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Research List

Maternal Outcomes Research

Environmental Health

Maternal iron metabolism gene variants modify umbilical cord blood lead levels by gene-environment interaction: a birth cohort study

Mateusz P Karwowski, Allan C Just , David C Bellinger, Rebecca Jim, Earl L Hatley, Adrienne S Ettinger, Howard Hu, and Robert O Wright

Background: Given the relationship between iron metabolism and lead toxicokinetics, we hypothesized that polymorphisms in iron metabolism genes might modify maternal-fetal lead transfer. The objective of this study was to determine whether maternal and/or infant transferrin (TF) and hemochromatosis (HFE) gene missense variants modify the association between maternal blood lead (MBL) and umbilical cord blood lead (UCBL).


Methods: We studied 476 mother-infant pairs whose archived blood specimens were genotyped for TF P570S, HFE H63D and HFE C282Y. MBL and UCBL were collected within 12 hours of delivery. Linear regression models were used to examine the association between log-transformed MBL and UCBL, examine for confounding and collinearity, and explore gene-environment interactions.


Results: The geometric mean MBL was 0.61 μg/dL (range 0.03, 3.2) and UCBL 0.42 (<0.02, 3.9). Gene variants were common with carrier frequencies ranging from 12-31%; all were in Hardy-Weinberg equilibrium. In an adjusted linear regression model, log MBL was associated with log UCBL (β = 0.92, 95% CI: 0.82, 1.03; p < 0.01) such that a 1% increase in MBL was associated with a 0.92% increase in UCBL among infants born to wild-type mothers. In infants born to C282Y variants, however, a 1% increase in MBL is predicted to increase UCBL 0.65% (βMain Effect = −0.002, 95% CI: −0.09, −0.09; p = 0.97; βInteraction = −0.27, 95% CI: −0.52, −0.01; p = 0.04), representing a 35% lower placental lead transfer among women with MBL 5 μg/dL.


Conclusions: Maternal HFE C282Y gene variant status is associated with greater reductions in placental transfer of lead as MBL increases. The inclusion of gene-environment interaction in risk assessment models may improve efforts to safeguard vulnerable populations.


Keywords: Hemochromatosis gene, C282Y, H63D, Lead, Pediatric, Polymorphism, Prenatal, P570S, Transferrin gene

Maternal Outcomes Research

Technical Assistance Service for Communities: Tar Creek Superfund Site, Opberable Unit 5

U.S. EPA

The Tar Creek Superfund Site was listed by the U.S. Environmental Protection Agency (EPA) on the National Priorities List (NPL) in September 1983. In 1993 after lead screening at the Indian Health Service (IHS) clinic in Ottawa County indicated that 35% of children tested had elevated blood lead levels, ATSDR conducted an exposure investigation. This investigation evaluated lead levels in soil, paint, dust, and water at nine houses identifi ed by IHS as home to children with blood lead levels of 10 μg/dL or greater.

Maternal Outcomes Research

Technical Assistance Service for Communities: Tar Creek Superfund Site, Fact Sheet

U.S. EPA

The community group Local Environmental Action Demanded (L.E.A.D.) Agency asked for assistance from EPA’s Technical Assistance Services for Communities (TASC) program. The request was for TASC review and comment on Version 1.1 of the Technical Memorandum: Development of Human Health Risk-Based Preliminary Remediation Goals for Operable Unit 5. The Technical Memorandum discusses human health risk-based preliminary remediation goals (PRGs) and ecological PRGs.
Maternal Outcomes Research

Journal of the Air & Waste Management Association

Impact of Mine Waste on Airborne Respirable Particulates in Northeastern Oklahoma, United States

Ami R. Zota , Robert Willis , Rebecca Jim , Gary A. Norris , James P. Shine , Rachelle M. Duvall , Laurel A. Schaider & John D. Spengler

This fact sheet explains the purpose of a BHHRA, how a BHHRA is performed and how the RAGS tables will be used, and presents exposure assumptions made by EPA. The TASC program prepared the fact sheet, and it is funded by TASC. Its contents do not necessarily reflect the policies, actions or positions of EPA.
Maternal Outcomes Research

ATSDR Activities at the Tar Creek Superfund Site 

ATSDR

Atmospheric dispersion of particles from mine waste is potentially an important route of human exposure to metals in communities close to active and abandoned mining areas. This study assessed sources of mass and metal concentrations in two size fractions of respirable particles using positive matrix factorization (U.S. Environmental Protection Agency [EPA] PMF 3.0). Weekly integrated samples of particulate matter (PM) 10 m in aerodynamic diameter or less (PM10) and fine PM (PM2.5, or PM 2.5 m in aerodynamic diameter) were collected at three monitoring sites, varying distances (0.5–20 km) from mine waste piles, for 58 consecutive weeks in a former lead (Pb) and zinc (Zn) mining region. Mean mass concentrations varied significantly across sites for coarse PM (PM10–PM2.5) but not PM2.5 particles. Concentrations of Pb and Zn significantly decreased with increasing distance from the mine waste piles in PM10–PM2.5 (P 0.0001) and PM2.5 (P 0.0005) fractions. Source apportionment analyses deduced five sources contributing to PM2.5 (mobile source combustion, secondary sulfates, mine waste, crustal/soil, and a source rich in calcium [Ca]) and three sources for the coarse fraction (mine waste, crustal/soil, and a Ca-rich source). In the PM2.5 fraction, mine waste contributed 1– 6% of the overall mass, 40% of Pb, and 63% of Zn. Mine waste impacts were more apparent in the PM10–PM2.5 fraction and contributed 4 –39% of total mass, 88% of Pb, and 97% of Zn. Percent contribution of mine waste varied significantly across sites (P 0.0001) for both size fractions, with highest contributions in the site closest to the mine waste piles. Seasonality, wind direction, and concentrations of the Ca-rich source were also associated with levels of ambient aerosols from the mine waste source. Scanning electron microscopy results indicated that the PMF-identified mine waste source is mainly composed of Zn-Pb agglomerates on crustal particles in the PM10–PM2.5 fraction. In conclusion, the differential impacts of mine waste on respirable particles by size fraction and location should be considered in future exposure evaluations.

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