Nancy Université, INRA, 2 avenue de la Forêt de Haye, Vandœuvre-lès-Nancy, France.
Chemosphere. 2012 Jul;88(3):300-6. doi: 10.1016/j.chemosphere.2012.02.041. Epub 2012 Mar 3.
Transfer of indicator polychlorobiphenyls (PCBs) from soil into hen eggs may occur in hens reared outdoor, which ingest significant amounts of soil. This transfer depends on the bioavailability of the ingested compounds. The impact of soil on the bioavailability of indicator PCBs was assessed by means by a relative bioavailability (RBA) trial, in which their deposition in egg yolk and in abdominal fat, in response to their ingestion through contaminated-soil and through spiked-oil were compared. A sandy soil (709 μg indicator PCBs kg(-1) dry matter) was collected in the vicinity of a former fire involving treated wood. Twenty-eight laying hens were individually housed and fed one of the seven experimental diets during 14 d. The seven experimental diets were an uncontaminated control diet, three diets in which contaminated soil was introduced at levels of 3%, 6% and 9% and three diets in which spiked oil was introduced to achieve similar levels and profile of contaminants. Yolk, abdominal fat and liver were collected at the end of exposure. Indicator PCBs were extracted by ASE (Accelerated Solvent Extraction) and analyzed by GC-HMRS. Within each ingested matrix, the concentration of indicator PCBs in yolk and in abdominal fat linearly increased with the amount of indicator PCB ingested (P<0.001). Except for PCB 28, the slopes of the responses to soil and to oil could not be differentiated (P>0.1). RBA estimates did not differ from 1 for all indicator PCBs except for PCB 28, for which it was 0.58-0.59. Measurements performed on liver confirm these conclusions.
土壤中的指示性多氯联苯(PCBs)可能会转移到户外饲养的母鸡的鸡蛋中,因为这些母鸡会摄入大量土壤。这种转移取决于摄入化合物的生物利用度。通过相对生物利用度(RBA)试验评估了土壤对指示性 PCB 生物利用度的影响,通过该试验比较了它们通过受污染土壤和添加油摄入后在蛋黄和腹部脂肪中的沉积。在附近曾经发生过涉及处理木材的火灾的地方收集了一种沙质土壤(709μg 指示性 PCBs kg(-1)干物质)。28 只产蛋母鸡被单独饲养,并在 14 天内喂食七种实验饮食中的一种。七种实验饮食分别为未受污染的对照饮食,以及三种分别用 3%、6%和 9%的污染土壤添加的饮食,以及三种添加了添加油以达到类似污染物水平和分布的饮食。暴露结束时收集蛋黄、腹部脂肪和肝脏。通过 ASE(加速溶剂萃取)提取指示性 PCBs,并通过 GC-HMRS 进行分析。在每种摄入的基质中,蛋黄和腹部脂肪中指示性 PCB 的浓度与摄入的指示性 PCB 量呈线性增加(P<0.001)。除 PCB 28 外,土壤和油的响应斜率无法区分(P>0.1)。除 PCB 28 外,所有指示性 PCBs 的 RBA 估计值均不等于 1,而 PCB 28 的 RBA 估计值为 0.58-0.59。对肝脏的测量结果证实了这些结论。