• 文献检索
  • 文档翻译
  • 深度研究
  • 学术资讯
  • Suppr Zotero 插件Zotero 插件
  • 邀请有礼
  • 套餐&价格
  • 历史记录
应用&插件
Suppr Zotero 插件Zotero 插件浏览器插件Mac 客户端Windows 客户端微信小程序
定价
高级版会员购买积分包购买API积分包
服务
文献检索文档翻译深度研究API 文档MCP 服务
关于我们
关于 Suppr公司介绍联系我们用户协议隐私条款
关注我们

Suppr 超能文献

核心技术专利:CN118964589B侵权必究
粤ICP备2023148730 号-1Suppr @ 2026

文献检索

告别复杂PubMed语法,用中文像聊天一样搜索,搜遍4000万医学文献。AI智能推荐,让科研检索更轻松。

立即免费搜索

文件翻译

保留排版,准确专业,支持PDF/Word/PPT等文件格式,支持 12+语言互译。

免费翻译文档

深度研究

AI帮你快速写综述,25分钟生成高质量综述,智能提取关键信息,辅助科研写作。

立即免费体验

回收过程中苯乙烯类塑料的降解:电子电气设备塑料不完全分类后聚丙烯在丙烯腈-丁二烯-苯乙烯共聚物中的容纳情况

Degradation of Styrenic Plastics during Recycling: Accommodation of PP within ABS after WEEE Plastics Imperfect Sorting.

作者信息

Signoret Charles, Girard Pierre, Guen Agathe Le, Caro-Bretelle Anne-Sophie, Lopez-Cuesta José-Marie, Ienny Patrick, Perrin Didier

机构信息

Polymers Composites and Hybrids (PCH), IMT Mines Ales, 30100 Ales, France.

LMGC, IMT Mines Ales, Université Montpellier, CNRS, 30100 Ales, France.

出版信息

Polymers (Basel). 2021 Apr 29;13(9):1439. doi: 10.3390/polym13091439.

DOI:10.3390/polym13091439
PMID:33947020
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC8124459/
Abstract

With the development of dark polymers for industrial sorting technologies, economically profitable recycling of plastics from Waste Electrical and Electronical Equipment (WEEE) can be envisaged even in the presence of residual impurities. In ABS extracted from WEEE, PP is expected to be the more detrimental because of its important lack of compatibility. Hence, PP was incorporated to ABS at different rates (2 to 8 wt%) with a twin-screw extruder. PP was shown to exhibit a nodular morphology with an average diameter around 1-2 µm. Tensile properties were importantly diminished beyond 4 wt% but impact resistance was decreased even at 2 wt%. Both properties were strongly reduced as function of the contamination rate. Various potential compatibilizers for the ABS + 4 wt% PP system were evaluated: PPH-g-MA, PPC-g-MA, ABS-g-MA, TPE-g-MA, SEBS and PP-g-SAN. SEBS was found the most promising, leading to diminution of nodule sizes and also acting as an impact modifier. Finally, a Design Of Experiments using the Response Surface Methodology (DOE-RSM) was applied to visualize the impacts and interactions of extrusion temperature and screw speed on impact resistance of compatibilized and uncompatibilized ABS + 4 wt% PP systems. Resilience improvements were obtained for the uncompatibilized system and interactions between extrusion parameters and compatibilizers were noticed.

