Methods for the collection and characterization of airborne particles in the textile industry

E. Visileanu, Marian Catalin Grosu, Paul Tiberiu Miclea, K. Altmann, D. Broßell
{"title":"Methods for the collection and characterization of airborne particles in\n the textile industry","authors":"E. Visileanu, Marian Catalin Grosu, Paul Tiberiu Miclea, K. Altmann, D. Broßell","doi":"10.54941/ahfe1004132","DOIUrl":null,"url":null,"abstract":"Airborne particulate matter is one of the main air pollutants. Their\n impact on mortality, and the occurrence of pulmonary and cardiovascular\n complications, have been the subject of numerous studies. Airborne particles\n are complex mixtures of organic and inorganic substances from different\n sources of particle emissions. Particulate Matter (PM) particles are\n classified according to their aerodynamic diameter expressed in µm and can\n vary from coarse (PM 10) to fine (less than PM 2.5). These diameter\n considerations are fundamental because they condition the penetration of\n particles into the bronchopulmonary system and the body. In recent years,\n there has been an interest in so-called “ultra-fine” particles, with a\n diameter of 0.1 µm (or 100 nm), or PM 0.1. They are nanoparticles and their\n impact on human health is not yet clear.With more than 1.5 million\n employees, textiles and clothing is a diverse sector that plays an important\n role in the European manufacturing industry, producing a turnover of €162\n billion.An important component of the solid particles that generate air\n pollution in the textile industry is microplastics (MP) and nano plastics\n (NP), which also include microfibers (<5mm) and nanofibers (<100\n nm), respectively. The particles released into the air during fiber and yarn\n processing range from 1 µg/m3 to 50 µg/m3.The paper presents the results of\n the determination of indoor and outdoor air concentration levels in textile\n companies, to identify the areas with the highest concentration level, by\n using an online recording system such as the Laser Aerosol Spectrometer MINI\n LAS model 11-E. The total concentration level TSP (µg/m3), the fractions PM\n 10(µg/m3), PM 2.5(µg/m3), PM1(µg/m3), as well as the total number of\n particles TC (1/l), were shown. It was noted that TSP is approximately at\n the same level both indoors and outdoors, but the fractions of PM10, PM2.5,\n and PM1 have much higher values indoors than outdoors with possible\n consequences on workers' health.The next step was the collection of fibers,\n namely micro and nano plastic particles from the vicinity of the workplaces\n of polyester, polyamide, and polypropylene fibers processing units in the\n textile industry in Romania, to obtain a sufficient quantity for laboratory\n analysis to determine the size and shape of the particles as well as their\n chemical composition. Two types of pumps were used, differentiated by their\n operating parameters: TECORA SKYPOST with airflow of 38 l/min and GILAIRPLUS\n with airflow 2l/min. Filters made of different materials with different\n diameters and pore sizes were used, namely: quartz filters (ø 47 mm, and ø\n 37 mm) on a TECORA SKYPOST type pump, polycarbonate nucleopore coated with a\n gold membrane (ø 25 mm) and silica filter (ø 9 mm) on GILAIRPLUS type\n pump.Using descriptive statistics, the calculation of correlation\n coefficients highlighted a strong correlation between the variables:\n \"Collected mass/ Air concentration\" and \"Collected mass/ Air volume\" for all\n diameters of the filters.The highest collected particle volume, determined\n by weighing the filters before and after collection, was obtained with the\n quartz filters (ø 47 mm) at an airflow of 38 l/min. The particles collected\n (polyester, polyamide, polypropylene) in the first stage were analyzed by\n SEM and thermogravimetric and it was found that the quartz filters absorbed\n the particles inside, with very few remaining on the surface. Thus no known\n methods can be used to perform analysis for particles collected on quartz\n filters. The number of particles on the filters was insufficient for\n analysis either because of the collection parameters used or because of the\n loss of particles during transport. As a result, in the next step, the use\n of 9 mm Si filters using the GILAIRPLUS pump at an airflow rate of 2l/min\n was chosen.To improve the transport conditions and avoid the loss of the\n particles and keep them on the surface of the filters, two methods were\n applied:- after weighing the filters were reintroduced into the collection\n pump holder;- a filtration system for airborne micro-nano plastics was\n designed and manufactured to selectively collect and transport PM10 and PM1\n particles collected on SI filters.In both cases, SEM, Raman mapping, and\n GS-MS microscopy were used for analysis.Several times more PM10 than PM1\n (74.5µg compared to 12.5 µg) was found. In all cases, both particles and\n fibers showed the same Raman fingerprint.The GS-MS analyses showed some\n contamination of the workspaces with particles other than the processed\n fibers. The presence of non-notifiable substances was also observed.The most\n viable filters are Si filters with a pore size of 10 microns to 1 micron and\n the use of the selected collection and transport filter system. In the\n following a filter system will be applied for collection on Au\n membrane-coated polycarbonate filters.","PeriodicalId":231376,"journal":{"name":"Human Systems Engineering and Design (IHSED 2023): Future Trends\n and Applications","volume":null,"pages":null},"PeriodicalIF":0.0000,"publicationDate":"1900-01-01","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":null,"platform":"Semanticscholar","paperid":null,"PeriodicalName":"Human Systems Engineering and Design (IHSED 2023): Future Trends\n and Applications","FirstCategoryId":"1085","ListUrlMain":"https://doi.org/10.54941/ahfe1004132","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"","JCRName":"","Score":null,"Total":0}
