堆肥对聚烯烃薄膜性能的影响——一个真实的实验

V. Vargha, Tamás Csoknyay, L. Kárpáti, Gábor Bordós, M. Hartman, J. Háhn, L. Korecz, G. Szarka, Zsolt László, O. Kelemen, S. Szoboszlay
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引用次数: 0

摘要

将商用聚丙烯(PP)、高、中、低密度聚乙烯(HDPE、MDPE、LDPE)薄膜以及含有促氧化添加剂和热塑性淀粉(TPS)的MDPE薄膜与生物可降解薄膜(如聚乳酸(PLA)、Ecovio (BASF)、Mater Bi(Novamont)和玻璃纸)一起堆肥6周。聚烯烃基薄膜的视觉外观没有明显变化,而生物可降解薄膜则分崩离析。聚烯烃基薄膜的厚度和力学性能在堆肥后也没有显著变化。然而,可降解膜的厚度由于生物膜的形成而增加,最终由于生物降解而减少,其力学性能急剧下降。傅里叶红外光谱(FTIR)证实了堆肥后由于氧化作用形成羰基吸收膜(分别为商业膜和含添加剂膜)。生物降解膜的ftir光谱在堆肥后发生了较大的变化。采用esr -光谱法检测了含有MDPE膜的促氧化添加剂在阳光下曝晒一周后自由基的形成,堆肥后自由基的形成强度增加。添加促氧化添加剂的MDPE薄膜经过堆肥处理后,其数平均分子质量下降,出现低分子质量分数,多分散性增加。通过扫描电镜检测,商业聚烯烃薄膜被微生物覆盖的密度远高于含有促氧化添加剂的薄膜。即使TPS也没有增加微生物的数量。生物可降解膜被不同类型的微生物密集覆盖,表面多孔,可见孔洞。综上所述,堆肥对商用PP和PE薄膜的性能没有显著影响。添加了促氧化添加剂和TPS的MDPE薄膜在堆肥6周后出现了初步降解的迹象,但不能认为是生物降解。所有测试的聚烯烃薄膜在堆肥中都没有生物可降解薄膜那样的降解程度。由此可见,聚烯烃薄膜在堆肥中既不能降解,也不能进行生物降解。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Effect of Composting on the Behavior of Polyolefin Films – A True-to-Life Experiment
Commercial polypropylene (PP), high-, medium- and low density polyethylene (HDPE, MDPE, LDPE) films, as well as MDPE films containing pro-oxidative additives and thermoplastic starch (TPS) were composted for six weeks together with biologically degradable films, such as poly (lactic acid) (PLA), Ecovio (BASF), Mater Bi(Novamont) and cellophane. Visual appearance of the polyolefin-based films did not change significantly, while the biologically degradable films fell apart. Thickness and mechanical properties of the polyolefin-based films also did not vary significantly after composting. The thickness of the degradable films however increased due to biofilm formation and finally decreased due to biodegradation, and their mechanical properties drastically dropped. FTIR proved the formation of carbonyl absorption of commercial and of the additive-containing films respectively) after composting due to oxidation. The FTIR-spectrum of the biodegradable films showed drastic change after composting. Formation of free radicals was detectable by ESR-spectroscopy, if pro-oxidative additive containing MDPE film was exposed for one week to sunlight, and the intensity of free radical formation increased after composting. The number-average molecular mass of MDPE films containing pro-oxidative additives decreased, low molecular mass fractions appeared and polydispersity increased after composting. Commercial polyolefin films were covered by microorganisms much more densly than films containing pro-oxidative additives detected by SEM. Even TPS did not increase the quantity of microorganisms. Biodegradable films were densly covered by microorganisms of different types and they became porous and holes were observable on their surface. It can be concluded that composting had no significant effect on the behaviour of the commercial PP and PE films. Signs of initial degradation were observable on MDPE films with pro-oxidative additives and TPS after 6 weeks composting, although it cannot be considered as biological degradation. Non of the tested polyolefin films suffered such degree of degradation in compost, as the biologically degradable films. It may be concluded that polyolefin films neither degrade in compost nor they undergo biodegradation.
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