摘要

随着用于工业分选技术的深色聚合物的发展,即使存在残留杂质,也可以设想从废弃电气和电子设备(WEEE)中经济高效地回收塑料。在从WEEE中提取的ABS中,由于PP与ABS的相容性很差,预计它是更有害的杂质。因此,使用双螺杆挤出机以不同比例(2至8 wt%)将PP混入ABS中。结果表明,PP呈现出平均直径约为1-2 µm的结节形态。当PP含量超过4 wt%时,拉伸性能显著降低,但即使在2 wt%时抗冲击性也会下降。这两种性能均随着污染率的增加而大幅降低。对ABS + 4 wt% PP体系的各种潜在增容剂进行了评估:PPH-g-MA、PPC-g-MA、ABS-g-MA、TPE-g-MA、SEBS和PP-g-SAN。结果发现SEBS最具潜力,它不仅能减小结节尺寸,还可作为抗冲击改性剂。最后,采用响应面法(DOE-RSM)进行实验设计,以观察挤出温度和螺杆转速对增容和未增容的ABS + 4 wt% PP体系抗冲击性的影响及相互作用。未增容体系的回弹性得到了改善,并且注意到挤出参数与增容剂之间存在相互作用。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/70e5/8124459/0649da2fecbf/polymers-13-01439-g018.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/70e5/8124459/2f3a7f128cb1/polymers-13-01439-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/70e5/8124459/dfd006ead8fd/polymers-13-01439-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/70e5/8124459/3d02f48809b7/polymers-13-01439-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/70e5/8124459/9a0da310b2bd/polymers-13-01439-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/70e5/8124459/f85684344dfd/polymers-13-01439-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/70e5/8124459/2100dee622b2/polymers-13-01439-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/70e5/8124459/b130dc80347b/polymers-13-01439-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/70e5/8124459/29d542cd1d07/polymers-13-01439-g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/70e5/8124459/0e364a0e9ee2/polymers-13-01439-g009.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/70e5/8124459/4342850b634f/polymers-13-01439-g010.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/70e5/8124459/bab9aea1d760/polymers-13-01439-g011.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/70e5/8124459/e37c10d33516/polymers-13-01439-g012.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/70e5/8124459/f37018f309a0/polymers-13-01439-g013.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/70e5/8124459/db76bb9cc6ed/polymers-13-01439-g014.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/70e5/8124459/feeb142238d1/polymers-13-01439-g015.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/70e5/8124459/d7ff0c9bad7d/polymers-13-01439-g016.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/70e5/8124459/c583dae6f061/polymers-13-01439-g017.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/70e5/8124459/0649da2fecbf/polymers-13-01439-g018.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/70e5/8124459/2f3a7f128cb1/polymers-13-01439-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/70e5/8124459/dfd006ead8fd/polymers-13-01439-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/70e5/8124459/3d02f48809b7/polymers-13-01439-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/70e5/8124459/9a0da310b2bd/polymers-13-01439-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/70e5/8124459/f85684344dfd/polymers-13-01439-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/70e5/8124459/2100dee622b2/polymers-13-01439-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/70e5/8124459/b130dc80347b/polymers-13-01439-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/70e5/8124459/29d542cd1d07/polymers-13-01439-g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/70e5/8124459/0e364a0e9ee2/polymers-13-01439-g009.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/70e5/8124459/4342850b634f/polymers-13-01439-g010.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/70e5/8124459/bab9aea1d760/polymers-13-01439-g011.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/70e5/8124459/e37c10d33516/polymers-13-01439-g012.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/70e5/8124459/f37018f309a0/polymers-13-01439-g013.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/70e5/8124459/db76bb9cc6ed/polymers-13-01439-g014.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/70e5/8124459/feeb142238d1/polymers-13-01439-g015.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/70e5/8124459/d7ff0c9bad7d/polymers-13-01439-g016.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/70e5/8124459/c583dae6f061/polymers-13-01439-g017.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/70e5/8124459/0649da2fecbf/polymers-13-01439-g018.jpg

相似文献

1
Degradation of Styrenic Plastics during Recycling: Accommodation of PP within ABS after WEEE Plastics Imperfect Sorting.回收过程中苯乙烯类塑料的降解:电子电气设备塑料不完全分类后聚丙烯在丙烯腈-丁二烯-苯乙烯共聚物中的容纳情况
Polymers (Basel). 2021 Apr 29;13(9):1439. doi: 10.3390/polym13091439.
2
A sustainable approach toward mechanical recycling unsortable post-consumer WEEE: Reactive and non-reactive compatibilization.一种针对消费后不可分类电子电气废弃物进行机械回收的可持续方法:反应性和非反应性增容。
Waste Manag. 2024 Apr 15;178:301-310. doi: 10.1016/j.wasman.2024.02.016. Epub 2024 Feb 28.
3
Impact of PP Impurities on ABS Tensile Properties: Computational Mechanical Modelling Aspects.聚丙烯杂质对丙烯腈-丁二烯-苯乙烯共聚物拉伸性能的影响:计算力学建模方面
Polymers (Basel). 2021 May 19;13(10):1647. doi: 10.3390/polym13101647.
4
Recycling of mixed plastic waste from electrical and electronic equipment. Added value by compatibilization.电子电气设备混合塑料废物的回收。通过增容实现附加值。
Waste Manag. 2016 Jul;53:196-203. doi: 10.1016/j.wasman.2016.04.022. Epub 2016 Apr 29.
5
Tailoring PLA/ABS Blends Compatibilized with SEBS-g-MA through Annealing Heat Treatment.通过退火热处理定制与 SEBS-g-MA 相容的 PLA/ABS 共混物。
Polymers (Basel). 2023 Aug 17;15(16):3434. doi: 10.3390/polym15163434.
6
MIR spectral characterization of plastic to enable discrimination in an industrial recycling context: I. Specific case of styrenic polymers.MIR 光谱特征分析在工业回收中的应用:I. 苯乙烯聚合物的具体案例。
Waste Manag. 2019 Jul 15;95:513-525. doi: 10.1016/j.wasman.2019.05.050. Epub 2019 Jul 1.
7
Influence of impurities on the performances of HIPS recycled from Waste Electric and Electronic Equipment (WEEE).杂质对从废弃电子电气设备(WEEE)中回收的高抗冲聚苯乙烯(HIPS)性能的影响。
Waste Manag. 2016 Oct;56:438-45. doi: 10.1016/j.wasman.2016.07.014. Epub 2016 Jul 15.
8
A Promising Recycling Strategy via Processing Polypropylene/Recycled Poly(ethylene terephthalate): Reactive Extrusion Using Dual Compatibilizers.一种通过处理聚丙烯/回收聚对苯二甲酸乙二酯实现的有前景的回收策略:使用双增容剂的反应挤出
Polymers (Basel). 2024 Aug 28;16(17):2439. doi: 10.3390/polym16172439.
9
Optimization of Surface Treatment Using Sodium Hypochlorite Facilitates Coseparation of ABS and PC from WEEE Plastics by Flotation.使用次氯酸钠优化表面处理通过浮选促进从电子废物塑料中分离 ABS 和 PC。
Environ Sci Technol. 2019 Feb 19;53(4):2086-2094. doi: 10.1021/acs.est.8b06432. Epub 2019 Jan 29.
10
Application of surface modification using sodium hypochlorite for helping flotation separation of acrylonitrile-butadiene-styrene and polystyrene plastics of WEEE.采用次氯酸钠表面改性法辅助从 WEEE 中浮选分离丙烯腈-丁二烯-苯乙烯和聚苯乙烯塑料。
Waste Manag. 2018 Dec;82:167-176. doi: 10.1016/j.wasman.2018.10.031. Epub 2018 Oct 25.

