全部 标题 作者
关键词 摘要

OALib Journal期刊
ISSN: 2333-9721
费用:99美元

查看量下载量

相关文章

更多...

Modeling the Human Kinetic Adjustment Factor for Inhaled Volatile Organic Chemicals: Whole Population Approach versus Distinct Subpopulation Approach

DOI: 10.1155/2012/404329

Full-Text   Cite this paper   Add to My Lib

Abstract:

The objective of this study was to evaluate the impact of whole- and sub-population-related variabilities on the determination of the human kinetic adjustment factor (HKAF) used in risk assessment of inhaled volatile organic chemicals (VOCs). Monte Carlo simulations were applied to a steady-state algorithm to generate population distributions for blood concentrations (CAss) and rates of metabolism (RAMs) for inhalation exposures to benzene (BZ) and 1,4-dioxane (1,4-D). The simulated population consisted of various proportions of adults, elderly, children, neonates and pregnant women as per the Canadian demography. Subgroup-specific input parameters were obtained from the literature and P3M software. Under the “whole population” approach, the HKAF was computed as the ratio of the entire population’s upper percentile value (99th, 95th) of dose metrics to the median value in either the entire population or the adult population. Under the “distinct subpopulation” approach, the upper percentile values in each subpopulation were considered, and the greatest resulting HKAF was retained. CAss-based HKAFs that considered the Canadian demography varied between 1.2 (BZ) and 2.8 (1,4-D). The “distinct subpopulation” CAss-based HKAF varied between 1.6 (BZ) and 8.5 (1,4-D). RAM-based HKAFs always remained below 1.6. Overall, this study evaluated for the first time the impact of underlying assumptions with respect to the interindividual variability considered (whole population or each subpopulation taken separately) when determining the HKAF. 1. Introduction An interindividual variability (or uncertainty) factor (IVF) of a default value of 10 is usually applied to the point of departure (POD) for deriving reference doses (RfDs) or reference concentrations (RfCs) for use in noncancer risk assessment [1–3]. As reviewed by Price et al. [4], the IVF has historically been defined as a factor required to protect the sensitive members of the population since the POD is generally determined for average healthy individuals. Actually, two models have been proposed to describe the IVF. Under the “sensitive population” model, the IVF is applied to correct for the possible failure of a critical study to include a sufficient number of members pertaining to distinct subpopulation exhibiting an increased sensitivity. Conversely, under the “finite sample size” model, the application of the IVF relates to the possibility that the retained POD may fail to identify the toxicity threshold in the overall population simply because of the finite size of the sample in which it was determined

