Abalos M, Parera J, Abad E, Rivera J
Department of Ecotechnologies, IIQAB-CSIC, Jordi Girona 18, 08034 Barcelona, Spain.
Chemosphere. 2008 Apr;71(6):1115-26. doi: 10.1016/j.chemosphere.2007.10.034. Epub 2008 Feb 20.
Among the tasks included in the "Quality and safety of feeding fats obtained from co-products or by-products of the food chain" Project, supported by the European Union and included in the 6th Framework Program, a number of fats and oils collected as co- or by-products from the food chain were selected for the determination of polychlorinated dibenzo-p-dioxins (PCDDs), polychlorinated dibenzofurans (PCDFs) and 'dioxin-like' polychlorinated biphenyls (DL-PCBs). In the majority of the cases these samples are currently employed as feed ingredients. Nevertheless, additional fats, which are forbidden for feedstuff purposes were also considered in this study. In general terms, fats and oils were classified taking into account their nature and the processes applied to obtain these co- or by-products. PCDD/F and DL-PCB levels were evaluated in a first group of samples composed of fish oils, animal fats and lecithins. As expected, fats and oils with an animal origin presented higher concentrations, expressed in pg WHO-TEQ/g, compared to the levels found in vegetable samples like lecithins. The category of fish oils had the highest values for both PCDD/Fs and the sum of PCDD/Fs and DL-PCBs, with some samples showing levels above the maximum established at the present legislation related to the presence of PCDD/Fs and DL-PCBs in animal feed [Commission Directive 2006/13/EC of 3 February 2006 amending Annexes I and II to Directive 2002/32/EC of the European Parliament and of the Council on undesirable substances in animal feed as regards dioxins and dioxin-like PCBs. Official Journal of the European Communities L32, 44-53]. In a second group, fats and oils with a more complex composition obtained from different transformation processes or even mixtures of fats were considered; thus, acid oils from chemical refining, acid oils from physical refining, recycled cooking oils, oils extracted from exhausted bleaching earths, hydrogenated by-products, fatty acids calcium soaps and miscellaneous fats were analyzed. The data revealed a significant variability in PCDD/F and DL-PCB levels, expressed in pg WHO-TEQ/g, in these products. It has to be pointed out that the analyses of fats and oils belonging to these categories of products were sometimes difficult due to the complexity of the samples. In terms of legislation most of these samples cannot be easily included into one of the specific categories of substances intended for feedstuff purposes that are regulated in Commission Directive 2006/13/EC.
在由欧盟资助并纳入第六框架计划的“从食物链副产品或副产物中获取的饲料脂肪的质量与安全”项目所包含的任务中,选取了一些作为食物链副产物或副产品收集的油脂,用于测定多氯代二苯并 - 对 - 二噁英(PCDDs)、多氯代二苯并呋喃(PCDFs)以及“类二噁英”多氯联苯(DL - PCBs)。在大多数情况下,这些样品目前用作饲料成分。然而,本研究也考虑了禁止用于饲料目的的其他油脂。一般而言,油脂根据其性质以及获取这些副产物或副产品所采用的工艺进行分类。在由鱼油、动物脂肪和卵磷脂组成的第一组样品中评估了PCDD/F和DL - PCB水平。正如预期的那样,与卵磷脂等植物性样品中的水平相比,动物源性的油脂以皮克WHO - TEQ/克表示时呈现出更高的浓度。鱼油类别在PCDD/Fs以及PCDD/Fs和DL - PCBs总和方面具有最高值,一些样品显示的水平高于当前与动物饲料中PCDD/Fs和DL - PCBs存在相关的法规所规定的最大值[2006年2月3日欧盟委员会指令2006/13/EC修订欧洲议会和理事会关于动物饲料中有害物质(关于二噁英和类二噁英多氯联苯)的指令2002/32/EC的附件I和附件II。欧洲共同体官方公报L32,44 - 53]。在第二组中,考虑了通过不同转化工艺获得的成分更复杂的油脂甚至油脂混合物;因此,分析了化学精炼酸油、物理精炼酸油、回收食用油、从废漂白土中提取的油、氢化副产品、脂肪酸钙皂以及其他油脂。数据显示这些产品中PCDD/F和DL - PCB水平(以皮克WHO - TEQ/克表示)存在显著差异。必须指出的是,由于样品的复杂性,对属于这些产品类别的油脂进行分析有时很困难。就法规而言,这些样品中的大多数不容易被纳入欧盟委员会指令2006/13/EC中规定的用于饲料目的的特定物质类别之一。