TOXICOLOGICAL PROFILE FOR CHROMIUM - Davidborowski.com
TOXICOLOGICAL PROFILE FOR CHROMIUM - Davidborowski.com TOXICOLOGICAL PROFILE FOR CHROMIUM - Davidborowski.com
CHROMIUM 3266. ANALYTICAL METHODSprecipitation. These methods have a number of inherent limitations including being tedious and subjectto considerable interindividual and interlaboratory variations (Singh et al. 1998b). Only one study hasattempted to utilize this biomarker, and it was found that volunteers exposed to chromium in drinkingwater showed no increase in protein-DNA crosslinking in blood cells (Kuykendall et al. 1996). Thissuggests that this procedure may not be sensitive enough for use in environmental monitoring unless anindividual has received a potentially toxic level of exposure. Chromium forms chromium-DNAcomplexes inside of cells and these complexes constitute a potential biomarker for the assessment ofenvironmental or occupational exposure. Recently, a novel method has been described for the sensitivedetection of chromium-DNA adducts using inductively coupled plasma mass spectrometry (Singh et al.1998b). The detection limits of this method are in the parts per trillion range and allows for the detectionof as few as 2 chromium adducts per 10,000 bases, which coupled with the low DNA samplerequirements, make this method sensitive enough to measure background levels in the population. Thereare no data to determine whether there are age-specific biomarkers of exposure or effects or anyinteractions with other chemicals that would be specific for children.Methods for Determining Parent Compounds and Degradation Products in EnvironmentalMedia. Air contaminated with chromium(VI), particularly in occupational settings, are of greatconcern. Methods have been developed that can determine low levels of total chromium andchromium(VI) in the air (Barrie and Hoff 1985; CARB 1990; NIOSH 1994c, 1994d; Sheehan et al. 1992).These methods have detection limits in the ng/m 3 range with excellent recoveries (90% or better). Thesemethods are sufficient to determine background chromium levels in the environment and levels at whichhealth effects may occur. Chromium can be detected in water at concentrations in the ppb range (EPA1983, 1996a; Harzdorf and Janser 1984) with recoveries of 90% or greater being reported. Methods areavailable that can differentiate chromium(VI) from chromium(III) in water samples (EPA 1986c). Areliable analytical method for extracting and quantifying chromium, including chromium(VI), from soilsurfaces has also been reported (EPA 1997). Current analytical methods exist that are sufficient formeasuring background levels of chromium in soil (EPA 1996b, 1997) and water (EPA 1983, 1986a,1996a).6.3.2 Ongoing StudiesNo ongoing studies regarding the determination of different speciated forms of chromium (as opposed tototal chromium content) in biological or some environmental media (e.g., soil, sediment) were found.
CHROMIUM 3277. REGULATIONS AND ADVISORIESInternational, national, and state regulations and guidelines pertinent to human exposure to chromium aresummarized in Table 7-1.Chromium disposal is regulated by the Clean Water Act Effluent Guidelines for the following industrialpoint sources: textiles, electroplating, organic chemicals, inorganic chemicals, petroleum refining, ironand steel manufacturing, nonferrous metal manufacturing, steam electric, ferroalloy, leather tanning andfinishing, asbestos, rubber, timber products processing, metal finishing, mineral mining, paving androofing, paint formulating, ink formulating, gum and wood, carbon black, battery manufacturing, coilcoating, porcelain enameling, aluminum forming, copper forming, electrical and electronic components,and nonferrous metals forming (EPA 1998b).An MRL of 0.000005 mg chromium(VI)/m 3 has been derived for intermediate-duration inhalationexposure to chromium(VI) as chromium trioxide mist and other dissolved hexavalent chromium aerosolsand mists. The MRL is based on a LOAEL of 0.002 mg chromium(VI)/m 3 for upper respiratory effects inhumans in the occupational exposure study by Lindberg and Hedenstierna (1983) which spanned bothintermediate and chronic durations.In the 1998 Draft for Public Comment, an MRL of 0.0001 mg chromium(VI)/m 3 had been derived forboth intermediate and chronic exposures as chromium trioxide mist and other dissolved hexavalentchromium aerosols and mists. This MRL was also based on the study Lindberg and Hedenstierna (1983),but an exposure level of 0.001 mg chromium(VI)/m 3 had been considered a NOAEL, and there had beenno adjustment from intermittent to continuous exposure. Further evaluation of this study indicated that aNOAEL could not be clearly defined; therefore, the LOAEL of 0.002 mg chromium(VI)/m 3 was selectedand adjusted for continuous exposure for the concern that the nasal lesions could accumulate at a greaterrate than the repair mechanisms. The MRL of 0.000005 mg/m 3 no longer applies for chronic exposurebecause concern that carcinogenicity associated with chronic exposure to hexavalent chromiumcompounds takes precedence.An MRL of 0.001 mg chromium(VI)/m 3 has been derived for intermediate-duration inhalation exposureto chromium(VI) as particulate hexavalent chromium compounds. The MRL is based on a benchmarkconcentration of 0.016 mg chromium(VI)/m 3 for increases in lactate dehydrogenase activity inbronchiolavage fluid from rats in the study by Glaser et al. (1990).
