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Air Quality Criteria for Lead Volume II of II - (NEPIS)(EPA) - US ...

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AX4-10<br />

Table AX4-4 (cont’d). Bone <strong>Lead</strong> Measurements in Environmentally-Exposed Subjects<br />

Reference, Study<br />

Location, and Period Study Description<br />

United States (cont’d)<br />

Rosen et al.<br />

(1989)<br />

Bronx, NY<br />

Unknown<br />

Kosnett et al. (1994)<br />

Dickson City, PA<br />

1991<br />

Rosen et al. (1993)<br />

Moosic and Throop, PA<br />

1989-91<br />

Stokes et al. (1998)<br />

Bunker Hill, ID; Spokane,<br />

WA<br />

1994<br />

Comparison <strong>of</strong> L-shell XRF measures<br />

and EDTA provocation test in lead-toxic<br />

children 1-6 yr old. Eligible if PbB 25-<br />

55 µg/dL and erythrocyte protoporphyrin<br />

>35 µg/dL.<br />

Aim to determine the influence <strong>of</strong><br />

demographic, exposure and medical<br />

factors on the bone Pb concentration <strong>of</strong><br />

subjects with environmental Pb exposure.<br />

101 subjects (49 males, 52 females; aged<br />

11 to 78 yrs) recruited from 49 <strong>of</strong> 123<br />

households geographically located in a<br />

suburban residential neighborhood.<br />

Tibia. Multiple regression.<br />

Suburban population (Throop, n = 269)<br />

exposed to unusually high emissions<br />

during 1963-81 from nearby battery<br />

recycling/secondary smelter. Moosic<br />

served as control community.<br />

Approximately 9% children aged 5-12 yr,<br />

15% 13-17 yr, 40% ≥ 18 yr. Soil and<br />

PbB, L-shell XRF.<br />

Examined whether environmental<br />

exposure to Pb during childhood was<br />

associated with current adverse<br />

neurobehavioral effects. K-shell XRF.<br />

Formerly exposed as children 19-30 yr<br />

(n = 238, age 19-30 yr).<br />

Referents (n = 258)<br />

<strong>Lead</strong> Measurement (SD or range)<br />

PbB in µg/dL, Bone Pb in µg/g Bone Mineral Findings, Interpretation<br />

Negative EDTA test results (n = 30): PbB 30 ± 5<br />

µg/dL, tibia Pb 12 ± 2 µg/g (range 7-52).<br />

Positive EDTA test results (n = 29): PbB 39 ± 8<br />

µg/dL, tibia Pb 37 ± 3 µg/g (range 7-200).<br />

Mean (SD) bone Pb12.7 (14.6).<br />

Log-trans<strong>for</strong>med bone Pb highly correlated with<br />

age (r = 0.71; p # 0.0001). Gender differences in<br />

log-trans<strong>for</strong>med bone Pb values were<br />

insignificant up until the 6 th decade.<br />

No significant differences in tibia Pb found<br />

among three age groups in Moosic or Throop.<br />

Mooaic: means 5-12 yr, 6 µg/g; 13-17 yr, 8 µg/g;<br />

$18 yr, 7 µg/g<br />

Throop: means 5-12 yr, 12 ± 1 µg/g; 13-17 yr,<br />

15 ± 2 µg/g; $18 yr, 12 ± 1 µg/g.<br />

Exposed group:<br />

PbB 2.9 µg/dL; tibia Pb 4.6 µg/g.<br />

Referent group:<br />

PbB 1.6 µg/dL; tibia Pb 0.6 µg/g.<br />

From PbB and LXRF alone, 90% <strong>of</strong> Pb-toxic<br />

children were correctly classified as being<br />

EDTA-positive or -negative. LXRF may be<br />

capable <strong>of</strong> replacing EDTA testing.<br />

Bone Pb showed no significant change up to<br />

age 20 yr, increased with the same slope in<br />

men and women between ages 20 and 55 yrs,<br />

and then increased at a faster rate in men older<br />

than 55 yrs.<br />

No change in bone Pb with age. Baseline<br />

values <strong>for</strong> bone Pb in the environmentally<br />

exposed population <strong>of</strong> Moosic can serve as a<br />

reference baseline <strong>for</strong> contemporary bone Pb<br />

levels in similar communities in the <strong>US</strong>A.

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