Oral bioavailability of lead and arsenic from a NIST standard reference soil material

被引:107
作者
Ellickson K.M. [1 ]
Meeker R.J. [2 ]
Gallo M.A. [2 ]
Buckley B.T. [3 ]
Lioy P.J. [2 ,4 ]
机构
[1] Joint Ph.D. Program in Exposure Assessment, Rutgers University, University of Medicine and Dentistry of New Jersey-Robert Wood Johnson Medical School, Piscataway, NJ 08854
[2] Department of Environmental and Community Medicine, Robert Wood Johnson Medical School, University of Medicine and Dentistry of New Jersey, Piscataway, NJ 08854
[3] Center for Analytical Excellence, Rutgers University, University of Medicine and Dentistry of New Jersey, Piscataway, NJ 08854
[4] Exposure Measurement and Assessment Division, Piscataway, NJ 08855
关键词
Arsenic; Oral Bioavailability; Soil Extraction; Intestinal Fluid; Metal Solubility;
D O I
10.1007/s002440010155
中图分类号
学科分类号
摘要
The oral bioavailability of soil contaminants is measured using in vitro or in vivo techniques. Current efforts in our laboratory are focused on the comparisons of in vitro methods for bioavailability estimation with the presently employed in vivo techniques, such as animal models. We present a comparison of two techniques for oral bioavailability estimation: in vitro dissolution and in vivo rat feeding using a standard reference soil. Lead (Pb) and arsenic (As) were chosen because of the range of concentration in this soil as well as the large historical database of bioavailability values for these metals. Metal solubility was measured using a sequential soil extraction in synthetic analogues of human saliva, gastric and intestinal fluids. The soluble metal was defined as the bioaccessible fraction. Oral bioavailability of Pb and As was measured in Sprague Dawley rats by determining metal levels in the major organs and urine, feces, and blood at 1-, 2-, and 3-day time points. Extractions to determine bioaccessibility yielded a gastric component of 76.1% and 69.4% for Pb and As, respectively, and intestinal components were 10.7% and 65.9%. The oral bioavailability of the standard reference soil was 0.7% and 37.8% for Pb and As, respectively. Bioaccessibility was greater than bioavailability for both metals in both gastrointestinal compartments. Although Pb had the highest soil concentration of the selected metals, it was the least bioavailable, while As was highly available in both the in vitro and in vivo method. These types of data allow for an in vitro-in vivo comparison of a soil whose metal concentrations have been certified and validated.
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页码:128 / 135
页数:7
相关论文
共 41 条
[1]  
Barry P.S.I., A comparison of concentration of lead in human tissue, Brit J Ind Med, 32, pp. 119-139, (1975)
[2]  
Blake K.C.H., Barbezat G.O., Mann M., Effect of dietary constituents on the gastrointestinal absorption of 203Pb in man, Environ Res, 30, pp. 182-187, (1983)
[3]  
Buchet J.P., Lauwerys R., Roels H., Urinary excretion of inorganic arsenic and its metabolites after repeated ingestion of sodium meta arsenite by volunteers, Int Arch Occup Environ Health, 48, pp. 111-118, (1981)
[4]  
Clapp T.C., Umbreit T.H., Meeker R.J., Kosson D.S., Gray D., Gallo M.A., Bioavailability of lead and chromium from encapsulated pigment materials, Bull Environ Contam Toxicol, 46, 2, pp. 271-275, (1991)
[5]  
Conrad M.E., Barton J.C., Factors affecting the absorption and excretion of lead in the rat, Gastroenterology, 74, 4, pp. 731-740, (1978)
[6]  
Crecelius E.A., Changes in the chemical speciation of arsenic following ingestion by man, Environ Health Perspect, 19, pp. 147-150, (1977)
[7]  
Davis A., Ruby M., Bergstrom P.D., Bioavailability of arsenic and lead in soils from the Butte, Montana, mining district, Environ Sci Technol, 27, 7, pp. 1415-1425, (1993)
[8]  
Davis A., Ruby M.V., Goad P., Eberle S., Chryssoulis S., Mass balance on surface bound, mineralogic, and total lead concentrations as related to industrial aggregate bioaccessibility, Environ Sci Technol, 31, 1, pp. 37-44, (1997)
[9]  
Diamond G.L., Goodrum P.E., Felter S.P., Ruoff W.L., Gastrointestinal absorption of metals, Drug Chem Toxicol, 20, 4, pp. 345-368, (1997)
[10]  
Guidance for data usability in risk assessment, (1990)