Chiang Hung-Lung, Lin Kuo-Hsiung, Lai Mei-Hsiu, Chen Ting-Chien, Ma Sen-Yi
Department Risk Management, China Medical University, Taichung 40402, Taiwan.
J Hazard Mater. 2007 Oct 1;149(1):151-9. doi: 10.1016/j.jhazmat.2007.03.064. Epub 2007 Mar 25.
A pyrolysis method was employed to recycle the metals and brominated compounds blended into printed circuit boards. This research investigated the effect of particle size and process temperature on the element composition of IC boards and pyrolytic residues, liquid products, and water-soluble ionic species in the exhaust, with the overall goal being to identify the pyrolysis conditions that will have the least impact on the environment. Integrated circuit (IC) boards were crushed into 5-40 mesh (0.71-4.4mm), and the crushed particles were pyrolyzed at temperatures ranging from 200 to 500 degrees C. The thermal decomposition kinetics were measured by a thermogravimetric (TG) analyzer. The composition of pyrolytic residues was analyzed by Energy Dispersive X-ray Spectrometer (EDS), Inductively Coupled Plasma Atomic Emission Spectrometer (ICP-AES) and Inductively Coupled Plasma-Mass Spectrometry (ICP-MS). In addition, the element compositions of liquid products were analyzed by ICP-AES and ICP-MS. Pyrolytic exhaust was collected by a water-absorption system in an ice-bath cooler, and IC analysis showed that the absorbed solution comprised 11 ionic species. Based on the pyrolytic kinetic parameters of TG analysis and pyrolytic residues at various temperatures for 30 min, the effect of particle size was insignificant in this study, and temperature was the key factor for the IC board pyrolysis. Two stages of decomposition were found for IC board pyrolysis under nitrogen atmosphere. The activation energy was 38-47 kcal/mol for the first-stage reaction and 5.2-9.4 kcal/mol for the second-stage reaction. Metal content was low in the liquid by-product of the IC board pyrolysis process, which is an advantage in that the liquid product could be used as a fuel. Brominate and ammonium were the main water-soluble ionic species of the pyrolytic exhaust. A plan for their safe and effective disposal must be developed if the pyrolytic recycling process is to be applied to IC boards.
采用热解方法回收混入印刷电路板中的金属和溴化化合物。本研究考察了粒径和工艺温度对集成电路板、热解残渣、液体产物以及废气中水溶性离子物种元素组成的影响,总体目标是确定对环境影响最小的热解条件。将集成电路(IC)板粉碎至5 - 40目(0.71 - 4.4毫米),并在200至500摄氏度的温度范围内对粉碎后的颗粒进行热解。通过热重(TG)分析仪测定热分解动力学。利用能量色散X射线光谱仪(EDS)、电感耦合等离子体原子发射光谱仪(ICP - AES)和电感耦合等离子体质谱仪(ICP - MS)分析热解残渣的组成。此外,通过ICP - AES和ICP - MS分析液体产物的元素组成。在冰浴冷却器中采用吸水系统收集热解废气,离子色谱分析表明吸收液包含11种离子物种。基于TG分析的热解动力学参数以及不同温度下30分钟的热解残渣,本研究中粒径的影响不显著,温度是集成电路板热解的关键因素。发现在氮气气氛下集成电路板热解存在两个分解阶段。第一阶段反应的活化能为38 - 47千卡/摩尔,第二阶段反应的活化能为5.2 - 9.4千卡/摩尔。集成电路板热解过程的液体副产物中金属含量较低,这一优势在于该液体产物可作为燃料使用。溴化物和铵盐是热解废气中的主要水溶性离子物种。如果要将热解回收工艺应用于集成电路板,必须制定其安全有效处置方案。