Colt Joanne S, Gunier Robert B, Metayer Catherine, Nishioka Marcia G, Bell Erin M, Reynolds Peggy, Buffler Patricia A, Ward Mary H
Division of Cancer Epidemiology and Genetics, National Cancer Institute, National Institutes of Health, Department of Health and Human Services, 6120 Executive Blvd. MSC 7240, Bethesda, MD, 20892-7240, USA.
Environ Health. 2008 Feb 21;7:6. doi: 10.1186/1476-069X-7-6.
Levels of pesticides and other compounds in carpet dust can be useful indicators of exposure in epidemiologic studies, particularly for young children who are in frequent contact with carpets. The high-volume surface sampler (HVS3) is often used to collect dust samples in the room in which the child had spent the most time. This method can be expensive and cumbersome, and it has been suggested that an easier method would be to remove dust that had already been collected with the household vacuum cleaner. However, the household vacuum integrates exposures over multiple rooms, some of which are not relevant to the child's exposure, and differences in vacuuming equipment and practices could affect the chemical concentration data. Here, we compare levels of pesticides and other compounds in dust from household vacuums to that collected using the HVS3.
Both methods were used in 45 homes in California. HVS3 samples were collected in one room, while the household vacuum had typically been used throughout the home. The samples were analyzed for 64 organic compounds, including pesticides, polycyclic aromatic hydrocarbons, and polychlorinated biphenyls (PCBs), using GC/MS in multiple ion monitoring mode; and for nine metals using conventional microwave-assisted acid digestion combined with ICP/MS.
The methods agreed in detecting the presence of the compounds 77% to 100% of the time (median 95%). For compounds with less than 100% agreement, neither method was consistently more sensitive than the other. Median concentrations were similar for most analytes, and Spearman correlation coefficients were 0.60 or higher except for allethrin (0.15) and malathion (0.24), which were detected infrequently, and benzo(k)fluoranthene (0.55), benzo(a)pyrene (0.55), PCB 105 (0.54), PCB 118 (0.54), and PCB 138 (0.58). Assuming that the HVS3 method is the "gold standard," the extent to which the household vacuum cleaner method yields relative risk estimates closer to unity by increasing random measurement error varies by compound and depends on the method used to calculate relative risk.
The household vacuum cleaner method appears to be a reasonable alternative to the HVS3 for detecting, ranking, and quantifying the concentrations of pesticides and other compounds in carpet dust.
地毯灰尘中农药及其他化合物的含量可作为流行病学研究中暴露情况的有用指标,对于经常接触地毯的幼儿而言尤为如此。大容量表面采样器(HVS3)常用于采集儿童待的时间最长的房间内的灰尘样本。这种方法可能成本高昂且操作繁琐,有人提出一种更简便的方法是收集家用吸尘器已采集的灰尘。然而,家用吸尘器采集的灰尘综合了多个房间的暴露情况,其中一些与儿童的暴露无关,而且吸尘设备和操作方式的差异可能会影响化学物质浓度数据。在此,我们比较了家用吸尘器采集的灰尘与使用HVS3采集的灰尘中农药及其他化合物的含量。
在加利福尼亚州的45户家庭中使用了这两种方法。在一个房间内采集HVS3样本,而家用吸尘器通常在整个家中使用。使用气相色谱/质谱联用仪在多离子监测模式下对样本中的64种有机化合物进行分析,包括农药、多环芳烃和多氯联苯(PCBs);使用常规微波辅助酸消解结合电感耦合等离子体质谱法对9种金属进行分析。
两种方法在检测化合物存在情况时的一致性为77%至100%(中位数为95%)。对于一致性低于100%的化合物,两种方法都并非始终比另一种方法更灵敏。大多数分析物的中位数浓度相似,除了很少检测到的丙烯菊酯(0.15)和马拉硫磷(0.24),以及苯并(k)荧蒽(0.55)、苯并(a)芘(0.55)、多氯联苯105(0.54)、多氯联苯118(0.54)和多氯联苯138(0.58)外,斯皮尔曼相关系数为0.60或更高。假设HVS3方法是“金标准”,家用吸尘器方法通过增加随机测量误差使相对风险估计值更接近1的程度因化合物而异,并且取决于用于计算相对风险的方法。
对于检测、排序和量化地毯灰尘中农药及其他化合物的浓度,家用吸尘器方法似乎是HVS3的合理替代方法。