Exposure and Biomonitoring Division, Healthy Environments and Consumer Safety Branch, Health Canada, 50 Colombine Driveway, Ottawa, ON, Canada K1A 0K9.
Sci Total Environ. 2013 Jan 15;443:520-9. doi: 10.1016/j.scitotenv.2012.11.003. Epub 2012 Dec 5.
The Canadian House Dust Study was designed to obtain nationally representative urban house dust metal concentrations (μg g(-1)) and metal loadings (μg m(-2)) for arsenic (As), cadmium (Cd), chromium (Cr), copper (Cu), nickel (Ni), lead (Pb), and zinc (Zn). Consistent sampling of active dust of known age and provenance (area sampled) also permitted the calculation of indoor loading rates (mg m(-2) day(-1) for dust and μg m(-2) day(-1) for metals) for the winter season (from 2007 to 2010) when houses are most tightly sealed. Geomean/median indoor dust loading rates in homes located more than 2 km away from industry of any kind (9.6/9.1 mg m(-2) day(-1); n=580) were significantly lower (p<.001) than geomean (median) dust loading rates in homes located within 2 km of industry (13.5/13.4 mg m(-2) day(-1); n=421). Proximity to industry was characterized by higher indoor metal loading rates (p<.003), but no difference in dust metal concentrations (.29≥p≤.97). Comparisons of non-smokers' and smokers' homes in non-industrial zones showed higher metal loading rates (.005≥p≤.038) in smokers' homes, but no difference in dust metal concentrations (.15≥p≤.97). Relationships between house age and dust metal concentrations were significant for Pb, Cd and Zn (p<.001) but not for the other four metals (.14≥p≤.87). All seven metals, however, displayed a significant increase in metal loading rates with house age (p<.001) due to the influence of higher dust loading rates in older homes (p<.001). Relationships between three measures of metals in house dust - concentration, load, and loading rate - in the context of house age, smoking behavior and urban setting consistently show that concentration data is a useful indicator of the presence of metal sources in the home, whereas dust mass is the overriding influence on metal loadings and loading rates.
加拿大尘螨研究旨在获得全国范围内具有代表性的城市房屋灰尘中金属浓度(μg/g)和金属负荷(μg/m2),其中包括砷(As)、镉(Cd)、铬(Cr)、铜(Cu)、镍(Ni)、铅(Pb)和锌(Zn)。对具有已知年龄和来源(采样面积)的活性灰尘进行一致采样,还可以计算出冬季(2007 年至 2010 年)当房屋密封最严密时的室内负荷率(mg/m2/天用于灰尘和μg/m2/天用于金属)。距离任何类型的工业超过 2 公里的房屋(n=580)的室内灰尘负荷率中值(中位数)明显低于(p<.001)距离工业 2 公里以内的房屋(n=421)(9.6/9.1 mg/m2/天)。工业接近程度与更高的室内金属负荷率有关(p<.003),但灰尘中金属浓度没有差异(.29≥p≤.97)。在非工业区,比较不吸烟者和吸烟者的房屋,发现吸烟者家庭的金属负荷率更高(.005≥p≤.038),但灰尘中金属浓度没有差异(.15≥p≤.97)。铅、镉和锌的房屋年龄与灰尘金属浓度之间的关系具有显著性(p<.001),但其他四种金属则没有(.14≥p≤.87)。然而,由于旧房屋中灰尘负荷率较高(p<.001),所有七种金属的金属负荷率均随着房屋年龄的增长而显著增加(p<.001)。房屋灰尘中金属浓度、负荷和负荷率的三种测量值与房屋年龄、吸烟行为和城市环境之间的关系一致表明,浓度数据是家中金属源存在的有用指标,而灰尘质量是金属负荷和负荷率的主要影响因素。