含铅涂料清除工作和清除等待期后的颗粒沉降。

K. Choe, M. Trunov, S. Grinshpun, K. Willeke, J. Harney, S. Trakumas, G. Mainelis, R. Bornschein, S. Clark, W. Friedman
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引用次数: 21

摘要

本研究利用直接实时颗粒监测,在受控环境中研究了减排工作后空气中颗粒浓度和大小分布的演变,并利用它来预测这些颗粒沉降时潜在的铅负荷。建立了一个860平方英尺的环境试验室,配备了先进的通风和空气净化系统。使用含铅涂料的木门被干燥打磨或刮擦,以产生最高的空气铅浓度。在所有试验中,即使没有空气交换,粒径分数空气颗粒浓度也随时间呈指数下降,这与不断混合空气的搅拌模型相一致,该模型预测沉降时间比平静沉降时间更长。由温度梯度和初始室内空气湍流产生的非常低水平的空气混合影响颗粒沉降。大约90%的空气中的铅在主动减排后的1小时内沉淀下来,然后才开始最后的清洁。在清扫地板后的第二次1小时的等待期间,额外的灰尘沉淀下来,因此空气中剩余铅的额外潜在铅负荷低于20微克/平方英尺。在这种最坏的情况下,间隙取样对铅负荷的低估不超过30%。在更现实的情况下,预计低估的水平远低于新的40微克/平方英尺的住房和城市发展(HUD)地板尘铅清除标准。根据HUD指南的建议,这些结果是在第一个等待期(在主动缓解结束和清洁开始之间)1小时获得的。因此,这项研究表明没有必要增加第一或第二次等待期。
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Particle settling after lead-based paint abatement work and clearance waiting period.
This study investigated the evolution of airborne particle concentration and size distribution following abatement work in a controlled environment utilizing direct real-time particle monitoring and used it to project potential lead loadings as those particles settle. An 860 ft3 environmental test chamber with sophisticated ventilation and air purifying systems was built. Wooden doors with lead-based paint were dry sanded or scraped to generate the highest feasible airborne lead concentrations. Size-fractional airborne particle concentrations decreased exponentially with time in all tests, even with no air exchange, consistent with the stirred model of constantly mixed air, which predicts longer settling than for tranquil settling. Very low levels of air mixing generated by temperature gradients and initial room air turbulence affected particle settling. About 90% of airborne lead mass settled within 1 hour after active abatement, before final cleaning began. During the second waiting period of 1 hour, which followed cleaning of the floor, additional dust settled so that the additional potential lead loading from remaining airborne lead was less than 20 microg/ft2. For this worst case scenario, the underestimate of the lead loading done by the clearance sampling did not exceed about 30%. For more realistic conditions, the underestimates are projected to be much lower than the new 40 microg/ft2 Housing and Urban Development (HUD) clearance standards for floor dust lead. These results were obtained for the first waiting period (between the end of active abatement and the beginning of cleaning) of 1 hour, as recommended by HUD guidelines. Thus, this study demonstrates no need to increase either the first or second waiting period.
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