TOXICOLOGICAL PROFILE FOR CHROMIUM - Davidborowski.com
TOXICOLOGICAL PROFILE FOR CHROMIUM - Davidborowski.com TOXICOLOGICAL PROFILE FOR CHROMIUM - Davidborowski.com
CHROMIUM 1862. HEALTH EFFECTSthe cement industry (Engebrigsten 1952), in railroad systems and diesel locomotive repair shops whereantirust diesel-engine coolants and radiator fluids contained sodium chromate (Kaplan and Zeligman1962; Winston and Walsh 1951), in tanneries (Fregert 1975), and in the welding, plating, wood and paperindustries (Burrows 1983). Other sources of chromium that have resulted in chromium sensitivity includedichromate-containing detergents and bleach (Wahba and Cohen 1979), glues, machine oils, foundrysand, match heads, boiler linings, and magnetic tapes (Burrows 1983).Several studies have estimated the exposure level necessary to elicit a 10% response in chromiumsensitizedindividuals. Nethercott et al. (1994) examined 54 individuals known to be sensitive tochromium-induced allergic contact dermatitis. For chromium(VI), about 10% elicited a response at0.09 µg chromium(VI)/cm 2 , whereas similar studies with chromium(III) were essentially negative. Sternet al. (1993) examined the data from seven studies conducted mostly in the 1960s on chromium(VI) patchtests and developed an aggregate dose-response curve using the Probit model. Although there wereconsiderable differences in methodologies and in the chromium(VI) compounds used (potassiumchromate, potassium dichromate, chromic acid, and lead acetate) with some administered in basic watersolutions, the aggregate data described a regular and consistent dose-response relationship which had astrong linear correlation (r=0.85). From this line, a 10% response of allergic dermatitis would occur inthe sensitized population at 10 ppm chromium(VI) and 5% at 7.6 ppm chromium(VI). Similarly,Paustenbach et al. (1992) used computer data fitting techniques to estimate the 10% threshold level. Thedata from eight historical chromium sensitization threshold studies involving patch testing with potassiumdichromate were used to estimate a weighted mean 10% threshold of 54 ppm chromium(VI) (150 ppmpotassium dichromate). As noted by Paustenbach et al. (1992), there are a number of methodicallimitations to the older patch test studies, including failure to disclose information on the diagnosticcriteria used to determine allergy, duration of application, and analytical method used to verify chromiumconcentration and valence. Thus, the 54 ppm threshold level may be somewhat conservative. Scott andProctor (1997) re-analyzed the data from three older chromium sensitization threshold elicitation studieswith information on the surface area of the patches and the more recent study by Nethercott et al. (1994).The 10% minium elicitation threshold ranged from 0.55 to 12.5 µg/cm 2 for the historical studies, ascompared to 0.09 µg/cm 2 for the Nethercott et al. (1994) study. Scott and Proctor (1997) note that thedifference between the 10% elicitation thresholds may be due to the use of 0.5% potassium dichromatediagnostic patches in the historical studies compared to 0.25% potassium dichromate in the more recentstudy. Using the lower concentration probably eliminated individuals who were less sensitive and thosewho had an irritant rather than allergic response to the higher concentration.
