doi:10.1016/j.chemosphere.2006.05.108
Copyright © 2006 Elsevier Ltd All rights reserved.
Refinements on the age-dependent half-life model for estimating child body burdens of polychlorodibenzodioxins and dibenzofurans
Brent D. Kergera,
,
, Hon-Wing Leungb, Paul K. Scottc and Dennis J. Paustenbachd
aHealth Science Resource Integration, 2976 Wellington Circle West, Tallahassee, FL 32309, USA
bPhiladelphia, PA, USA
cChemRisk, Pittsburgh, PA, USA
dChemRisk, San Francisco, CA, USA
Accepted 26 May 2006.
Available online 5 January 2007.
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Abstract
We modified our prior age-dependent half-life model to characterize the range of child (ages 0–7) body burdens associated with dietary and environmental exposure to polychlorodibenzodioxins and furans (PCDD/Fs). Several exposure scenarios were evaluated. Infants were assumed to be either breast-fed or formula-fed from birth to 6 months of age. They then received intakes of PCDD/Fs through age 7 from foods based on weighted means estimates [JECFA, 2001. Joint FAO/WHO Committee on Food Additives. Fifty-seventh meeting, Rome, June 5–14 , 2001, pp. 24–40], and with or without exposures (ingestion and dermal) to urban residential soils at 1 ppb TCDD toxic equivalents (TEQ). A one-compartment (adipose volume) toxicokinetic model for TCDD described by Kreuzer [Kreuzer, P.F., Csanady, Gy.A., et al., 1997. 2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) and congeners in infants. A toxicokinetic model of human lifetime body burden by TCDD with special emphasis on its uptake by nutrition. Arch. Toxicol. 71, 383–400] was expanded to include the key non-TCDD congeners in human breast milk and adipose tissues, and two model parameter refinements were examined: (1) use of updated and more detailed age-correlated body fat mass data [CDC, 2000. Centers for Disease Control. CDC Growth Charts: United States. Advance Data from Vital and Health Statistics of the Centers for Disease Control and Prevention, National Center for Health Statistics, Number 314, December 2000]; (2) use of breast milk PCDD/F concentration data from sampling completed in 2000–2003 [Wittsiepe, J., Fürst, P., et al., 2004. PCDD/F and dioxin-like PCB in human blood and milk from German mothers. Organohalogen Compd. 66, 2865–2872]. The updated body fat mass data nearly halved the predicted peak body burden for breast-feeding and lowered the time-weighted average (TWA) body burdens from ages 0–7 by 30–40% for breast-fed and formula-fed infants. Combined use of the updated breast milk PCDD/F concentration and body fat mass data increased the contribution of breast-feeding but reduced TWA body burdens from diet and soil. We conclude that further refinements are needed, but reliance on these better data sets for body fat mass and breast milk PCDD/F concentration significantly improves the model’s ability to accurately predict body burdens during early childhood.
Keywords: Dioxins; Furans; Childhood; Diet; Soil; Toxicokinetic model
Fig. 1A. Predicted child body burdens at 50th percentile dietary and environmental intakes using dataset A. Modeling was conducted with the same intake rates and dioxin concentration in breast milk (0.55 pg TCDD/g milk fat) and in formula (0.075 pg TCDD/g milk fat) as those used by Kreuzer et al. (1997). The breast milk data reported by Fürst et al. (1994) were used to calculate the concentrations of other PCDD/F congeners. Body weights and body fat mass data were derived from USEPA, 2002a and ICRP, 1975, respectively. Time-weighted average (TWA) body burden estimates from birth to 7 years of age are presented beside each category.
Fig. 1B. Predicted child body burdens at 50th percentile dietary and environmental intakes using dataset B. Modeling was conducted with more detailed body weight and body fat mass data (CDC, 2000) and with more recent breast milk PCDD/F concentration data (e.g., 1.57 pg TCDD/g milk fat) reported by Wittsiepe et al. (2004). Time-weighted average (TWA) body burden estimates from birth to 7 years of age are presented beside each category.
Fig. 2A. Predicted child body burdens at 95th percentile dietary and environmental intakes using dataset A. Modeling was conducted with the same intake rates and dioxin concentration in breast milk (0.55 pg TCDD/g milk fat) and in formula (0.075 pg TCDD/g milk fat) as those used by Kreuzer et al. (1997). The breast milk data reported by Fürst et al. (1994) were used to calculate the concentrations of other PCDD/F congeners. Body weights and body fat mass were derived from USEPA, 2002a and ICRP, 1975, respectively. Time-weighted average (TWA) body burden estimates from birth to 7 years of age are presented beside each category.
Fig. 2B. Predicted child body burdens at 95th percentile dietary and environmental intakes using dataset B. Modeling was conducted with more detailed body weight and body fat mass data (CDC, 2000) and with more recent breast milk PCDD/F concentration data (e.g., 1.57 pg TCDD/g milk fat) reported by Wittsiepe et al. (2004). Time-weighted average (TWA) body burden estimates from birth to 7 years of age are presented beside each category.
Table 1.
Age-dependent half-life model parameters
a Data from ICRP used for model A.
b Data from CDC used for model B.
c TEQ% from
Fürst et al. (1994) collected from 526 breast milk samples during 1986–1991.
d TEQ% from
Wittsiepe et al. (2004) collected from 169 breast milk samples during 2000–2003.
Table 2.
Model Inputs for absorbed daily TEQ dose (pg/kg-day)
