岩棉和耐火陶瓷纤维

C. Rice
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Each has a slightly different formulation and characteristics; therefore it is important where possible to identify the particular product number. \n \n \n \nDimension, durability, and dose delivered to the target organ are critical factors in the toxicity of MMVF. \n \n \n \nMMVF are characterized by length (L) and diameter (D). The arithmetic mean or median of the observed distribution of lengths and diameters may be given as the count mean or median diameter (CMD) or length (CML). If the observed values are transformed by taking the natural logarithm of the measured parameters, the geometric mean (GM) of each dimension may be given with a geometric standard deviation (GSD). The size determinations may be made by either scanning (SEM) or transmission (TEM) electron microscopy. TEM has the lower limits of detection by which investigators can characterize fibers with diameters in the nanometer range. Dose by some routes of administration may be further described by the mass of material, for example, in implantation or single bolus injection studies. For inhalation studies, GM and GSD length and diameter are usually listed for the exposure aerosol, and often the number of fibers within specific size ranges are listed. \n \n \n \nFollowing inhalation, fibers may be deposited on surfaces within the respiratory tract or exhaled. For the fibers that are deposited, the site of deposition (dose) depends upon the characteristics of the fiber and results from one of five mechanisms: impaction, interception, sedimentation, electrostatic precipitation, or diffusion. The majority of the deposition of MMVF is probably governed by the first three mechanisms. Impaction and interception occur when the fiber is removed from the airstream by physically contacting the surface of the airway or a bifurcation. Sedimentation occurs in the lower airways, where the velocity of the fiber becomes low enough for it to settle on the airway surface. Electrostatic precipitation results when the fiber carries a charge opposite to that of the airway surface; for mineral wool fibers, no reports have been found on surface charge measurements. Deposition due to diffusion requires that the air molecules collide with the fiber, resulting in movement toward the surface. This mechanism could contribute to deposition of very thin fibers, e.g., those with diameters substantially less than one-half micron, but few of them are expected in the work environment. \n \n \n \nThe clearance mechanism of the deposited fibers depends upon the characteristics of the fiber and the site of deposition. Fibers deposited in the tracheobronchial region are cleared with the mucous by the cilia and swallowed. This process is completed in a matter of days, during which little change in fiber dimensions would be anticipated. Fibers deposited lower in the respiratory tract are cleared more slowly. Here the fibers are cleared by translocation to another area of the lung or dissolve; translocation may be facilitated by partial dissolution of the fiber or breakage into particles of shorter length. When fibers recovered from the lung or other tissue are characterized by dimensions, comparison with the parent material provides information on deposition and distribution. \n \n \n \nSolubility has been investigated as an indicator of durability. \n \n \n \nThe interpretation of short-term bioassay results is still under study. Bernstein et al. suggested that the results of dissolution at neutral pH are correlated with in vivo biopersistence. Others report that the dissolution rates of MMVF that have high aluminum content are much greater in acidic environments. Evidence from animal studies shows that the macrophages may interact with long fibers and that multiple macrophages attach to a single fiber which can lead to dissolution. \n \n \nKeywords: \n \nMineral wood; \nProduction; \nRock/slag