- Page 296 and 297: CHROMIUM 2764. PRODUCTION, IMPORT/E
- Page 298 and 299: CHROMIUM 2784. PRODUCTION, IMPORT/E
- Page 301 and 302: CHROMIUM 2815. POTENTIAL FOR HUMAN
- Page 303 and 304: Derived from HazDat 2000Figure 5-2.
- Page 305 and 306: CHROMIUM 2855. POTENTIAL FOR HUMAN
- Page 307 and 308: State bTable 5-2. Releases to the E
- Page 309 and 310: State bTable 5-2. Releases to the E
- Page 311 and 312: CHROMIUM 2915. POTENTIAL FOR HUMAN
- Page 313 and 314: CHROMIUM 2935. POTENTIAL FOR HUMAN
- Page 315 and 316: CHROMIUM 2955. POTENTIAL FOR HUMAN
- Page 317 and 318: CHROMIUM 2975. POTENTIAL FOR HUMAN
- Page 319 and 320: CHROMIUM 2995. POTENTIAL FOR HUMAN
- Page 321 and 322: CHROMIUM 3015. POTENTIAL FOR HUMAN
- Page 323 and 324: CHROMIUM 3035. POTENTIAL FOR HUMAN
- Page 325 and 326: CHROMIUM 3055. POTENTIAL FOR HUMAN
- Page 327 and 328: CHROMIUM 3075. POTENTIAL FOR HUMAN
- Page 329 and 330: CHROMIUM 3095. POTENTIAL FOR HUMAN
- Page 331 and 332: CHROMIUM 3115. POTENTIAL FOR HUMAN
- Page 333 and 334: CHROMIUM 3135. POTENTIAL FOR HUMAN
- Page 335 and 336: CHROMIUM 3156. ANALYTICAL METHODSTh
- Page 337 and 338: Sample matrixTable 6-1. Analytical
- Page 339 and 340: CHROMIUM 3196. ANALYTICAL METHODS6.
- Page 341 and 342: Sample matrixOccupational air(weldi
- Page 343 and 344: Sample matrixWaste water 1986(chrom
- Page 345: CHROMIUM 3256. ANALYTICAL METHODS6.
- Page 349 and 350: CHROMIUM 3297. REGULATIONS AND ADVI
- Page 351 and 352: CHROMIUM 3317. REGULATIONS AND ADVI
- Page 353 and 354: CHROMIUM 3337. REGULATIONS AND ADVI
- Page 355 and 356: CHROMIUM 3357. REGULATIONS AND ADVI
- Page 357 and 358: CHROMIUM 3377. REGULATIONS AND ADVI
- Page 359 and 360: CHROMIUM 3398. REFERENCES*Aaseth J,
- Page 361 and 362: CHROMIUM 3418. REFERENCES*Anderson
- Page 363 and 364: CHROMIUM 3438. REFERENCES*Baranowsk
- Page 365 and 366: CHROMIUM 3458. REFERENCESBlack CB,
- Page 367 and 368: CHROMIUM 3478. REFERENCES*Buckell M
- Page 369 and 370: CHROMIUM 3498. REFERENCES*Chen NSC,
- Page 371 and 372: CHROMIUM 3518. REFERENCESCriqui M,
- Page 373 and 374: CHROMIUM 3538. REFERENCESDOD. 1947.
