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Mercury Inhalation Risks in Indoor Air from Use of Coal Combustion Products(CCPs)in Building Materials

机译:室内空气中的汞吸入风险从煤炭燃烧产品(CCP)在建筑材料中

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Coal combustion products(CCPs),including coal fly ash(CFA)and flue gasdesulfurization(FGD)products,are increasingly being used as substitutes for traditionalsubstances in building materials.For example,approximately 30%of US wallboard isnow manufactured from FGD gypsum,while CFA has gained widespread use as apartial replacement for Portland cement in concrete.Given concerns that have beenraised regarding the presence of mercury(Hg)in CCPs,and the potential for Hgreleases from CCP materials into indoor air,we conducted a risk assessment toestimate inhalation risks from indoor air exposures to Hg for two CCP utilizationscenarios:(1)CFA concrete blocks used in a school classroom,and(2)FGD gypsumwallboard used in a school classroom or home.For CFA concrete,we relied on datafrom recent laboratory studies of Hg emissions during dry curing of concrete at near-ambient temperatures to calculate two Hg release rates to indoor air,one based on themaximum 28-day curing rate from these studies to represent a high-end estimate ofpotential emissions and one based on extrapolated longer-term curing emissions torepresent an upper-bound estimate of more typical,long-term emissions.Forwallboard,we calculated a Hg release rate based on laboratory flux chambermeasurements for gypsum wallboard samples.We estimated indoor air Hgconcentrations using these Hg release rates and conservative values for otherparameters(e.g.,air exchange rates,material loading ratios)in a steady-state indoor airmodel.Even using parameters intended to overstate potential exposures,we predictedindoor air Hg concentrations that are generally consistent with or below ambientbackground Hg levels.Moreover,predicted indoor Hg concentrations were well belowestablished inhalation toxicity criteria(hazard indices ranged from 0.00003 to 0.015).Thus,based on our findings,we conclude that CCPs in concrete and wallboard buildingmaterials are unlikely to result in Hg exposures in either classroom settings or inresidential homes that pose a health concern.Key results are displayed graphicallybelow.
机译:煤燃烧产物(CCP),包括煤粉煤灰(CFA)和烟熏氟磺酰化(FGD)产品,越来越多地被用作建筑材料中的传统替代品。例如,大约30%的美国墙板由FGD石膏制造,而CFA在混凝土中获得了广泛用途作为波特兰水泥的公寓替代。在CCP中存在汞(Hg)的存在,以及从CCP材料进入室内空气的招聘次数的可能性,我们进行了风险评估,对吸入风险进行了风险评估从室内空气暴露到HG的两个CCP利用过程:(1)学校课堂中使用的CFA混凝土块,(2)用于学校教室或家中的FGD Gypsumwallboard。对于CFA混凝土,我们依赖于HG的DataFrom近期实验室研究在近乎环境温度下混凝土干燥固化过程中的排放,以计算室内空气的两个HG释放速率,一个基于从这些研究到r的临时8天固化速率EPRESENT高端估计的对势排放的高端估计和基于外推长期固化排放的估计是更典型的长期排放的上束性估计.Forwallboard,我们计算了基于石膏墙板样品的实验室助焊剂的HG释放速率.WE使用这些HG释放速率和保守值的室内空气HGConcentations在稳态室内Airmodel中使用这些HG释放速率和保守值,以及使用旨在夸大潜在暴露的参数,我们预测潜在曝光的参数通常是一致的或低于Famientbackground Hg水平。oreover,预测的室内Hg浓度远远低于平吸入毒性标准(危险索引从0.00003到0.015),基于我们的研究结果,我们得出结论,混凝土和墙板建筑材料中的CCP不太可能导致课堂设置或inriedential hom中的Hg曝光构成健康问题的es.key结果是图形的。

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