Byrne S L, Shurdut B A, Saunders D G
Environmental Chemistry Laboratories-Indianapolis Laboratory, Dow AgroSciences, Indianapolis, IN 46268-1054 USA.
Environ Health Perspect. 1998 Nov;106(11):725-31. doi: 10.1289/ehp.98106725.
Multipathway exposures were evaluated for residents of houses over a 10-day period following a crack and crevice application of a chlorpyrifos-based formulation. Three multiroom houses with two adults each were treated. Air concentration, total deposition, and dislodgeable residues on horizontal surfaces were measured to assess potential respiratory, oral, and dermal exposures, respectively, in treated and untreated high activity rooms. In addition, urine samples collected from the adults were analyzed for the primary metabolite of chlorpyrifos, 3,5,6-trichloropyridinol, to determine absorbed dose. The maximum chlorpyrifos air concentration observed was 2.3 microgram/m3, with air concentrations generally decreasing to levels ranging from 0.1 to 0.3 microgram/m3 within 10 days. Carpet dislodgeable residues, used to evaluate the amount of residues potentially transferred upon contact, were less than the analytical method limit of quantitation (1.6 microgram/m2). Hard plastic balls placed in the homes on the day before application contained no detectable dislodgeable residues (<6.5 microgram/m2). Ten-day cumulative nontarget residues deposited on surfaces, as determined by deposition pads, were less than 2.3 microgram/100 cm2. Deposition samples from all living area floors collected 2 hr after application contained less than 9.9 microgram/100 cm2. Therefore, contact with household surfaces and subsequent hand-to-mouth activity are not expected to significantly contribute to overall exposure. Estimated exposures to children, based on the passive dosimetry measurements, ranged from 0.26 to 2.1% of the no observed effect level for plasma cholinesterase depression. In addition, potential exposures to the adult residents, as indicated by the urinary 3,5,6-TCP biomonitoring, did not increase as a result of the application.
在使用基于毒死蜱的制剂进行缝隙处理后的10天内,对房屋居民的多途径暴露情况进行了评估。处理了三栋多房间房屋,每栋房屋有两名成年人。测量了空气浓度、总沉积量以及水平表面上的可去除残留量,以分别评估处理过和未处理过的高活动房间内潜在的呼吸道、口腔和皮肤暴露。此外,对从成年人采集的尿液样本进行分析,检测毒死蜱的主要代谢产物3,5,6 - 三氯吡啶醇,以确定吸收剂量。观察到的毒死蜱最大空气浓度为2.3微克/立方米,空气浓度通常在10天内降至0.1至0.3微克/立方米的范围。用于评估接触时潜在转移残留量的地毯可去除残留量低于分析方法的定量限(1.6微克/平方米)。在施药前一天放置在房屋内的硬塑料球未检测到可去除残留量(<6.5微克/平方米)。通过沉积垫测定,表面上10天累积的非目标残留量低于2.3微克/100平方厘米。施药后2小时从所有居住区域地板采集的沉积样本中,残留量低于9.9微克/100平方厘米。因此,预计与家庭表面接触以及随后的手口活动对总体暴露的贡献不大。根据被动剂量测定法测量,估计儿童的暴露量为血浆胆碱酯酶抑制未观察到效应水平的0.26%至2.1%。此外,尿中3,5,6 - TCP生物监测表明,成年居民的潜在暴露量并未因施药而增加。