wool; \nRefractory ceramic fiber; \nCommunity methods; \nToxic effects; \nCohort studies; \nStandards; \nRegulation; \nEnvironment; \nOdor; \nWorkplace exposure","PeriodicalId":19820,"journal":{"name":"Patty's Toxicology","volume":null,"pages":null},"PeriodicalIF":0.0000,"publicationDate":"2012-08-17","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"1","resultStr":"{\"title\":\"Rock Wool and Refractory Ceramic Fibers\",\"authors\":\"C. Rice\",\"doi\":\"10.1002/0471435139.TOX014.PUB2\",\"DOIUrl\":null,\"url\":null,\"abstract\":\"Man-made vitreous fibers (MMVF) is a generic descriptor for a group of fibrous materials made from melting inorganic substances such as sand, clay, glass, or slag. 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Electrostatic precipitation results when the fiber carries a charge opposite to that of the airway surface; for mineral wool fibers, no reports have been found on surface charge measurements. Deposition due to diffusion requires that the air molecules collide with the fiber, resulting in movement toward the surface. This mechanism could contribute to deposition of very thin fibers, e.g., those with diameters substantially less than one-half micron, but few of them are expected in the work environment. \\n \\n \\n \\nThe clearance mechanism of the deposited fibers depends upon the characteristics of the fiber and the site of deposition. Fibers deposited in the tracheobronchial region are cleared with the mucous by the cilia and swallowed. This process is completed in a matter of days, during which little change in fiber dimensions would be anticipated. Fibers deposited lower in the respiratory tract are cleared more slowly. 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引用次数: 1

摘要

人造玻璃纤维(MMVF)是一组由熔融无机物(如沙、粘土、玻璃或炉渣)制成的纤维材料的通用描述符。合成玻璃体纤维(SVF)或人造合成玻璃体纤维(MSVF)也可用来描述这类材料。这些术语已普遍取代了早期使用的人造矿物纤维(MMMF)。MMVF按生产中使用的原材料进一步分类;主要类别包括玻璃纤维(玻璃棉或连续长丝)、矿棉(岩石或矿渣)和耐火陶瓷纤维。后两种类型将在本章中讨论;玻璃纤维的描述在第1章中。在每个类别中,已经生产了各种各样的商业产品,可以通过制造商和产品名称和编号来识别。每一种都有稍微不同的配方和特点;因此,在可能的情况下识别特定的产品编号是很重要的。尺寸,持久性和剂量传递到靶器官是MMVF毒性的关键因素。MMVF的特征是长度(L)和直径(D)。观察到的长度和直径分布的算术平均值或中位数可以作为计数平均值或中位数直径(CMD)或长度(CML)给出。如果用测量参数的自然对数对观测值进行变换,则可以给出每个维度的几何平均值(GM)和几何标准差(GSD)。尺寸的测定可以通过扫描(SEM)或透射(TEM)电子显微镜进行。透射电镜具有检测下限,研究人员可以通过它来表征直径在纳米范围内的纤维。某些给药途径的剂量可以进一步用物质的质量来描述,例如,在植入或单丸注射研究中。对于吸入研究,通常列出暴露气溶胶的GM和GSD长度和直径,并且通常列出特定尺寸范围内的纤维数量。吸入后,纤维可能沉积在呼吸道内的表面或呼出。对于沉积的纤维,沉积的位置(剂量)取决于纤维的特性和五种机制之一的结果:撞击、拦截、沉积、静电沉淀或扩散。大多数MMVF的沉积可能由前三种机制控制。当纤维通过物理接触气道表面或分叉从气流中移除时,就会发生撞击和阻断。沉降发生在下气道,在那里纤维的速度变得足够低,使其沉淀在气道表面。当纤维携带的电荷与气道表面的电荷相反时,就会产生静电沉淀;对于矿棉纤维,没有发现关于表面电荷测量的报告。由于扩散导致的沉积需要空气分子与纤维碰撞,从而导致向表面移动。这种机制可能有助于沉积非常薄的纤维,例如,直径大大小于半微米的纤维,但在工作环境中很少有这种纤维。沉积纤维的清除机制取决于纤维的特性和沉积部位。沉积在气管支气管区域的纤维被纤毛与粘液一起清除并吞下。这个过程在几天内完成,在此期间纤维尺寸几乎没有变化。沉积在呼吸道下部的纤维被清除得更慢。在这里,纤维通过转移到肺的其他区域或溶解而被清除;纤维的部分溶解或断裂成较短长度的颗粒,可促进易位。当从肺或其他组织中回收的纤维具有尺寸特征时,与母体材料的比较提供了沉积和分布的信息。溶解度作为耐久性的指标进行了研究。短期生物测定结果的解释仍在研究中。Bernstein等人认为,在中性pH下的溶解结果与体内生物持久性相关。也有人报告说,高铝含量的MMVF在酸性环境中的溶解速度要大得多。动物实验的证据表明,巨噬细胞可能与长纤维相互作用,多个巨噬细胞附着在一根纤维上,导致纤维溶解。关键词:矿物木材;生产;摇滚/渣棉;耐火陶瓷纤维;社区的方法;毒性作用;队列研究;标准;监管;环境;的气味;工作场所的暴露
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Rock Wool and Refractory Ceramic Fibers
Man-made vitreous fibers (MMVF) is a generic descriptor for a group of fibrous materials made from melting inorganic substances such as sand, clay, glass, or slag. Synthetic vitreous fibers (SVF) or man-made synthetic vitreous fibers (MSVF) may also be used to describe these groups of materials. These terms have generally replaced earlier use of man-made mineral fibers (MMMF). MMVF are further classified by the raw material used in production; major categories include glass fibers (glass wool or continuous filament), mineral wool (rock or slag), and refractory ceramic fibers. The latter two types are covered in this chapter; glass fibers are described in Chapter. Within each category, a variety of commercial products have been produced and may be identified by manufacturer and product name and number. Each has a slightly different