From: Experimental determination of the oral bioavailability and bioaccessibility of lead particles
SUBSTRATE | IVBA% | REFERENCES |
---|---|---|
Flanders soil | 91±4 | |
Oker 11 soil | 56±4 |  |
47 Omaha community smelter soils, US | 68-69 (average) | Â |
HER-2930 smelter soil, US | 69±1.5 (using Dr Drexler’s Pb levels) |  |
 | 85±1.1 (using EPA’s average bulk Pb levels) |  |
17 residential soils, tailings, and slags from mining waste sites, US | 14±1.7 to 90±3.1 |  |
1 NIST paint | 75±3.8 |  |
1 Galena | 6±2.3 |  |
8 shooting range soils, US | 83±1 to 100±3 |  |
20 soils from the N-S transect, US (agricultural, grazing land, open range, forested land, residential, desert) | 3.7 to 39 | Â |
70 samples of tap water particles | 1.5 to 100 | Â |
9 soils from mining sites* | 3.1±0.1 to 99.3±14.3 | [86]RIVM (Intestinal) |
1 NIST paint* + soil | 86.2 ± 2.3 |  |
1 Galena* | 1.7 ± 0.2 |  |
15 mining soils, France | 9-75 (Intestinal) | |
10 smelting soils, France | 34-90 (Intestinal) | Â |
27 urban topsoils, France | 11-63 (Intestinal) | Â |
12 soils (mining, composite, phosphate-treated), 1 dust, from various studies (European and North American) | 0.6±0.1 to 112.8±18.5 (Gastric) |  |
 | 0.1±0.1 to 89.5±91.3 (Intestinal) |  |
2 urban residential soils, Australia | 20.0±4.0 to 26.1±6.5 | |
3 domestic incinerator soils, Australia | 11.7±2.8 to 22.5±5.0 |  |
 | 3.2±2.6 to 8.5±0.6†|  |
Brushal, Carl-1, Hamburg, and Oker-11 soils§ | 30.7±6.1 to 62.9±11.0 |  |
9 shooting range soils, Australia | 21.3-102.6 | Â |
 | 59±3.7 to 92±9.0 (3 soils)†|  |
5 historical fill soils, Australia | 5.5-26.1 (4 soils) | Â |
 | 10.7±0.7 to 16.6±1.1 (2 soils)†|  |
13 mining/smelting soils, Australia | 11.6-82.5 | Â |
 | 31±18.4 to 74±17.3 (3 soils)†|  |
1 gasworks, Australia | 27.2 | Â |
 | 27±1.6†|  |
1 geogenic, Australia | 12.5 | Â |