引用本文的文献

1
Review and Assessment of Existing and Future Techniques for Traceability with Particular Focus on Applicability to ABS Plastics.现有及未来可追溯技术的回顾与评估,特别关注其对ABS塑料的适用性。
Polymers (Basel). 2024 May 9;16(10):1343. doi: 10.3390/polym16101343.
2
ABS/Silicon Dioxide Micro Particulate Composite from 3D Printing Polymeric Waste.由3D打印聚合物废料制成的ABS/二氧化硅微颗粒复合材料。
Polymers (Basel). 2022 Jan 27;14(3):509. doi: 10.3390/polym14030509.
3
Impact of PP Impurities on ABS Tensile Properties: Computational Mechanical Modelling Aspects.

本文引用的文献

1
MIR spectral characterization of plastic to enable discrimination in an industrial recycling context: II. Specific case of polyolefins.MIR 光谱特征在塑料中的应用,以实现工业回收领域的区分:II. 聚烯烃的具体案例。
Waste Manag. 2019 Oct;98:160-172. doi: 10.1016/j.wasman.2019.08.010. Epub 2019 Aug 23.
2
Towards a more circular economy for WEEE plastics - Part B: Assessment of the technical feasibility of recycling strategies.迈向更具循环经济的废弃电子电气设备塑料 - 第 B 部分:回收策略技术可行性评估。
Waste Manag. 2019 Aug 1;96:206-214. doi: 10.1016/j.wasman.2019.07.035. Epub 2019 Jul 27.
3
Mechanical and chemical recycling of solid plastic waste.
聚丙烯杂质对丙烯腈-丁二烯-苯乙烯共聚物拉伸性能的影响:计算力学建模方面
Polymers (Basel). 2021 May 19;13(10):1647. doi: 10.3390/polym13101647.
固体塑料废弃物的机械回收与化学回收
Waste Manag. 2017 Nov;69:24-58. doi: 10.1016/j.wasman.2017.07.044. Epub 2017 Aug 18.
4
Production, use, and fate of all plastics ever made.所有塑料制品的生产、使用及去向。
Sci Adv. 2017 Jul 19;3(7):e1700782. doi: 10.1126/sciadv.1700782. eCollection 2017 Jul.
5
Development of a new approach based on midwave infrared spectroscopy for post-consumer black plastic waste sorting in the recycling industry.开发一种基于中波红外光谱的新方法,用于回收行业中消费后黑色塑料废物的分类。
Waste Manag. 2017 Oct;68:38-44. doi: 10.1016/j.wasman.2017.07.023. Epub 2017 Jul 20.
6
Influence of impurities on the performances of HIPS recycled from Waste Electric and Electronic Equipment (WEEE).杂质对从废弃电子电气设备(WEEE)中回收的高抗冲聚苯乙烯(HIPS)性能的影响。
Waste Manag. 2016 Oct;56:438-45. doi: 10.1016/j.wasman.2016.07.014. Epub 2016 Jul 15.
7
Disassembly properties and material characterisation of household small waste electric and electronic equipment.家用小型废弃电器电子产品的拆卸特性与材料特性分析。
Waste Manag. 2016 Jul;53:225-36. doi: 10.1016/j.wasman.2016.04.011. Epub 2016 Apr 29.
8
Forecasting waste compositions: A case study on plastic waste of electronic display housings.预测废弃物成分:以电子显示外壳的塑料废弃物为例。
Waste Manag. 2015 Dec;46:28-39. doi: 10.1016/j.wasman.2015.09.019. Epub 2015 Oct 1.
9
Life cycle assessment of post-consumer plastics production from waste electrical and electronic equipment (WEEE) treatment residues in a Central European plastics recycling plant.中欧某塑料回收厂利用废弃电气电子设备(WEEE)处理残渣生产消费后塑料的生命周期评估。
Sci Total Environ. 2015 Oct 1;529:158-67. doi: 10.1016/j.scitotenv.2015.05.043. Epub 2015 May 25.
10
Rapid discrimination of plastic packaging materials using MIR spectroscopy coupled with independent components analysis (ICA).利用 MIR 光谱结合独立成分分析(ICA)快速鉴别塑料包装材料。
Waste Manag. 2014 Nov;34(11):2131-8. doi: 10.1016/j.wasman.2014.06.015. Epub 2014 Jul 11.