Briffaerts K, Spirinckx C, Van der Linden A, Vrancken K
VITO, Boeretang 200, B2400 Mol, Belgium.
Waste Manag. 2009 Aug;29(8):2321-31. doi: 10.1016/j.wasman.2009.03.019. Epub 2009 Apr 21.
Waste consumer batteries are recycled using different routes based on hydrometallurgical and pyrometallurgical processes. Two hydrometallurgical and two pyrometallurgical treatment scenarios are compared starting from an average composition of Belgian waste batteries. The environmental performance is compared using life cycle analysis (LCA). The recycling rate is studied through mass balance calculation. Each treatment scenario results in a specific recycling rate. The environmental impact and benefits also vary between the treatment options. There is no such thing as a typical hydrometallurgical or pyrometallurgical treatment. When applying a hydrometallurgical treatment scenario, the focus lies on zinc and iron recycling. When allowing manganese recycling, the energy demand of the hydrometallurgical process increases considerably. Both pyrometallurgical options recycle zinc, iron and manganese. According to the LCA, none of the treatment scenarios performs generally better or worse than the others. Each option has specific advantages and disadvantages. The Batteries Directive 2006/66/EC sets out a recycling rate of 50% for consumer waste batteries. Based on metal recycling alone, the mass balances show that the target is difficult to obtain.
废旧消费电池通过基于湿法冶金和火法冶金工艺的不同路线进行回收。从比利时废电池的平均成分出发,对比了两种湿法冶金和两种火法冶金处理方案。使用生命周期分析(LCA)对比环境绩效。通过质量平衡计算研究回收率。每种处理方案都有特定的回收率。不同处理方案的环境影响和效益也有所不同。不存在典型的湿法冶金或火法冶金处理方式。应用湿法冶金处理方案时,重点在于锌和铁的回收。若允许回收锰,湿法冶金工艺的能源需求会大幅增加。两种火法冶金方案都回收锌、铁和锰。根据生命周期分析,没有一种处理方案总体上比其他方案更好或更差。每种方案都有特定的优缺点。2006/66/EC号电池指令规定消费废旧电池的回收率为50%。仅基于金属回收,质量平衡表明该目标难以实现。