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Hematologic effects appear to be among the most sensitive indicators of lead
absorption. Lead interference with heme synthesis has been noted in humans and
other mammalian species at blood levels below 10-15 ug/dL. Lead can also lead
to the accumulation of porphyrin in erythrocytes with elevated levels of
erythrocyte protoporphyrin (EP) associated with blood lead levels of 25-
30 ug/dL in adults and 15 ug/dL in children. Anemia is characteristic of more
severe cases of lead poisoning, resulting from erythrocyte destruction and
reduced hemoglobin synthesis (ATSDR 1992).
Renal toxicity has also been observed in victims of lead intoxication.
Reversible proximal tubule damage has been observed primarily in cases of
short-term exposure with reduced glomerular function associated with more
chronic exposures (ATSDR 1992). In adults, chronic exposures to lead can result
in hypertension. Acute exposures can result in peripheral neuropathy and/or
nephropathy. Due to the relationship between maternal body lead stores and fetal
circulation, fetal development can be adversely affected by elevated maternal
body-lead burdens.
USEPA classifies inorganic lead as a category B2, probable human
carcinogen. There is inadequate evidence of carcinogenicity based on human
studies, but several animal bioassays have shown statistically significant
increases in renal tumors following dietary and drinking water exposure to lead
acetate or lead subacetate, two soluble lead salts (IRIS 1999). USEPA has not
calculated a cancer slope factor for inorganic lead because of the large
uncertainties involved, including the effect of age, health, nutritional status, and
body burden (IRIS 1999).
The USEPA has not established a risk reference dose (RfD) for lead because
it appears that some of the observed effects occur at such low doses as to be
essentially without a threshold (IRIS 1999). Because a USEPA derived reference
dose is not available, an alternative approach called the integrated uptake/
biokinetic model is used to evaluate the potential for adverse health effects due
to lead. This is a validated model that calculates blood-lead levels based on
estimated exposure doses of lead to children in to various media such as food,
soil, dust, and water. Once blood lead levels are estimated, adverse effects can be
predicted. To determine an estimation of the health risk due to exposure to lead
at the site of interest, a threshold based on blood lead has been defined, at
10 ug/dl (CDC 1991).
Toxicokinetics
Absorption through the gastrointestinal tract is a function of many factors
including the fasting state and nutritional status of the individual, solubility of
the lead, and particle size. For dietary lead, absorption in children is
approximately 50 percent compared with 5 to 15 percent gastrointestinal lead
absorption in adults (World Health Organization (WHO) 1995). Lead is not well
absorbed dermally, from 0.006 percent to less than 0.3 percent (WHO 1995).
Lead is well absorbed by the lungs, and absorption depends on a number of
factors. These include whether the lead is in particulate or vapor form and the
D45
Appendix D Toxicological Profiles
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