Proposed occupational exposure limits for select ethylene glycol ethers using PBPK models and Monte Carlo simulations

被引:37
作者
Sweeney, LM
Tyler, TR
Kirman, CR
Corley, RA
Reitz, RH
Paustenbach, DJ
Holson, JF
Whorton, MD
Thompson, KM
Gargas, ML
机构
[1] Sapphire Grp Inc, Beavercreek, OH 45431 USA
[2] Union Carbide Corp, Danbury, CT USA
[3] Sapphire Grp Inc, Cleveland, OH USA
[4] Battelle Mem Inst, Richland, WA USA
[5] RHR Toxicol, Midland, MI USA
[6] Exponent, Menlo Pk, CA USA
[7] WIL Labs, Ashland, OH USA
[8] M Donald Whorton MD Inc, Alameda, CA USA
[9] Harvard Univ, Sch Publ Hlth, Boston, MA 02115 USA
关键词
occupational exposure limit; ethoxyethyl acetate; ethoxyethanol; methoxyethanol; EGEEA; EGEE; EGME; PBPK models; Monte Carlo simulation;
D O I
10.1093/toxsci/62.1.124
中图分类号
R99 [毒物学(毒理学)];
学科分类号
100405 ;
摘要
Methoxyethanol (ethylene glycol monomethyl ether, EGME), ethoxyethanol (ethylene glycol monoethyl ether, EGEE), and ethoxyethyl acetate (ethylene glycol monoethyl ether acetate, EGEEA) are all developmental toxicants in laboratory animals. Due to the imprecise nature of the exposure data in epidemiology studies of these chemicals, we relied on human and animal pharmacokinetic data, as well as animal toxicity data, to derive 3 occupational exposure limits (OELs). Physiologically based pharmacokinetic (PBPK) models for EGME, EGEE, and EGEEA in pregnant rats and humans have been developed (M. L. Gargas et al., 2000, Toxicol. Appl. Pharmacol. 165, 53-62; M. L. Gargas et at, 2000, Toxicol. Appl. Pharmacol. 165, 63-73). These models were used to calculate estimated human-equivalent no adverse effect levels (NAELs), based upon internal concentrations in rats exposed to no observed effect levels (NOELs) for developmental toxicity. Estimated NAEL values of 25 ppm for EGEEA and EGEE and 12 ppm for EGME were derived using average values for physiological, thermodynamic, and metabolic parameters in the PBPK model. The uncertainties in the point estimates for the NOELs and NAELs were estimated from the distribution of internal dose estimates obtained by varying key parameter values over expected ranges and probability distributions. Key parameters were identified through sensitivity analysis. Distributions of the values of these parameters were sampled using Monte Carlo techniques and appropriate dose metrics calculated for 1600 parameter sets. The 95th percentile values were used to calculate interindividual pharmacokinetic uncertainty factors (UFs) to account for variability among humans (UFh.pk). These values of 1.8 for EGEEA/EGEE and 1.7 for EGME are less than the default value of 3 for this area of uncertainty. The estimated human equivalent NAELs were divided by UFh.pk and the default UFs for pharmacodynamic variability among animals and among humans to calculate the proposed OELs. This methodology indicates that OELs (8-h time-weighted average) that should protect workers from the most sensitive adverse effects of these chemicals are 2 ppm EGEEA and EGEE (11 mg/m(3) EGEEA, 7 mg/m(3) EGEE) and 0.9 ppm (3 mg/m3) EGME, These recommendations assume that dermal exposure will be minimal or nonexistent.
引用
收藏
页码:124 / 139
页数:16
相关论文
共 73 条
[1]  
*ACGIH, 1999, AM C GOV IND HYG CIN
[2]  
ACGIH, 1991, AM C GOV IND HYG CIN
[3]   Investigation of the impact of pharmacokinetic variability and uncertainty on risks predicted with a pharmacokinetic model for chloroform [J].
Allen, BC ;
Covington, TR ;
Clewell, HJ .
TOXICOLOGY, 1996, 111 (1-3) :289-303
[4]   Toxicity of methoxyacetic acid in cultured human luteal cells [J].
Almekinder, JL ;
Lennard, DE ;
Walmer, DK ;
Davis, BJ .
FUNDAMENTAL AND APPLIED TOXICOLOGY, 1997, 38 (02) :191-194
[5]   TISSUE DOSIMETRY, PHARMACOKINETIC MODELING, AND INTERSPECIES SCALING FACTORS [J].
ANDERSEN, ME ;
CLEWELL, H ;
KRISHNAN, K .
RISK ANALYSIS, 1995, 15 (04) :533-537
[6]   DEVELOPMENTAL EFFECTS AFTER INHALATION EXPOSURE OF GRAVID RABBITS AND RATS TO ETHYLENE-GLYCOL MONOETHYL ETHER [J].
ANDREW, FD ;
HARDIN, BD .
ENVIRONMENTAL HEALTH PERSPECTIVES, 1984, 57 (AUG) :13-23
[7]  
[Anonymous], 6015 NCTR
[8]   Noncancer risk assessment: A probabilistic alternative to current practice [J].
Baird, SJS ;
Cohen, JT ;
Graham, JD ;
Shlyakhter, AI ;
Evans, JS .
HUMAN AND ECOLOGICAL RISK ASSESSMENT, 1996, 2 (01) :79-102
[9]   Harmonization: Developing consistent guidelines for applying mode of action and dosimetry information to cancer and noncancer risk assessment [J].
Barton, HA ;
Andersen, ME ;
Clewell, HJ .
HUMAN AND ECOLOGICAL RISK ASSESSMENT, 1998, 4 (01) :75-115
[10]  
Chia SE, 1997, AM J IND MED, V31, P148