formulation and characteristics; therefore it is important where possible to identify the particular product number. Dimension, durability, and dose delivered to the target organ are critical factors in the toxicity of MMVF. MMVF are characterized by length (L) and diameter (D). The arithmetic mean or median of the observed distribution of lengths and diameters may be given as the count mean or median diameter (CMD) or length (CML). If the observed values are transformed by taking the natural logarithm of the measured parameters, the geometric mean (GM) of each dimension may be given with a geometric standard deviation (GSD). The size determinations may be made by either scanning (SEM) or transmission (TEM) electron microscopy. TEM has the lower limits of detection by which investigators can characterize fibers with diameters in the nanometer range. Dose by some routes of administration may be further described by the mass of material, for example, in implantation or single bolus injection studies. For inhalation studies, GM and GSD length and diameter are usually listed for the exposure aerosol, and often the number of fibers within specific size ranges are listed. Following inhalation, fibers may be deposited on surfaces within the respiratory tract or exhaled. For the fibers that are deposited, the site of deposition (dose) depends upon the characteristics of the fiber and results from one of five mechanisms: impaction, interception, sedimentation, electrostatic precipitation, or diffusion. The majority of the deposition of MMVF is probably governed by the first three mechanisms. Impaction and interception occur when the fiber is removed from the airstream by physically contacting the surface of the airway or a bifurcation. Sedimentation occurs in the lower airways, where the velocity of the fiber becomes low enough for it to settle on the airway surface. Electrostatic precipitation results when the fiber carries a charge opposite to that of the airway surface; for mineral wool fibers, no reports have been found on surface charge measurements. Deposition due to diffusion requires that the air molecules collide with the fiber, resulting in movement toward the surface. This mechanism could contribute to deposition of very thin fibers, e.g., those with diameters substantially less than one-half micron, but few of them are expected in the work environment. The clearance mechanism of the deposited fibers depends upon the characteristics of the fiber and the site of deposition. Fibers deposited in the tracheobronchial region are cleared with the mucous by the cilia and swallowed. This process is completed in a matter of days, during which little change in fiber dimensions would be anticipated. Fibers deposited lower in the respiratory tract are cleared more slowly. Here the fibers are cleared by translocation to another area of the lung or dissolve; translocation may be facilitated by partial dissolution of the fiber or breakage into particles of shorter length. When fibers recovered from the lung or other tissue are characterized by dimensions, comparison with the parent material provides information on deposition and distribution. Solubility has been investigated as an indicator of durability. The interpretation of short-term bioassay results is still under study. Bernstein et al. suggested that the results of dissolution at neutral pH are correlated with in vivo biopersistence. Others report that the dissolution rates of MMVF that have high aluminum content are much greater in acidic environments. Evidence from animal studies shows that the macrophages may interact with long fibers and that multiple macrophages attach to a single fiber which can lead to dissolution. Keywords: Mineral wood; Production; Rock/slag wool; Refractory ceramic fiber; Community methods; Toxic effects; Cohort studies; Standards; Regulation; Environment; Odor; Workplace exposure
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