Department of Applied Environmental Science (ITM), Stockholm University, Stockholm, Sweden.
Waste Manag. 2013 Apr;33(4):842-9. doi: 10.1016/j.wasman.2012.12.008. Epub 2013 Jan 9.
Ash from incinerated waste consists mainly of a complex mixture of metals and other inorganic elements and should be classified based on its inherent hazardous effects according to EUs Waste Framework Directive. In a previous study, we classified eight eluates from ash materials from Swedish incineration plants, both chemically and ecotoxicologically (using bacteria, algae, crustacean and fish). Based on measured concentrations in the eluates together with literature acute toxicity data on the crustacean Nitocra spinipes we identified six elements (i.e. Zn, Cu, Pb, Al, K and Ca) potentially responsible for the observed ecotoxicity. However, comparing the used test methods with N. spinipes, the acute test was relatively insensitive to the eluates, whereas the (sub)chronic test (i.e. a partial life cycle test, investigating larval development ratio) was very sensitive. The overall aim of this follow-up study was to verify if the pinpointed elements could be responsible for the observed (sub)chronic toxicity of the eluates. Individual effect levels (i.e. NOEC values) for these six elements were therefore generated using the (sub)chronic test. Our results show that for six of the eight eluates, the observed ecotoxicity can be explained by individual elements not classified as ecotoxic (Al, K and Ca) according to chemical legislation. These elements will not be considered using summation models on elements classified as ecotoxic in solid material for the classification of H-14, but will have significant implications using ecotoxicological test methods for this purpose.
焚烧废物产生的灰烬主要由金属和其他无机元素的复杂混合物组成,应根据欧盟废物框架指令,根据其固有危险效应进行分类。在之前的一项研究中,我们对来自瑞典焚烧厂的灰烬材料的八种洗脱液进行了化学和生态毒理学分类(使用细菌、藻类、甲壳类动物和鱼类)。基于洗脱液中的实测浓度以及有关甲壳类动物 Nitocra spinipes 的文献急性毒性数据,我们确定了六种可能导致观察到的生态毒性的元素(即 Zn、Cu、Pb、Al、K 和 Ca)。然而,将所用测试方法与 Nitocra spinipes 进行比较后,急性测试对洗脱液相对不敏感,而(亚)慢性测试(即部分生命周期测试,研究幼虫发育比率)则非常敏感。本后续研究的总体目标是验证所确定的元素是否可能导致洗脱液的观察到的(亚)慢性毒性。因此,使用(亚)慢性测试生成了这六种元素的个体效应水平(即无可见效应浓度值)。我们的结果表明,对于八种洗脱液中的六种,观察到的生态毒性可以用未根据化学法规归类为生态毒性的个别元素(Al、K 和 Ca)来解释。在对 H-14 进行固体物质中归类为生态毒性的元素进行总和模型计算时,这些元素不会被考虑在内,但在为此目的使用生态毒理学测试方法时,它们将具有重要意义。