References

[1]  M. L. Dourson, S. P. Felter, and D. Robinson, “Evolution of science-based uncertainty factors in noncancer risk assessment,” Regulatory Toxicology and Pharmacology, vol. 24, no. 2, pp. 108–120, 1996.
[2]  M. L. Dourson and J. F. Stara, “Regulatory history and experimental support of uncertainty (safety) factors,” Regulatory Toxicology and Pharmacology, vol. 3, no. 3, pp. 224–238, 1983.
[3]  U.S.EPA., A review of the reference dose and reference concentration process. Risk Assessment Forum. EPA/630/P-02/00F. Washington, DC, USA, 2002.
[4]  P. S. Price, R. E. Keenan, and B. Schwab, “Defining the interindividual (intraspecies) uncertainty factor,” Human and Ecological Risk Assessment, vol. 5, no. 5, pp. 1023–1033, 1999.
[5]  J. L. C. M. Dorne and A. G. Renwick, “The refinement of uncertainty/safety factors in risk assessment by the incorporation of data on toxicokinetic variability in humans,” Toxicological Sciences, vol. 86, no. 1, pp. 20–26, 2005.
[6]  IPCS, Assessing Human Health Risks of Chemicals: Derivation of Guidance Values for Health Based Exposure Limits, World Health Organization, International Panel on Chemical Safety. Environmental Health Criteria, Geneva, Switzerland, 1994.
[7]  A. G. Renwick and N. R. Lazarus, “Human variability and noncancer risk assessment—an analysis of the default uncertainty factor,” Regulatory Toxicology and Pharmacology, vol. 27, no. 1 I, pp. 3–20, 1998.
[8]  IPCS, Chemical-Specific Adjustment Factors (CSAFs) for Interspecies Differences and Human Variability: Guidance Document for the Use of Data in Dose/Concentration-Response Assessment, WHO, Geneva, Switzerland, 2005.
[9]  M. E. Meek, A. Renwick, E. Ohanian et al., “Guidelines for application of chemical-specific adjustment factors in dose/concentration-response assessment,” Toxicology, vol. 181-182, pp. 115–120, 2002.
[10]  U.S.EPA., Integrated Risk Information System. U.S. Environmental Protection Agency, Washington, DC, USA, 2010.
[11]  G. Ginsberg, D. Hattis, B. Sonawane et al., “Evaluation of child/adult pharmacokinetic differences from a database derived from the therapeutic drug literature,” Toxicological Sciences, vol. 66, no. 2, pp. 185–200, 2002.
[12]  J. L. C. M. Dorne, K. Walton, and A. G. Renwick, “Human variability in xenobiotic metabolism and pathway-related uncertainty factors for chemical risk assessment: a review,” Food and Chemical Toxicology, vol. 43, no. 2, pp. 203–216, 2005.
[13]  J. L. C. M. Dorne, “Human variability in hepatic and renal elimination: implications for risk assessment,” Journal of Applied Toxicology, vol. 27, no. 5, pp. 411–420, 2007.
[14]  A. Nong, D. G. McCarver, R. N. Hines, and K. Krishnan, “Modeling interchild differences in pharmacokinetics on the basis of subject-specific data on physiology and hepatic CYP2E1 levels: a case study with toluene,” Toxicology and Applied Pharmacology, vol. 214, no. 1, pp. 78–87, 2006.
[15]  M. Valcke and K. Krishnan, “Evaluation of the impact of the exposure route on the human kinetic adjustment factor,” Regulatory Toxicology and Pharmacology, vol. 59, no. 2, pp. 258–269, 2011.
[16]  M. Valcke and K. Krishnan, “An assessment of the impact of physico-chemical and biochemical characteristics on the human kinetic adjustment factor for systemic toxicants,” Toxicology, vol. 286, no. 1–3, pp. 36–47, 2011.
[17]  A. K. M?rk and G. Johanson, “Chemical-specific adjustment factors for intraspecies variability of acetone toxicokinetics using a probabilistic approach,” Toxicological Sciences, vol. 116, no. 1, pp. 336–348, 2010.
[18]  M. J. J. Ronis, K. O. Lindros, and M. Ingelman-Sundberg, “The CYP2E family,” in Cytochrome P450 Metabolic and Toxicological Aspects, C. Ioannides, Ed., pp. 211–240, CRC Press, Boca Raton, Fla, USA, 1996.
[19]  E. K. Johnsrud, S. B. Koukouritaki, K. Divakaran, L. L. Brunengraber, R. N. Hines, and D. G. McCarver, “Human hepatic CYP2E1 expression during development,” Journal of Pharmacology and Experimental Therapeutics, vol. 307, no. 1, pp. 402–407, 2003.
[20]  J. C. Lipscomb, L. K. Teuschler, J. C. Swartout, C. A. F. Striley, and J. E. Snawder, “Variance of microsomal protein and cytochrome P450 2E1 and 3A forms in adult human liver,” Toxicology Mechanisms and Methods, vol. 13, no. 1, pp. 45–51, 2003.
[21]  A. Nannelli, A. De Rubertis, V. Longo, and P. G. Gervasi, “Effects of dioxane on cytochrome P450 enzymes in liver, kidney, lung and nasal mucosa of rat,” Archives of Toxicology, vol. 79, no. 2, pp. 74–82, 2005.
[22]  S. Haddad, M. Béliveau, R. Tardif, and K. Krishnan, “A PBPK modeling-based approach to account for interactions in the health risk assessment of chemical mixtures,” Toxicological Sciences, vol. 63, no. 1, pp. 125–131, 2001.
[23]  R. H. Reitz, P. S. McCroskey, C. N. Park, M. E. Andersen, and M. I. Gargas, “Development of a physiologically based pharmacokinetic model for risk assessment with 1,4-dioxane,” Toxicology and Applied Pharmacology, vol. 105, no. 1, pp. 37–54, 1990.
[24]  M. E. Andersen, “Pharmacokinetics of inhaled gases and vapors,” Neurobehavioral Toxicology and Teratology, vol. 3, no. 4, pp. 383–389, 1981.
