Characterization of a solid recovered fuel for prediction of its thermal degradation

Sylvie Valin, Tiphaine Benoist, Sylvain Salvador
{"title":"Characterization of a solid recovered fuel for prediction of its thermal degradation","authors":"Sylvie Valin,&nbsp;Tiphaine Benoist,&nbsp;Sylvain Salvador","doi":"10.1007/s42768-025-00258-x","DOIUrl":null,"url":null,"abstract":"<div><p>The objective is to characterize one solid recovered fuel (SRF) and to determine a mixture of model components to represent each of its fractions, both in terms of elemental composition and thermal degradation kinetics. The SRF was first sorted into fractions: hard plastic (21%, mass fraction), soft plastic (12%), wood (15%), paper and cardboard (13%), textile (11%), elastomer (6%), foam (4%), expanded polystyrene (PS, 3%), inert (6%) and fine particles (9%). The SRF fractions and selected model components were characterized in detail via thermogravimetric analysis (TGA), Fourier transformed infrared spectroscopy (FTIR), X-ray diffraction (XRD), and scanning electron microscopy (SEM) coupled with energy dispersive X-ray spectroscopy (EDX). The results confirmed the relevance or presence of a list of model components for each fraction. In the second step, the mass fractions of the model components in the mixtures were calculated for each SRF fraction, with a mathematical optimization method based only on the elemental analysis results. These mixtures succeeded in representing the compositions of the fractions, both for organic and inorganic elements. The hard plastic fraction mainly contains polyethylene (PE) and polypropylene (PP) at 38.6% each, as do PS (5.0%) and polyvinylchloride (PVC, 10.9%). The soft plastic fraction is well represented by PE. The textile fraction is complex and includes cotton (15.0%), polyethylene terephthalate (PET, 40.5%), PP (20.9%), and acrylic (5.2%). The fine particle fraction is rich in pollutants: soil (29.8%), plaster (20.3%), and glass wool (5.0%). The consideration of these fine particles in the SRF composition is thus crucial for determining the sources of inorganic elements.</p><h3>Graphical abstract</h3>\n<div><figure><div><div><picture><source><img></source></picture></div></div></figure></div></div>","PeriodicalId":807,"journal":{"name":"Waste Disposal & Sustainable Energy","volume":"7 4","pages":"591 - 609"},"PeriodicalIF":0.0000,"publicationDate":"2025-10-30","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":null,"platform":"Semanticscholar","paperid":null,"PeriodicalName":"Waste Disposal & Sustainable Energy","FirstCategoryId":"6","ListUrlMain":"https://link.springer.com/article/10.1007/s42768-025-00258-x","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"","JCRName":"","Score":null,"Total":0}
引用次数: 0

Abstract

The objective is to characterize one solid recovered fuel (SRF) and to determine a mixture of model components to represent each of its fractions, both in terms of elemental composition and thermal degradation kinetics. The SRF was first sorted into fractions: hard plastic (21%, mass fraction), soft plastic (12%), wood (15%), paper and cardboard (13%), textile (11%), elastomer (6%), foam (4%), expanded polystyrene (PS, 3%), inert (6%) and fine particles (9%). The SRF fractions and selected model components were characterized in detail via thermogravimetric analysis (TGA), Fourier transformed infrared spectroscopy (FTIR), X-ray diffraction (XRD), and scanning electron microscopy (SEM) coupled with energy dispersive X-ray spectroscopy (EDX). The results confirmed the relevance or presence of a list of model components for each fraction. In the second step, the mass fractions of the model components in the mixtures were calculated for each SRF fraction, with a mathematical optimization method based only on the elemental analysis results. These mixtures succeeded in representing the compositions of the fractions, both for organic and inorganic elements. The hard plastic fraction mainly contains polyethylene (PE) and polypropylene (PP) at 38.6% each, as do PS (5.0%) and polyvinylchloride (PVC, 10.9%). The soft plastic fraction is well represented by PE. The textile fraction is complex and includes cotton (15.0%), polyethylene terephthalate (PET, 40.5%), PP (20.9%), and acrylic (5.2%). The fine particle fraction is rich in pollutants: soil (29.8%), plaster (20.3%), and glass wool (5.0%). The consideration of these fine particles in the SRF composition is thus crucial for determining the sources of inorganic elements.

Graphical abstract

固体回收燃料的表征及其热降解预测
目标是表征一种固体回收燃料(SRF),并确定模型成分的混合物,以代表其每个馏分,包括元素组成和热降解动力学。SRF首先被分成几个部分:硬塑料(21%,质量分数)、软塑料(12%)、木材(15%)、纸和纸板(13%)、纺织品(11%)、弹性体(6%)、泡沫(4%)、膨胀聚苯乙烯(PS, 3%)、惰性(6%)和细颗粒(9%)。通过热重分析(TGA)、傅里叶变换红外光谱(FTIR)、x射线衍射(XRD)、扫描电子显微镜(SEM)和能量色散x射线光谱(EDX)对SRF组分和选定的模型组分进行了详细的表征。结果证实了每个部分的模型组件列表的相关性或存在性。第二步,计算每个SRF分数下模型组分在混合物中的质量分数,采用仅基于元素分析结果的数学优化方法。这些混合物成功地代表了有机和无机元素的组分。硬塑料部分主要为聚乙烯(PE)和聚丙烯(PP),各占38.6%,PS(5.0%)和聚氯乙烯(PVC)占10.9%。软塑性部分以PE为代表。纺织组分复杂,包括棉花(15.0%)、聚对苯二甲酸乙二醇酯(PET, 40.5%)、PP(20.9%)和丙烯酸(5.2%)。细颗粒部分含有丰富的污染物:土壤(29.8%)、灰泥(20.3%)、玻璃棉(5.0%)。因此,考虑SRF组成中的这些细颗粒对于确定无机元素的来源至关重要。图形抽象
本文章由计算机程序翻译,如有差异,请以英文原文为准。
求助全文
约1分钟内获得全文 求助全文
来源期刊
自引率
0.00%
发文量
0
×
引用
GB/T 7714-2015
复制
MLA
复制
APA
复制
导出至
BibTeX EndNote RefMan NoteFirst NoteExpress
×
提示
您的信息不完整,为了账户安全,请先补充。
现在去补充
×
提示
您因"违规操作"
具体请查看互助需知
我知道了
×
提示
确定
请完成安全验证×
copy
已复制链接
快去分享给好友吧!
我知道了
右上角分享
点击右上角分享
0
联系我们:info@booksci.cn Book学术提供免费学术资源搜索服务,方便国内外学者检索中英文文献。致力于提供最便捷和优质的服务体验。 Copyright © 2023 布克学术 All rights reserved.
京ICP备2023020795号-1
ghs 京公网安备 11010802042870号
Book学术文献互助
Book学术文献互助群
群 号:604180095
Book学术官方微信
小红书