TOXICOLOGICAL PROFILE FOR CHROMIUM - Davidborowski.com
TOXICOLOGICAL PROFILE FOR CHROMIUM - Davidborowski.com TOXICOLOGICAL PROFILE FOR CHROMIUM - Davidborowski.com
CHROMIUM 2845. POTENTIAL FOR HUMAN EXPOSUREaquatic phase occurs in the soluble state or as suspended solids adsorbed onto clayish materials, organics,or iron oxides. Most of the soluble chromium is present as chromium(VI) or as soluble chromium(III)complexes and generally accounts for a small percentage of the total. Soluble chromium(VI) may persistin some bodies of water for a long time, but will eventually be reduced to chromium(III) by organicmatters or other reducing agents in water (Cary 1982; EPA 1984a). The residence times of chromium(total) in lake water range from 4.6 to 18 years (Schmidt and Andren 1984). Chromium(III) in soil ismostly present as insoluble carbonate and oxide of chromium(III); therefore, it will not be mobile in soil.The solubility of chromium(III) in soil and its mobility may increase due to the formation of solublecomplexes with organic matters in soil. A lower soil pH may facilitate complexation. Chromium has alow mobility for translocation from roots to the aboveground parts of plants (Calder 1988; Cary 1982;EPA 1984a, 1985a; King 1988; Stackhouse and Benson 1989).The arithmetic mean concentrations of total chromium in the ambient air in United States, urban,suburban, and rural areas monitored during 1977–1984 ranged from 0.005 to 0.525 µg/m 3 (EPA 1984a,1990b). The chromium concentrations in U.S. river waters usually range from
CHROMIUM 2855. POTENTIAL FOR HUMAN EXPOSURE5.2 RELEASES TO THE ENVIRONMENTAccording to the Toxics Release Inventory (TRI), in 1997 a total of 32,811,382 pounds (14,883,243 kg)of chromium was released to the environment from 3,391 large processing facilities (TRI97 1999).Table 5-1 lists estimated amounts released from specific anthropogenic sources during an unspecifiedtime prior to 1990, including the percentage which were in the hexavalent state (EPA 1990b). Inaddition, an estimated 272,732 pounds (123,711 kg) were released by manufacturing and processingfacilities to publicly owned treatment works (POTWs) and an estimated 5,788,705 pounds(2,625,757 kg) were transferred offsite (TRI97 1999). The TRI data should be used with caution becauseonly certain types of facilities are required to report. This is not an exhaustive list.5.2.1 AirAccording to the Toxics Release Inventory, in 1997 the estimated releases of chromium of706,204 pounds (320,334 kg) to the air from 3,391 large processing facilities accounted for about 2.2% oftotal environmental releases (TRI97 1999). Table 5-2 lists amounts released from facilities. The TRIdata should be used with caution, however, since only certain types of facilities are required to report.This is not an exhaustive list.Total chromium has been identified in 45 air samples collected from 1,036 NPL hazardous waste siteswhere it was detected in some environmental media (HazDat 2000). Chromium(VI) has been identifiedin 4 air samples collected from 120 NPL hazardous waste sites where it was detected in someenvironmental media (HazDat 2000).Continental dust flux is the main natural source of chromium in the atmosphere; volcanic dust and gasflux are minor natural sources of chromium in the atmosphere (Fishbein 1981). Chromium is releasedinto the atmosphere mainly by anthropogenic stationary point sources, including industrial, commercial,and residential fuel combustion, via the combustion of natural gas, oil, and coal. Other importantanthropogenic stationary point sources of chromium emission to the atmosphere are metal industries. Ithas been estimated that .16,000 metric tons of chromium were emitted into the atmosphere from U.S.anthropogenic sources in 1970 (EPA 1984a). These older estimates indicated that emissions from themetal industry ranged from 35% to 86% of the total, and emissions from fuel combustion ranged from11% to 65% of the total (EPA 1978). More recent estimates of atmospheric chromium emission in 1976and 1980 in the Los Angeles, California, and Houston, Texas, areas indicate that emissions from
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<strong>CHROMIUM</strong> 2855. POTENTIAL <strong>FOR</strong> HUMAN EXPOSURE5.2 RELEASES TO THE ENVIRONMENTAccording to the Toxics Release Inventory (TRI), in 1997 a total of 32,811,382 pounds (14,883,243 kg)of chromium was released to the environment from 3,391 large processing facilities (TRI97 1999).Table 5-1 lists estimated amounts released from specific anthropogenic sources during an unspecifiedtime prior to 1990, including the percentage which were in the hexavalent state (EPA 1990b). Inaddition, an estimated 272,732 pounds (123,711 kg) were released by manufacturing and processingfacilities to publicly owned treatment works (POTWs) and an estimated 5,788,705 pounds(2,625,757 kg) were transferred offsite (TRI97 1999). The TRI data should be used with caution becauseonly certain types of facilities are required to report. This is not an exhaustive list.5.2.1 AirAccording to the Toxics Release Inventory, in 1997 the estimated releases of chromium of706,204 pounds (320,334 kg) to the air from 3,391 large processing facilities accounted for about 2.2% oftotal environmental releases (TRI97 1999). Table 5-2 lists amounts released from facilities. The TRIdata should be used with caution, however, since only certain types of facilities are required to report.This is not an exhaustive list.Total chromium has been identified in 45 air samples collected from 1,036 NPL hazardous waste siteswhere it was detected in some environmental media (HazDat 2000). Chromium(VI) has been identifiedin 4 air samples collected from 120 NPL hazardous waste sites where it was detected in someenvironmental media (HazDat 2000).Continental dust flux is the main natural source of chromium in the atmosphere; volcanic dust and gasflux are minor natural sources of chromium in the atmosphere (Fishbein 1981). Chromium is releasedinto the atmosphere mainly by anthropogenic stationary point sources, including industrial, <strong>com</strong>mercial,and residential fuel <strong>com</strong>bustion, via the <strong>com</strong>bustion of natural gas, oil, and coal. Other importantanthropogenic stationary point sources of chromium emission to the atmosphere are metal industries. Ithas been estimated that .16,000 metric tons of chromium were emitted into the atmosphere from U.S.anthropogenic sources in 1970 (EPA 1984a). These older estimates indicated that emissions from themetal industry ranged from 35% to 86% of the total, and emissions from fuel <strong>com</strong>bustion ranged from11% to 65% of the total (EPA 1978). More recent estimates of atmospheric chromium emission in 1976and 1980 in the Los Angeles, California, and Houston, Texas, areas indicate that emissions from