CHROMIUM 1872. HEALTH EFFECTSThe threshold concentration of extractable chromium(VI) in solid material was considered by Stern et al.(1993) to be as low as 10 ppm. The lowest observed effect level for elicitation of allergic contactdermatitis from ingestion of chromium(VI) was considered to be 0.26 ppm. In regard to the thresholdconcentration of chromium(VI) in soil for elicitation of contact dermatitis, the extractability ofchromium(VI) from soil matrix was considered to be a factor. The effective concentration at the surfaceof the skin is determined by the concentration of chromium(VI) in solution following extraction from soilmatrix. A study by Horowitz and Finley (1993) suggests that dermal contact with soil contaminated withchromite ore processing residue would probably not elicit allergic contact dermatitis in sensitizedindividuals. This study estimated that 0.1% or less of the chromium(VI) in chromite ore processingresidue would leach out in the presence of human sweat. Thus, the chromium(VI) concentration in thesoil would have to be 10,000–54,000 ppm (estimation based on 10–54 ppm sensitization elicitationthreshold).An inhalation immunological study in rats indicated that sodium dichromate stimulated the humoralimmune system, affected the T-lymphocytes, and increased the phagocytic activity of macrophages(Glaser et al. 1985). Pulmonary inflammation was indicated in rats repeatedly exposed to atmospherescontaining soluble potassium chromate, as evidenced by increases in total recoverable cells, neutrophils,and monocytes in bronchoalveolar lavage, and reduced percentages of pulmonary macrophages (Cohen etal. 1998); this was not seen in rats similarly exposed to insoluble barium chromate. Splenocytes from ratsthat were exposed to potassium chromate in the drinking water showed increased proliferative responsesto T- and B-cell mitogens and to the antigen mitomycin C. The response to mitomycin C was enhanced5-fold when potassium chromate was added to splenocytes from chromium(VI)-exposed rats, indicating asensitization phenomenon (Snyder and Valle 1991). Contact dermatitis has been elicited in guinea pigsand mice by both chromium(VI) and chromium(III) compounds (Gross et al. 1968; Jansen and Berrens1968; Mor et al. 1988).Since exposure to low levels of chromium as found in consumer products can result in sensitization,hypersensitive individuals may develop rashes and erythema from contact with soil contaminated withhigh concentrations or consumer products containing chromium.Neurological Effects. Information regarding neurological effects after exposure to chromium or itscompounds is limited. Dizziness, headache, and weakness were experienced by workers in a chromeplating plant where poor exhaust resulted in excessively high concentrations of chromium trioxide(Lieberman 1941). Such poor working conditions are unlikely to still exist in the United States due to
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<strong>CHROMIUM</strong> 1862. HEALTH EFFECTSthe cement industry (Engebrigsten 1952), in railroad systems and diesel lo<strong>com</strong>otive repair shops whereantirust diesel-engine coolants and radiator fluids contained sodium chromate (Kaplan and Zeligman1962; Winston and Walsh 1951), in tanneries (Fregert 1975), and in the welding, plating, wood and paperindustries (Burrows 1983). Other sources of chromium that have resulted in chromium sensitivity includedichromate-containing detergents and bleach (Wahba and Cohen 1979), glues, machine oils, foundrysand, match heads, boiler linings, and magnetic tapes (Burrows 1983).Several studies have estimated the exposure level necessary to elicit a 10% response in chromiumsensitizedindividuals. Nethercott et al. (1994) examined 54 individuals known to be sensitive tochromium-induced allergic contact dermatitis. For chromium(VI), about 10% elicited a response at0.09 µg chromium(VI)/cm 2 , whereas similar studies with chromium(III) were essentially negative. Sternet al. (1993) examined the data from seven studies conducted mostly in the 1960s on chromium(VI) patchtests and developed an aggregate dose-response curve using the Probit model. Although there wereconsiderable differences in methodologies and in the chromium(VI) <strong>com</strong>pounds used (potassiumchromate, potassium dichromate, chromic acid, and lead acetate) with some administered in basic watersolutions, the aggregate data described a regular and consistent dose-response relationship which had astrong linear correlation (r=0.85). From this line, a 10% response of allergic dermatitis would occur inthe sensitized population at 10 ppm chromium(VI) and 5% at 7.6 ppm chromium(VI). Similarly,Paustenbach et al. (1992) used <strong>com</strong>puter data fitting techniques to estimate the 10% threshold level. Thedata from eight historical chromium sensitization threshold studies involving patch testing with potassiumdichromate were used to estimate a weighted mean 10% threshold of 54 ppm chromium(VI) (150 ppmpotassium dichromate). As noted by Paustenbach et al. (1992), there are a number of methodicallimitations to the older patch test studies, including failure to disclose information on the diagnosticcriteria used to determine allergy, duration of application, and analytical method used to verify chromiumconcentration and valence. Thus, the 54 ppm threshold level may be somewhat conservative. Scott andProctor (1997) re-analyzed the data from three older chromium sensitization threshold elicitation studieswith information on the surface area of the patches and the more recent study by Nethercott et al. (1994).The 10% minium elicitation threshold ranged from 0.55 to 12.5 µg/cm 2 for the historical studies, as<strong>com</strong>pared to 0.09 µg/cm 2 for the Nethercott et al. (1994) study. Scott and Proctor (1997) note that thedifference between the 10% elicitation thresholds may be due to the use of 0.5% potassium dichromatediagnostic patches in the historical studies <strong>com</strong>pared to 0.25% potassium dichromate in the more recentstudy. Using the lower concentration probably eliminated individuals who were less sensitive and thosewho had an irritant rather than allergic response to the higher concentration.