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Abstract

Airborne particulate matter is one of the main air pollutants. Their impact on mortality, and the occurrence of pulmonary and cardiovascular complications, have been the subject of numerous studies. Airborne particles are complex mixtures of organic and inorganic substances from different sources of particle emissions. Particulate Matter (PM) particles are classified according to their aerodynamic diameter expressed in µm and can vary from coarse (PM 10) to fine (less than PM 2.5). These diameter considerations are fundamental because they condition the penetration of particles into the bronchopulmonary system and the body. In recent years, there has been an interest in so-called “ultra-fine” particles, with a diameter of 0.1 µm (or 100 nm), or PM 0.1. They are nanoparticles and their impact on human health is not yet clear.With more than 1.5 million employees, textiles and clothing is a diverse sector that plays an important role in the European manufacturing industry, producing a turnover of €162 billion.An important component of the solid particles that generate air pollution in the textile industry is microplastics (MP) and nano plastics (NP), which also include microfibers (<5mm) and nanofibers (<100 nm), respectively. The particles released into the air during fiber and yarn processing range from 1 µg/m3 to 50 µg/m3.The paper presents the results of the determination of indoor and outdoor air concentration levels in textile companies, to identify the areas with the highest concentration level, by using an online recording system such as the Laser Aerosol Spectrometer MINI LAS model 11-E. The total concentration level TSP (µg/m3), the fractions PM 10(µg/m3), PM 2.5(µg/m3), PM1(µg/m3), as well as the total number of particles TC (1/l), were shown. It was noted that TSP is approximately at the same level both indoors and outdoors, but the fractions of PM10, PM2.5, and PM1 have much higher values indoors than outdoors with possible consequences on workers' health.The next step was the collection of fibers, namely micro and nano plastic particles from the vicinity of the workplaces of polyester, polyamide, and polypropylene fibers processing units in the textile industry in Romania, to obtain a sufficient quantity for laboratory analysis to determine the size and shape of the particles as well as their chemical composition. Two types of pumps were used, differentiated by their operating parameters: TECORA SKYPOST with airflow of 38 l/min and GILAIRPLUS with airflow 2l/min. Filters made of different materials with different diameters and pore sizes were used, namely: quartz filters (ø 47 mm, and ø 37 mm) on a TECORA SKYPOST type pump, polycarbonate nucleopore coated with a gold membrane (ø 25 mm) and silica filter (ø 9 mm) on GILAIRPLUS type pump.Using descriptive statistics, the calculation of correlation coefficients highlighted a strong correlation between the variables: "Collected mass/ Air concentration" and "Collected mass/ Air volume" for all diameters of the filters.The highest collected particle volume, determined by weighing the filters before and after collection, was obtained with the quartz filters (ø 47 mm) at an airflow of 38 l/min. The particles collected (polyester, polyamide, polypropylene) in the first stage were analyzed by SEM and thermogravimetric and it was found that the quartz filters absorbed the particles inside, with very few remaining on the surface. Thus no known methods can be used to perform analysis for particles collected on quartz filters. The number of particles on the filters was insufficient for analysis either because of the collection parameters used or because of the loss of particles during transport. As a result, in the next step, the use of 9 mm Si filters using the GILAIRPLUS pump at an airflow rate of 2l/min was chosen.To improve the transport conditions and avoid the loss of the particles and keep them on the surface of the filters, two methods were applied:- after weighing the filters were reintroduced into the collection pump holder;- a filtration system for airborne micro-nano plastics was designed and manufactured to selectively collect and transport PM10 and PM1 particles collected on SI filters.In both cases, SEM, Raman mapping, and GS-MS microscopy were used for analysis.Several times more PM10 than PM1 (74.5µg compared to 12.5 µg) was found. In all cases, both particles and fibers showed the same Raman fingerprint.The GS-MS analyses showed some contamination of the workspaces with particles other than the processed fibers. The presence of non-notifiable substances was also observed.The most viable filters are Si filters with a pore size of 10 microns to 1 micron and the use of the selected collection and transport filter system. In the following a filter system will be applied for collection on Au membrane-coated polycarbonate filters.
