评估回收所有PET瓶制成新食品包装的可能性

T. Begley, T. Mcneal, J. Biles, K. Paquette
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引用次数: 39

摘要

为了评估将所有PET瓶回收到食品包装中的可行性,需要对聚合物中可能存在的污染物的最大浓度进行现实的估计。为了估计非食品物质储存中可能在PET中的污染物的最大浓度,对两种类型的PET进行了吸附实验。这些测试材料是0.8mm厚的无定形PET(污染物的相对水槽)和商用PET瓶壁。使用含有1%林丹(c6h6cl6)的商业洗发水,将测试材料与洗发水在20和40°C下接触储存231天。这款商业洗发水也是一个极端的例子,因为它含有7%的丙酮,这种溶剂会使PET膨胀,进一步增强化学物质的吸收。另外,通过制备10%甲苯米格里醇(一种分馏椰子油)溶液、10%二苯甲酮米格里醇溶液、5% 2-丁氧乙氧基乙醇(2-BE) / 50/50水/乙醇溶液和10%硬脂酸甲酯/庚烷溶液,对PET进行吸附实验。从洗发水到PET的吸附数据说明了菲克行为。具体来说,室温下的吸附量比40℃下的吸附量少40倍。在20℃和40℃下,231天后从洗发水中吸附到PET中的林丹量分别为0.1和3.7mg dm -2。这些值在质量/质量基础上对应于28和765mgkg -1。所有的吸附量都在其他作者使用替代污染测试方案测量和发表的范围内。此外,对回收箱内的实际瓶子进行了污染量分析。结果讨论了消费者在由回收PET制成的食品容器中接触非食品污染物的潜在风险,以及食品和药物管理局(FDA)推荐的替代测试方法,以确定PET回收过程与生产适合食品接触使用的容器的兼容性。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Evaluating the potential for recycling all PET bottles into new food packaging
To evaluate the feasibility of recycling all PET bottles into food packaging, realistic estimates of the maximum concentration of contaminants that might be expected in the polymer are needed. To estimate the maximum concentration of a contaminant that might be in PET from the storage of non-food substances, sorption experiments into two types of PET were performed. These test materials were 0.8mm thick amorphous PET (a relative sink for contaminants) and commercial PET bottle wall. Using a commercial shampoo containing 1% lindane (C 6 H 6 Cl 6), the test materials were stored in contact with the shampoo at 20 and 40 ° C for 231 days. This commercial shampoo also represents an extreme case because it contains 7% acetone, a solvent which swells PET, further enhancing sorption of chemicals. Additional sorption experiments into PET were performed by preparing solutions of 10% toluene in Miglyol (a fractionated coconut oil), 10% benzophenone in Miglyol, 5% 2-butoxyethoxy ethanol (2-BE) in 50/50 water/ethanol, and 10% methyl stearate in heptane. Sorption data from the shampoo into PET illustrate Fickian behaviour. Specifically, the amount of sorption at room temperature is 40 times less than that at 40 ° C. The amount of lindane sorbed into PET from the shampoo after 231 days was 0.1 and 3.7mg dm -2 at 20 and 40 ° C respectively. These values correspond to 28 and 765mgkg -1 on a mass/mass basis. All sorptions are within the ranges measured and published by other authors using surrogate contamination testing schemes. Additionally, actual bottles from recycle bins were analysed for the amount of contamination. Results are discussed in terms of potential consumer exposure to non-food contaminants in food containers made of recycled PET and in relation to the surrogate testing methods recommended by the Food and Drug Administration (FDA) for determining the compatibility of a PET recycling process to produce containers suitable for food-contact use.
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