampling location was not close to a MSW incineration site; rather it is more typical of city background. We detected t-Ph with very high concentrations ranging from 7.6 to 168 ng m À3 (average 45 ng m À3) in winter and 24–158 ng m À3 (61 ng m À3) in summer. t-Ph was found as the second most abundant dicarboxylic acid in most of the samples, in particular in nighttime samples, following oxalic acid (114–696 ng m À3), which is the most abundant water-soluble organic in particles from many locations around the globe (eg, Kawamura and Ikushima, 1993). Although phthalic acid (Ph) has been reported as the most abundant aromatic diacid in particles globally, Ph and isophthalic (i-Ph) acids were rather minor isomers in Chennai aerosols (Pavuluri et al., 2010). t-Ph concentrations in Chennai aerosols are 10 times greater than those reported for urban aerosols (TSP) from North America and East Asia as well as marine aerosols (TSP) from the Western Pacific and Southern Ocean (Table 1). In South Asia, in particular, India, the generation of MSW is very high with a rate of 0.5–0.7 kg capita À1 day À1 (48 Tg per year; 1997), in which plastics account for 2–8%.> 90% of MSW are disposed into open landfills without regulations (Jha et al., 2008), and local residents very often set light to the garbage to avoid the stench from the wastes and the occurrence of mosquitoes that transmit malaria. Plastics may readily decompose into monomers under open-fire conditions. These monomers can be emitted to the atmosphere and adsorbed onto preexisting particles. Interestingly, mass concentrations of t-Ph in Chennai aerosols were 55–1620 ng mg À1 (average 466 ng mg À1) in winter and 305–1890 ng mg À1 (764 ng mg À1) in summer. These values are comparable to those reported for …