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

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AX6-79<br />

Table AX6-4.1 (cont’d). Renal Effects <strong>of</strong> <strong>Lead</strong> in the General Population<br />

Reference, Study<br />

Location, and<br />

Period Study Description Pb Measurement Findings, Interpretation<br />

Asia<br />

Lin et al. (1993)<br />

Taiwan<br />

Study date not<br />

provided<br />

Satarug et al. (2004)<br />

Bangkok, Thailand<br />

Study date not<br />

provided<br />

123 adults living near a Pb battery factory <strong>for</strong> more<br />

than 10 yrs.<br />

Divided into 3 groups by proximity to the factory.<br />

Group 1 ≤500 m (n = 49)<br />

Group 2 1000-1500 m (n = 47)<br />

Group 3 farther away (n = 27)<br />

Exclusionary criteria included history <strong>of</strong> exposure to<br />

nephrotoxicants and nephrotoxicant medications, such<br />

as NSAIDs.<br />

24 h urinary NAG excretion<br />

3.3 U/day (Group 1)<br />

2.4 U/day (Group 3)<br />

Multiple linear regression with adjustment <strong>for</strong> age.<br />

118 Thai adults (53 men, 65 women).<br />

Renal outcome measures noted below, also include<br />

BUN and total urinary protein.<br />

Serum creatinine<br />

0.94 mg/dL (males)<br />

0.66 mg/dL (females)<br />

Urinary NAG<br />

4.4 U/g creatinine (males)<br />

4.6 U/g creatinine (females)<br />

Urinary ∃ 2-microglobulin<br />

51 µg/g creatinine (males)<br />

29 µg/g creatinine (females)<br />

Mean blood Pb<br />

16.6 µg/dL (Group 1)<br />

13.5 µg/dL (Group 2)<br />

7.9 µg/dL (Group 3)<br />

EDTA diagnostic chelation<br />

(done in Group 1)<br />

126.1 µg/24 hrs<br />

Mean “serum” Pb<br />

0.42 µg/dL (males) 0.3 µg/dL<br />

(females)<br />

Note – cannot determine from<br />

article if actually serum Pb<br />

(much less commonly used) or<br />

blood Pb.<br />

Mean urinary Pb<br />

1.3 µg/g creatinine (males)<br />

2.4 µg/g creatinine<br />

(females)<br />

Urinary cadmium also<br />

assessed.<br />

Significantly higher prevalence <strong>of</strong> abnormal urinary NAG<br />

found in the exposed group 1 compared to the control group 3<br />

(55.6% compared to 11.1%; p < 0.001). However, mean<br />

NAG not significantly higher in Group 1.<br />

In all 45 participants in whom both measures were obtained,<br />

EDTA chelatable Pb was not correlated with urinary NAG<br />

excretion. However, a significant correlation between EDTA<br />

chelatable Pb #200 µg/24 hrs and urinary NAG excretion was<br />

observed in the 39 participants in this group. Further<br />

evaluation with multiple linear regression, adjusting <strong>for</strong> age,<br />

revealed a ∃ = 0.034 (95% CI: 0.009, 0.059); p = 0.01.<br />

No correlation noted between blood Pb level and urinary<br />

NAG.<br />

Limitations = small sample size, plots indicate potential <strong>for</strong><br />

influential outliers.<br />

In men, urinary Pb excretion correlated only with urinary<br />

protein at borderline significance (r = 0.22, p < 0.06).<br />

In women, urinary Pb excretion correlated with urinary NAG<br />

(r = 0.5, p < 0.001), protein (r = 0.31, p = 0.01) and<br />

∃ 2-microglobulin (r = 0.36, p = 0.002) excretion.<br />

After adjustment <strong>for</strong> urinary cadmium, only association<br />

between urinary Pb and NAG remained significant.<br />

Three urinary renal biomarkers correlated with urinary<br />

cadmium, although only at borderline significance (p = 0.06)<br />

<strong>for</strong> ∃2-microglobulin.<br />

Limitations = small sample size, Pb dose assessment since<br />

only urine Pb used in renal analyses, limited data analysis.

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