Contamination and risk of heavy metals in soils and sediments from a typical plastic waste recycling area in North China
Introduction
The quantities of end-of-life plastics from households and industries have increased markedly in recent decades (Thompson et al., 2009). Plastic waste treatment is becoming a vital task worldwide because these wastes are resistant to degradation and are leading to various environmental problems, including plastic pollution in the ocean (Rochman et al., 2013, Jambeck et al., 2015). In the past, plastic waste was usually landfilled together with municipal solid waste. Low sustainability, increasing cost and decreasing space for landfills are forcing consideration of alternative options for plastic waste disposal. Recycling has become the primary policy for treating plastic waste in many countries (Al-Salem et al., 2009, Hopewell et al., 2009). Material recycling is becoming the key disposal method for plastic waste in developing countries because of the relatively low investment and simple technology requirements, although energy recovery and chemical recycling are encouraged in some developed countries (Al-Salem et al., 2009, Hopewell et al., 2009).
Many plastic wastes contain or are contaminated with harmful chemicals. It was reported that the chemical ingredients of more than 50% of plastics are hazardous (Lithner et al., 2011). Some hazardous chemicals are also widely used as specific targeted additives in plastic products. For example, brominated organics and phthalate esters (PAEs) have been extensively applied in plastic products as flame retardants and plasticizers, respectively. These additives also include other flame retardants and plasticizers, pigments, stabilizers, and reinforcement components, which are composed of heavy metals or metal compounds (Dimitrakakis et al., 2009, Luo et al., 2011, Nakashima et al., 2012, Rochman et al., 2013). In some products, the contents of these dangerous additives are high or extremely high (Morf et al., 2007, Dimitrakakis et al., 2009, Stenvall et al., 2013). For example, the upper concentration ranges of Pb and Sb were reported at 100–2000 mg kg−1 and 2–13 g kg−1, respectively, in the plastic fraction of waste electrical and electronic equipment (WEEE) (Morf et al., 2007). In addition, plastic wastes can potentially absorb various priority pollutants from the environment to some extent (Nakashima et al., 2012, Rochman et al., 2013). Hence, many toxicants could be released into the environment during the milling, washing and melt processing of material recycling of plastic wastes, especially with the rather primitive and crude facilities used.
Pollutant release from material recycling has not received much attention. Such contamination is traditionally undervalued perhaps because this recycling is only a mechanical process and is conducted at relatively low temperatures (<300 °C in the extrusion). Several studies have recently reported the emission of harmful compounds from material recycling processes. Dozens of volatile organic compounds were identified in the air and the workers suffered acute and chronic health risks in poly(acrylonitrile-butadiene styrene) (ABS) and polystyrene (PS) recycling workshops (Huang et al., 2013, He et al., 2015). High levels of polycyclic aromatic hydrocarbons and PAEs were also measured in the air from a polyvinyl chloride (PVC) plastic waste recycling plant (Tsai et al., 2009, He et al., 2015). Our previous research reported that high concentrations of polybrominated diphenyl ethers (PBDEs) occurred in the environment and in human hair in a plastic recycling area in China and their potential risks should be of great concern (Tang et al., 2014). Available information about the toxicant emissions and pollution characteristics from these processes is still rare.
The occurrence of material recycling of plastic waste by environmentally unfriendly and primitive technologies in developing countries, especially in Asia, Africa and Latin America, has increased in recent years (Pacheco et al., 2012, Huang et al., 2013, Yang and Buekens, 2014). In China, the total recycling of plastic wastes increased from 16.1 million tonnes in 2008 to 24.9 million tonnes in 2013; of the plastic recycled, primitive material recycling of plastic waste is common (Wei and Zhang, 2014). So far, little is known about the release of heavy metals into the environment in plastic waste recycling areas where primitive methods are used, and the potential ecological and human risks of heavy metals from such sites remain unknown. Using Wen′an, in northern China, as a case study for plastic waste recycling, the objectives of this study were to conduct a reconnaissance survey to investigate and characterize the level and risk of toxic metals in soils and sediments. The results will improve our understanding of the extent of heavy metal pollution caused by plastic waste recycling and provide information to plan risk management measures.
Section snippets
Study area
Wen′an County, in northeast Hebei Province, China, has a population of 460,000 and an area of 1028 km2. The material recycling of plastic wastes has been practiced intensively in 101 villages in eight towns in Wen′an, the largest distribution center of material recycling of plastics in North China, employing nearly 100,000 people (Xu et al., 2010, Liu, 2011). These valuable materials have been reclaimed for more than 20 years in the village of Yincun, located in the central part of Zhaogezhuang,
Heavy metals in soils
The descriptive statistics of heavy metal concentrations in the soil samples from the plastic waste recycling area and reference area are summarized in Table 1. While As and Sb are metalloids, an extensive definition of “heavy metal” is used in the present study to simplify the expression of the whole manuscript. In Zhaogezhuang and Daliu, the Kolmogorov–Smirnov (K–S) test indicated that Cd, Cr, Cu, Hg, Pb, Sb and Zn had skewed concentration distributions and As had normal concentration
Acknowledgments
This research was supported by the National Environmental Protection Public Welfare Science and Technology Research Program of China (201309023), the National Natural Science Foundation of China (No. 41571445), and the Fundamental Research Funds for the Central Universities (No. 15MS60).
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