Buckley T J, Prah J D, Ashley D, Zweidinger R A, Wallace L A
U.S. EPA, National Exposure Research Laboratory, Research Triangle Park, North Carolina, USA.
J Air Waste Manag Assoc. 1997 Jul;47(7):739-52. doi: 10.1080/10473289.1997.10463934.
Biomarkers of methyl tertiary butyl either (MTBE) exposure and the partitioning of inhaled MTBE into the body were investigated in a human chamber study. Two subjects were exposed to an environmentally relevant nominal 5,011 micrograms/m3 (1.39 ppm) MTBE for 1 hour, followed by clean-air exposure for 7 hours. Breath and blood were simultaneously sampled, while total urine was collected at prescribed times before, during, and after the exposure. Mass-balance and toxicokinetic analyses were conducted based upon the time series measurement of multiple body-burden endpoints, including MTBE in alveolar breath, and MTBE and tertiary butyl alcohol (TBA) in venous blood and urine. The decay of MTBE in the blood was assessed by fitting the post-exposure data to a 2- or 3-exponential model that yielded residence times(tau) of 2-3 min, 15-50 min, and 3-13 h as measured by alveolar breath, and 5 min, 60 min, and 32 h as evaluated from venous blood measurements. Based on observations of lower than expected blood and breath MTBE during uptake and a decreasing blood-to-breath ratio during the post-exposure decay period, we hypothesize that the respiratory mucous membranes were serving as a reservoir for the retention of MTBE. The decay data suggest that 6-9% of the MTBE intake may be retained by this non-blood reservoir. The compartmental modeling was further used to estimate important parameters that define the uptake of inhaled MTBE. The first of these parameters is f, the fraction of C(air) exhaled at equilibrium, estimated as 0.60 and 0.46 for the female and male subject, respectively. The second parameter is the blood-to-breath partition coefficient (P) estimated as approximately 18. The product of these parameters provides an estimate of the blood concentration at equilibrium as 8-11 times the air concentration. Blood TBA lagged MTBE levels and decayed more slowly (tau = 1.5-3 h), providing a more stable indication of longer term integrated exposure. The concentration ranges of MTBE and TBA in urine were similar to that of the blood, ranging from 0.37 to 15 micrograms/L and 2 to 15 micrograms/L, respectively. In urine, MTBE and TBA by themselves bore little relationship to the exposure. However, the MTBE:TBA ratio followed the pattern of exposure, with peak values occurring at the end of the exposure (20- and 60-fold greater than pre-exposure values) before decaying back to pre-exposure levels by the end of the 7-h decay period. Urinary elimination accounted for a very small fraction of total MTBE elimination (< 1%).
在一项人体舱室研究中,对甲基叔丁基醚(MTBE)暴露的生物标志物以及吸入的MTBE在体内的分配情况进行了调查。两名受试者暴露于环境相关的名义浓度为5011微克/立方米(1.39 ppm)的MTBE中1小时,随后暴露于清洁空气中7小时。同时采集呼吸气和血液样本,在暴露前、暴露期间和暴露后规定的时间收集全部尿液。基于对包括肺泡呼吸气中的MTBE、静脉血和尿液中的MTBE及叔丁醇(TBA)在内的多个体内负荷终点的时间序列测量,进行了质量平衡和毒代动力学分析。通过将暴露后的数据拟合为二指数或三指数模型来评估血液中MTBE的衰减情况,该模型得出的停留时间(τ)通过肺泡呼吸气测量为2 - 3分钟、15 - 50分钟和3 - 13小时,通过静脉血测量评估为5分钟、60分钟和32小时。基于摄取过程中血液和呼吸气中MTBE低于预期的观察结果以及暴露后衰减期血液与呼吸气比值的下降,我们推测呼吸道黏膜充当了MTBE潴留的储存库。衰减数据表明,MTBE摄入量的6 - 9%可能被这个非血液储存库保留。进一步使用房室模型来估计定义吸入MTBE摄取的重要参数。这些参数中的第一个是f,即平衡时呼出的C(空气)分数,女性和男性受试者分别估计为0.60和0.46。第二个参数是血液与呼吸气分配系数(P),估计约为18。这些参数的乘积提供了平衡时血液浓度的估计值,约为空气浓度的8 - 11倍。血液中的TBA滞后于MTBE水平且衰减更慢(τ = 1.5 - 3小时),能更稳定地指示长期综合暴露情况。尿液中MTBE和TBA的浓度范围与血液相似,分别为0.37至15微克/升和2至15微克/升。在尿液中,MTBE和TBA本身与暴露关系不大。然而,MTBE:TBA比值遵循暴露模式,在暴露结束时出现峰值(比暴露前值高20倍和60倍),然后在7小时衰减期结束时回落到暴露前水平。尿液排泄仅占MTBE总排泄量的极小部分(<1%)。