- Page 375 and 376: CHROMIUM 3558. REFERENCES*EPA. 1984
- Page 377 and 378: CHROMIUM 3578. REFERENCES*EPA. 1996
- Page 379 and 380: CHROMIUM 3598. REFERENCESFlint GN,
- Page 381 and 382: CHROMIUM 3618. REFERENCES*Gale TF,
- Page 383 and 384: CHROMIUM 3638. REFERENCESGriepink B
- Page 385 and 386: CHROMIUM 3658. REFERENCES*Hayes RB,
- Page 387 and 388: CHROMIUM 3678. REFERENCESHunt CD, S
- Page 389 and 390: CHROMIUM 3698. REFERENCES*Jansen LH
- Page 391 and 392: CHROMIUM 3718. REFERENCESKeith RL,
- Page 393 and 394: CHROMIUM 3738. REFERENCES*Korallus
- Page 395 and 396: CHROMIUM 3758. REFERENCES*Laborda R
<strong>CHROMIUM</strong> 3277. REGULATIONS AND ADVISORIESInternational, national, and state regulations and guidelines pertinent to human exposure to chromium aresummarized in Table 7-1.Chromium disposal is regulated by the Clean Water Act Effluent Guidelines for the following industrialpoint sources: textiles, electroplating, organic chemicals, inorganic chemicals, petroleum refining, ironand steel manufacturing, nonferrous metal manufacturing, steam electric, ferroalloy, leather tanning andfinishing, asbestos, rubber, timber products processing, metal finishing, mineral mining, paving androofing, paint formulating, ink formulating, gum and wood, carbon black, battery manufacturing, coilcoating, porcelain enameling, aluminum forming, copper forming, electrical and electronic <strong>com</strong>ponents,and nonferrous metals forming (EPA 1998b).An MRL of 0.000005 mg chromium(VI)/m 3 has been derived for intermediate-duration inhalationexposure to chromium(VI) as chromium trioxide mist and other dissolved hexavalent chromium aerosolsand mists. The MRL is based on a LOAEL of 0.002 mg chromium(VI)/m 3 for upper respiratory effects inhumans in the occupational exposure study by Lindberg and Hedenstierna (1983) which spanned bothintermediate and chronic durations.In the 1998 Draft for Public Comment, an MRL of 0.0001 mg chromium(VI)/m 3 had been derived forboth intermediate and chronic exposures as chromium trioxide mist and other dissolved hexavalentchromium aerosols and mists. This MRL was also based on the study Lindberg and Hedenstierna (1983),but an exposure level of 0.001 mg chromium(VI)/m 3 had been considered a NOAEL, and there had beenno adjustment from intermittent to continuous exposure. Further evaluation of this study indicated that aNOAEL could not be clearly defined; therefore, the LOAEL of 0.002 mg chromium(VI)/m 3 was selectedand adjusted for continuous exposure for the concern that the nasal lesions could accumulate at a greaterrate than the repair mechanisms. The MRL of 0.000005 mg/m 3 no longer applies for chronic exposurebecause concern that carcinogenicity associated with chronic exposure to hexavalent chromium<strong>com</strong>pounds takes precedence.An MRL of 0.001 mg chromium(VI)/m 3 has been derived for intermediate-duration inhalation exposureto chromium(VI) as particulate hexavalent chromium <strong>com</strong>pounds. The MRL is based on a benchmarkconcentration of 0.016 mg chromium(VI)/m 3 for increases in lactate dehydrogenase activity inbronchiolavage fluid from rats in the study by Glaser et al. (1990).