Lippmann M, Yeates D B, Albert R E
Br J Ind Med. 1980 Nov;37(4):337-62. doi: 10.1136/oem.37.4.337.
The relation between the concentrations and characteristics of air contaminants in the work place and the resultant toxic doses and potential hazards after their inhalation depends greatly on their patterns of deposition and the rates and pathways for their clearance from the deposition sites. The distribution of the deposition sites of inhaled particles is strongly dependent on their aerodynamic diameters. For normal man, inhaled non-hygroscopic particles greater than or equal to 2 micrometers that deposit in the conducting airways by impaction are concentrated on to a small fraction of the surface. Cigarette smoking and bronchitis produce a proximal shift in the deposition pattern. The major factor affecting the deposition of smaller particles is their transfer from tidal to reserve air. For particles soluble in respiratory tract fluid, systemic uptake may be relatively complete for all deposition patterns, and there may be local toxic or irritant effects or both. On the other hand, slowly soluble particles depositing in the conducting airways are carried on the surface to the glottis and are swallowed within one day. Mucociliary transport rates are highly variable, both along the ciliated airways of a given individual and between individuals. The changes in clearance rates produced by drugs, cigarette smoke, and other environmental pollutants can greatly increase or decrease these rates. Particles deposited in non-ciliated airways have large surface-to-volume ratios, and clearance by dissolution can occur for materials generally considered insoluble. They may also be cleared as free particles either by passive transport along surface liquids or, after phagocytosis, by transport within alveolar macrophages. If the particles penetrate the epithelium, either bare or within macrophages, they may be sequestered within cells or enter the lymphatic circulation and be carried to pleural, hilar, and more distant lymph nodes. Non-toxic insoluble particles are cleared from the alveolar region in a series of temporal phases. The earliest, lasting several weeks, appears to include the clearance of phagocytosed particles via the bronchial tree. The terminal phases appear to be related to solubility at interstitial sites. While the mechanisms and dynamics of particle deposition and clearance are reasonably well established in broad outline, reliable quantitative data are lacking in many specific areas. More information is needed on: (1) normal behaviour, (2) the extent of the reserve capacity of the system to cope with occupational exposures, and (3) the role of compensatory changes in airway sizes and in secretory and transport rates in providing protection against occupational exposures, and in relation to the development and progression of dysfunction and disease.
工作场所空气中污染物的浓度与特性,以及吸入后产生的毒性剂量和潜在危害之间的关系,在很大程度上取决于它们的沉积模式以及从沉积部位清除的速率和途径。吸入颗粒沉积部位的分布强烈依赖于它们的空气动力学直径。对于正常人来说,吸入的大于或等于2微米的非吸湿性颗粒通过撞击沉积在传导气道中,集中在一小部分表面上。吸烟和支气管炎会使沉积模式向近端转移。影响较小颗粒沉积的主要因素是它们从潮气量空气转移到储备空气。对于可溶于呼吸道液体的颗粒,对于所有沉积模式,全身吸收可能相对完全,并且可能存在局部毒性或刺激作用或两者兼有。另一方面,沉积在传导气道中的缓慢可溶性颗粒会随着表面被带到声门并在一天内被吞咽。黏液纤毛运输速率变化很大,在给定个体的纤毛气道内以及个体之间都是如此。药物、香烟烟雾和其他环境污染物引起的清除率变化可大大增加或降低这些速率。沉积在无纤毛气道中的颗粒具有大的表面积与体积比,对于通常被认为不溶性的物质,可通过溶解进行清除。它们也可能作为游离颗粒通过沿表面液体的被动运输或在吞噬作用后通过肺泡巨噬细胞内的运输而被清除。如果颗粒穿透上皮,无论是裸露的还是在巨噬细胞内,它们可能会被隔离在细胞内或进入淋巴循环并被带到胸膜、肺门和更远的淋巴结。无毒不溶性颗粒在一系列时间阶段从肺泡区域清除。最早的阶段持续数周,似乎包括通过支气管树清除吞噬的颗粒。最终阶段似乎与间质部位的溶解度有关。虽然颗粒沉积和清除的机制和动力学在大致轮廓上已相当明确,但在许多特定领域缺乏可靠的定量数据。需要更多关于以下方面的信息:(1)正常行为,(2)系统应对职业暴露的储备能力程度,以及(3)气道大小以及分泌和运输速率的代偿性变化在提供针对职业暴露的保护方面的作用,以及与功能障碍和疾病的发生和发展的关系。