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纺织工业中空气中微粒的收集和表征方法
大气颗粒物是主要的大气污染物之一。它们对死亡率的影响,以及肺部和心血管并发症的发生,一直是许多研究的主题。空气中的颗粒是来自不同颗粒排放源的有机和无机物质的复杂混合物。颗粒物(PM)根据其空气动力学直径(以微米表示)进行分类,可以从粗(PM 10)到细(小于PM 2.5)不等。这些直径的考虑是基本的,因为它们条件颗粒渗透到支气管肺系统和身体。近年来,人们对所谓的“超细”颗粒产生了兴趣,这种颗粒的直径为0.1微米(或100纳米),或PM 0.1。它们是纳米粒子,它们对人类健康的影响尚不清楚。拥有超过150万名员工的纺织和服装是一个多元化的行业,在欧洲制造业中扮演着重要的角色,创造了1620亿欧元的营业额。在纺织工业中产生空气污染的固体颗粒的一个重要组成部分是微塑料(MP)和纳米塑料(NP),它们还分别包括微纤维(<5mm)和纳米纤维(<100 nm)。在纤维和纱线加工过程中释放到空气中的颗粒在1µg/m3到50µg/m3之间。本文介绍了利用激光气溶胶光谱仪(Laser Aerosol Spectrometer MINI LAS model 11-E)等在线记录系统对纺织企业室内和室外空气浓度水平的测定结果,以确定浓度最高的区域。显示了总浓度水平TSP(µg/m3), pm10(µg/m3), PM 2.5(µg/m3), PM1(µg/m3),以及总颗粒数TC (1/l)。报告指出,室内和室外的总悬浮颗粒物大致相同,但室内PM10、PM2.5和PM1的含量远高于室外,这可能对工人的健康产生影响。下一步是收集纤维,即来自罗马尼亚纺织工业中聚酯、聚酰胺和聚丙烯纤维加工单位工作场所附近的微纳米塑料颗粒,以获得足够的数量进行实验室分析,以确定颗粒的大小和形状及其化学成分。使用了两种类型的泵,根据其运行参数进行区分:气流为38升/分钟的TECORA SKYPOST和气流为21升/分钟的GILAIRPLUS。采用不同材料制成的不同直径和孔径的过滤器,即:TECORA SKYPOST型泵上的石英过滤器(ø 47 mm和ø 37 mm), GILAIRPLUS型泵上的聚碳酸酯核孔包覆金膜(ø 25 mm)和二氧化硅过滤器(ø 9 mm)。使用描述性统计,相关系数的计算突出了所有过滤器直径的“收集质量/空气浓度”和“收集质量/空气体积”变量之间的强相关性。石英过滤器(ø 47 mm)在38 l/min的气流下,通过对过滤器收集前后的称重来确定收集的颗粒体积最大。对第一阶段收集的颗粒(聚酯、聚酰胺、聚丙烯)进行扫描电镜和热重分析,发现石英过滤器吸收了内部的颗粒,表面残留的颗粒很少。因此,没有已知的方法可以用于对石英过滤器上收集的颗粒进行分析。由于所使用的收集参数或由于在运输过程中颗粒的损失,过滤器上的颗粒数量不足以进行分析。因此,在下一步中,选择使用GILAIRPLUS泵以2l/min的气流速率使用9 mm Si过滤器。为了改善输送条件,避免颗粒的损失并使其保持在过滤器表面,采用了两种方法:称重后将过滤器重新引入收集泵支架;设计并制造了一种机载微纳塑料过滤系统,选择性地收集和输送SI过滤器上收集的PM10和PM1颗粒。在这两种情况下,使用SEM,拉曼图谱和GS-MS显微镜进行分析。PM10(74.5µg)比PM1(12.5µg)多出数倍。在所有情况下,颗粒和纤维都显示出相同的拉曼指纹。GS-MS分析显示,除了加工过的纤维外,还有一些颗粒污染了工作区。还观察到存在非申报物质。最可行的过滤器是孔径为10微米至1微米的硅过滤器,并使用选定的收集和传输过滤系统。在下面的过滤系统将应用于收集金膜涂层的聚碳酸酯过滤器。
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