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满足欧盟 ELV 目标:热解汽车碎料机残渣的中试规模研究,固体残渣产物中的多环芳烃、多氯联苯和环境污染物。

Meeting EU ELV targets: Pilot-scale pyrolysis automotive shredder residue investigation of PAHs, PCBs and environmental contaminants in the solid residue products.

机构信息

Centre for Waste Management, University of Central Lancashire, Preston PR1 2HE, UK.

Centre for Waste Management, University of Central Lancashire, Preston PR1 2HE, UK; Recycling Lives Recycling Park, Preston, Lancashire PR2 5BX, UK.

出版信息

Waste Manag. 2020 Mar 15;105:233-239. doi: 10.1016/j.wasman.2020.02.005. Epub 2020 Feb 20.

DOI:10.1016/j.wasman.2020.02.005
PMID:32088569
Abstract

The EU's publication of the 2017 End-of-Life Vehicle Recycling and Recovery results reported that the UK failed to meet its targets. The Commission's data showed that the UK only achieved a rate of 94.1% falling short of the 95% target. The treatment of automotive shredder residue (ASR) using pyrolysis technologies offers a potential solution to this shortfall. The pyrolysis products could contribute to the target as well as supporting the circular economy package. However, there are questions about their hazardous nature and whether they qualify as secondary products. ASR, from a commercial plant, was processed through a pilot-scale pyrolysis unit, which separated the char into two fractions: coarse ≥0.1 mm and fine ≤0.1 mm. These were chosen as potential commercial products. Chars were produced from two processing temperatures of 800 and 1000 °C. These temperatures maximise gas production and produce the best "quality" char in terms of limiting organic contamination. It was found that the toxicity of the chars changed with both processing temperature and size fraction; with the maximum total PAHs concentration in the fine fraction at 800 °C. The coarse fractions were shown to be non-hazardous. It is suggested that some form of post-separation may be required to remove the hazardous component. The implication was that non-separated char could be classified as hazardous even if its overall characteristics were not, due to the role of dilution. If there were any questions about the status of the char this could prevent the use of ASR to meet the higher ELV target.

摘要

欧盟公布的 2017 年报废车辆回收和再利用结果报告显示,英国未能达到其目标。委员会的数据显示,英国仅实现了 94.1%的回收率,未达到 95%的目标。采用热解技术处理汽车破碎机残余物(ASR)为弥补这一差距提供了一种潜在的解决方案。热解产物可以为目标做出贡献,也可以支持循环经济方案。然而,关于它们的危害性以及它们是否符合二次产品标准存在疑问。从商业工厂获得的 ASR 通过一个中试规模的热解单元进行处理,该单元将炭分成两个部分:粗≥0.1mm 和细≤0.1mm。这些被选为潜在的商业产品。在 800 和 1000°C 的两个加工温度下生产炭。这些温度最大限度地提高了气体产量,并在限制有机污染方面产生了最佳“质量”炭。结果发现,炭的毒性随加工温度和粒度的变化而变化;在 800°C 时,细颗粒中总多环芳烃浓度最高。粗颗粒被证明是无危险的。有人建议,可能需要某种形式的后分离来去除危险成分。这意味着,如果不进行分离,即使炭的整体特性不危险,由于稀释的作用,炭也可能被归类为危险物质。如果对炭的状况有任何疑问,这可能会阻止使用 ASR 来达到更高的 ELV 目标。

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