(Cr) Toxicity | ATSDR - CSEM - Agency for Toxic Substances and ...
(Cr) Toxicity | ATSDR - CSEM - Agency for Toxic Substances and ...
(Cr) Toxicity | ATSDR - CSEM - Agency for Toxic Substances and ...
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<strong>Agency</strong> <strong>for</strong> <strong>Toxic</strong> <strong>Substances</strong> <strong>and</strong> Disease Registry Chromium <strong><strong>Toxic</strong>ity</strong><br />
Case Studies in Environmental Medicine (<strong>CSEM</strong>)<br />
What Are the Routes of Exposure <strong>for</strong> Chromium?<br />
Learning<br />
Objectives<br />
Upon completion of this section, you will be able to<br />
• identify the routes of exposure to chromium.<br />
Introduction The entry routes of chromium into the human body are inhalation, ingestion,<br />
<strong>and</strong> dermal absorption. Occupational exposure generally occurs through<br />
inhalation <strong>and</strong> dermal contact, whereas the general population is exposed<br />
most often by ingestion through chromium content in soil, food, <strong>and</strong> water.<br />
Inhalation After human exposure to <strong>Cr</strong>(III) by inhalation, urinary concentrations of<br />
chromium were found to be increased indicating respiratory absorption<br />
[Aitio, Jarvisalo et al. 1984; Foa, Riboldi et al. 1988; Dayan <strong>and</strong> Paine 2001].<br />
Data from a few animal experiments indicate that with equal solubility,<br />
<strong>Cr</strong>(VI) compounds are absorbed more readily than <strong>Cr</strong>(III) compounds,<br />
probably because <strong>Cr</strong>(VI) readily penetrates cell membranes [Mertz 1969;<br />
Wieg<strong>and</strong>, Ottenwalder et al. 1984].<br />
Ingestion<br />
<strong>Cr</strong>(VI) is reduced to <strong>Cr</strong>(III) in the lower respiratory tract by the<br />
epithelial lining fluid <strong>and</strong> by pulmonary alveolar macrophages [Dayan<br />
<strong>and</strong> Paine 2001]. One study showed that at equivalent numbers of cells,<br />
the reducing efficiency of alveolar macrophages by biochemical<br />
mechanisms was significantly greater in tobacco smokers than in<br />
nonsmokers [Petrilli, Rossi et al. 1986].<br />
In general, <strong>Cr</strong>(VI) compounds are better absorbed through the intestinal<br />
mucosa than the <strong>Cr</strong>(III) compounds. However, due to the actions of stomach<br />
acid <strong>and</strong> other components within the gastrointestinal tract, most of an<br />
ingested <strong>Cr</strong>(VI) dosage is converted to <strong>Cr</strong>(III) [Cohen, Kargacin et al. 1993].<br />
In humans <strong>and</strong> animals, less than 1% of inorganic <strong>Cr</strong>(III) <strong>and</strong> about 10% of<br />
inorganic <strong>Cr</strong>(VI) are absorbed from the gut; the latter amount is slightly<br />
higher in a fasting state [Donaldson <strong>and</strong> Barreras 1966; Dayan <strong>and</strong> Paine<br />
2001].<br />
Skin Data from volunteers <strong>and</strong> indirect evidence from occupational studies<br />
indicate that absorption of <strong>Cr</strong>(VI) compounds can occur through intact skin<br />
[Baranowska-Dutkiewicz 1981]. Studies in experimental animals showed<br />
poor absorption of <strong>Cr</strong>(III) compounds following dermal route [Dayan <strong>and</strong><br />
Paine 2001].<br />
Key Points<br />
• Occupational exposure generally occurs through inhalation <strong>and</strong> dermal<br />
contact, whereas the general population is exposed most often by<br />
ingestion through chromium content in soil, food, <strong>and</strong> water.<br />
• The majority of <strong>Cr</strong>(VI) that enters the body via inhalation or ingestion<br />
is quickly reduced to <strong>Cr</strong>(III).<br />
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