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PRINCIPLES OF TOXICOLOGY

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340 PROPERTIES AND EFFECTS <strong>OF</strong> METALS<br />

The current daily oral RfD for chromium (+3) is 1.0 mg/kg. The current daily oral RfD for chromium<br />

(+6) is 5 × 10 –3 mg/kg. Chromium (+6) is classified as a Class A (confirmed human carcinogen) by<br />

the inhalation route of exposure only. Chromium (+3) is not classified as a carcinogen by any route of<br />

exposure.<br />

Lead<br />

Lead is a naturally occurring bluish-gray metal found in the earth’s crust. Lead can combine with other<br />

chemicals to form what are known as lead salts. These compounds are water-soluble, while elemental<br />

lead is not. Lead is used in the production of batteries, ammunition, metal products, as well as scientific<br />

and medical equipment. Most of the lead mobilized in the environment is the result of human activities.<br />

Exposure to inorganic lead and inorganic lead compounds or to organic lead compounds can occur<br />

in environmental or occupational circumstances. Inorganic lead exposure is most applicable to general<br />

and occupational exposure. Human body burdens of lead result from inhalation and oral exposure to<br />

inorganic lead. In humans, oral absorption of ingested lead occurs primarily in the gastrointestinal<br />

tract; 50 percent of the oral dose is absorbed by children and 15 percent is absorbed by adults. Typically,<br />

the lead body burden of an average adult human has been reported to range between 100 and 300 mg.<br />

Exposure to lead can affect a number of organs and/or systems in humans and animals. The research<br />

on lead contains dose–response data for humans primarily from studies of occupationally exposed<br />

groups, as well as the general population. Inhalation contributes a greater proportion of the dose for<br />

occupationally exposed groups, and the oral route contributes a greater proportion of the dose for the<br />

general population. The effects of lead are the same regardless of the route of entry into the body and<br />

are well correlated with blood lead level.<br />

Lead in soil and dust are important sources of exposure in children. The Centers for Disease Control<br />

(CDC) in 1985 stated that concentrations of lead in soil or dust at 500–1000 mg/kg are associated with<br />

blood levels in children that exceed background levels. Death from lead poisoning occurred in children<br />

with blood lead levels >125 µg/dL, including several deaths in children who exhibited severe<br />

encephalopathy. The duration of exposure associated with this effect was on the order of a few weeks<br />

or more, and, in some cases, it may have been an acute toxic response. For industrial sites, where access<br />

to soil may be limited or restricted, it was recommended that the upper end of the range that was<br />

identified in the Office of Solid Waste and Emergency Response (OSWER) Directive 9355.4-02 for<br />

lead be used in establishing protective concentrations for lead in soil at industrial sites (range of<br />

500–1000 mg/kg). However, subsequent studies in areas of high lead soil concentrations in mining<br />

areas have not confirmed those recommendations.<br />

Relatively low exposure levels of lead may cause adverse neurological effects in fetuses and young<br />

children. Very low blood lead levels (e.g., 10–20 µg/dL) have been associated with effects on learning<br />

ability. The CDC initially defined lead toxicity in a child as a blood lead level in the range of 25–35<br />

µg/dL, coupled with an erythrocyte protoporphyrin level of >35 µg/dL. The threshold has since been<br />

lowered to 10 µg/dL by that agency. A blood lead level of 50 µg/dL has been determined to be an<br />

approximate threshold for the expression of lead toxicity in exposed adult workers, and the occupational<br />

recommended conservative benchmark typically is 30 µg/dL. Neurobehavioral effects have also<br />

been documented in animal studies as well as human studies.<br />

Lead affects the hematopoietic system by altering the activity of three enzymes involved in heme<br />

biosynthesis. The impairment of heme synthesis has a number of subsequent effects, including<br />

decreased hemoglobin levels and anemia. These effects have been observed in lead workers and in<br />

children with prolonged lead exposure. A decrease in cytochrome P450 content of hepatic microsomes<br />

has been noted in animal studies.<br />

Lead may cause kidney damage as a result of acute or chronic exposure. Reversible proximal tubular<br />

damage can result from acute lead exposure. Heavy, chronic exposure can result in nephritis, interstitial<br />

fibrosis, and tubular atrophy.<br />

Colic—characterized by abdominal pain, constipation, cramps, nausea, vomiting, anorexia, and<br />

weight loss—is a symptom of lead poisoning in occupationally exposed cases and in children.

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