Skip to main content
. 2005 Aug 17;113(12):1735–1740. doi: 10.1289/ehp.8178

Table 6.

Speciated urinary arsenic and soil arsenic levels for young children at various sites.

Speciated urinary arsenic concentration (μg/L)
Soil arsenic concentration (mg/kg)
n GM (GSD) Range n GM (GSD) Range
Middleport, NY, 2003 77 4.0 (2.2)
5.3 ± 3.0a
0.89–17.7 29 19.9 (1.6)
22.5 ± 11.7a
10.4–58.8
Bingham Creek, UT (UCDEH 1997)
Residences near Bingham Creek channel 696 5.86 (1.96) ND–35 1,045 27 (1.8) 4–623
Ruston/North Tacoma, WA, 1985–1986 (Polissar et al. 1987)
 < 0.5 miles from smelter 118 52.1 (42.5)b NR 45 352 (410)b 12–2,069
 0.5–1.2 miles from smelter 97 22.5 (29.3)b NR 40 125 (109)b 9–1,322
 1.5–8.5 miles from smelter 49 13.7 (10.3)b NR 34 29.6 (49)b 2–290
 Reference site (Bellingham, WA) 4 13.3 (3.3)b NR 10 6.6 (2.7)b 2–10
 > 100 miles from smelter
Ruston/North Tacoma, WA, 1987 (TPCHD 1988)
 < 0.5 miles from smelter 88 16.2 (16) NR NR NR NR
Anaconda, MT (Hwang et al. 1997a, 1997b)
 Close to smelter 177 9.5 (1.7) NR–16.4 876 286c NR
 Intermediate 62 7.5 (1.5) NR–19.0 405 150c NR
 Remote 42 7.1 (1.8) NR–12.1 302 90c NR

Abbreviations: ND, not detected; NR, not reported.

a

Arithmetic average ± SD.

b

Arithmetic averages were reported for urine and soil. Urine values are the weighted arithmetic average from separate results for male and female.

c

Average yard soil arsenic concentrations for Anaconda are the GM calculated as the weighted average of all soil samples.