[25]  W. A. Chiu and P. White, “Steady-state solutions to PBPK models and their applications to risk assessment I: route-to-route extrapolation of volatile chemicals,” Risk Analysis, vol. 26, no. 3, pp. 769–780, 2006.
[26]  G. A. Csanády and J. G. Filser, “The relevance of physical activity for the kinetics of inhaled gaseous substances,” Archives of Toxicology, vol. 74, no. 11, pp. 663–672, 2001.
[27]  M. Pelekis, D. Krewski, and K. Krishnan, “Physiologically based algebraic expressions for predicting steady-state toxicokinetics of inhaled vapors,” Toxicology Methods, vol. 7, no. 3, pp. 205–225, 1997.
[28]  P. S. Price, R. B. Conolly, C. F. Chaisson et al., “Modeling interindividual variation in physiological factors used in PBPK models of humans,” Critical Reviews in Toxicology, vol. 33, no. 5, pp. 469–503, 2003.
[29]  ICRP, “Basic anatomical and physiological data for use in radiological protection: reference values. A report of age- and gender-related differences in the anatomical and physiological characteristics of reference individuals. ICRP Publication 89,” Annals of the ICRP, vol. 32, no. 3-4, pp. 5–265, 2002.
[30]  Statistiques Canada, Estimations de la population selon le sexe et le groupe d'age au 1er juillet 2010, Canadahttp://www.statcan.gc.ca/daily-quotidien/100929/t100929b4-fra.htm.
[31]  S. J. Ventura, J. C. Abma, W. D. Mosher, and S. K. Henshaw, “Estimated pregnancy rates by outcome for the United States, 1990–2004,” National Vital Statistics Reports, vol. 56, no. 15, pp. 1–28, 2008.
[32]  M. Jamei, G. L. Dickinson, and A. Rostami-Hodjegan, “A framework for assessing inter-individual variability in pharmacokinetics using virtual human populations and integrating general knowledge of physical chemistry, biology, anatomy, physiology and genetics: a tale of 'bottom-up' vs 'top-down' recognition of covariates,” Drug Metabolism and Pharmacokinetics, vol. 24, no. 1, pp. 53–75, 2009.
[33]  S. F. Hudachek and D. L. Gustafson, “Customized in silico population mimics actual population in docetaxel population pharmacokinetic analysis,” Journal of Pharmaceutical Sciences, vol. 100, no. 3, pp. 1156–1166, 2011.
[34]  P. Brochu, J. F. Ducré-Robitaille, and J. Brodeur, “Physiological daily inhalation rates for free-living pregnant and lactating adolescents and women aged 11 to 55 years, using data from doubly labeled water measurements for use in health risk assessment,” Human and Ecological Risk Assessment, vol. 12, no. 4, pp. 702–735, 2006.
[35]  P. Brochu, J. Brodeur, and K. Krishnan, “Derivation of physiological inhalation rates in children, adults, and elderly based on nighttime and daytime respiratory parameters,” Inhalation Toxicology, vol. 23, no. 2, pp. 74–94, 2011.
[36]  E. M. Faustman and P. Ribeiro, “Pharmacokinetic consideration in developmental toxicity,” in Developmental Toxicology: Risk Assessment and the Future, R. D. Hood, Ed., pp. 109–136, D. Van Nostrand Reinhold Company, New York, NY, USA, 1990.
[37]  K. Price, S. Haddad, and K. Krishnan, “Physiological modeling of age-specific changes in the pharmacokinetics of organic chemicals in children,” Journal of Toxicology and Environmental Health—Part A, vol. 66, no. 5, pp. 417–433, 2003.
[38]  R. Sarangapani, P. Robinan Gentry, T. R. Covington, J. G. Teeguarden, and H. J. Clewell, “Evaluation of the potential impact of age- and gender-specific lung morphology and ventilation rate on the dosimetry of vapors,” Inhalation Toxicology, vol. 15, no. 10, pp. 987–1016, 2003.
[39]  WHO, Principles for Evaluating Health Risks in Children Associated with Exposure to Chemicals, Environmental Health Criteria 237, World Health Organization, Geneva, Switzerland, 2006.
[40]  M. Pelekis, L. A. Gephart, and S. E. Lerman, “Physiological-model-based derivation of the adult and child pharmacokinetic intraspecies uncertainty factors for volatile organic compounds,” Regulatory Toxicology and Pharmacology, vol. 33, no. 1, pp. 12–20, 2001.
[41]  M. Pelekis, M. J. Nicolich, and J. S. Gauthier, “Probabilistic framework for the estimation of the adult and child toxicokinetic intraspecies uncertainty factors,” Risk Analysis, vol. 23, no. 6, pp. 1239–1255, 2003.
[42]  L. T. Haber, A. Maier, P. R. Gentry, H. J. Clewell, and M. L. Dourson, “Genetic polymorphisms in assessing interindividual variability in delivered dose,” Regulatory Toxicology and Pharmacology, vol. 35, no. 2 I, pp. 177–197, 2002.
[43]  H. J. Clewell, P. R. Gentry, T. R. Covington, R. Sarangapani, and J. G. Teeguarden, “Evaluation of the potential impact of age- and gender-specific pharmacokinetic differences on tissue dosimetry,” Toxicological Sciences, vol. 79, no. 2, pp. 381–393, 2004.
[44]  P. Neafsey, G. Ginsberg, D. Hattis, D. O. Johns, K. Z. Guyton, and B. Sonawane, “Genetic polymorphism in CYP2E1: population distribution of CYP2E1 activity,” Journal of Toxicology and Environmental Health—Part B, vol. 12, no. 5-6, pp. 362–388, 2009.

Full-Text

comments powered by Disqus

Contact Us

service@oalib.com

QQ:3279437679

WhatsApp +8615387084133

WeChat 1538708413