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. 2015 May 22;12(5):5614–5633. doi: 10.3390/ijerph120505614

Table 5.

Dietary arsenic intake a from water (μg·day−1) and food (μg·day−1, ww), along with t-As in urine (ng·mL−1) for each interviewee.

Interviewee As intake in drinking water b (μg·day−1) i-As intake in food (μg·day−1) Total i-As intake (drinking water+food) (μg·day−1) Percentage of drinking water support (%) t-As in urine c (ng·mL−1)
1 125 56.0 181.0 69.1 78
2 396 140.0 536.0 73.9 153
3 351 231.0 582.0 60.3 416
4 311 115.7 426.7 72.9 111
5 513 124.6 637.6 80.5 459
6 378 330.6 708.6 53.3 256
7 290 121.0 411.0 70.6 365
8 260 23.2 283.2 91.8 149
9 440 930.1 1370.1 32.1 292
10 380 901.6 1281.6 29.7 116
11 312 194.4 506.4 61.6 112
12 350 954.5 1304.5 26.8 272
13 299 340.2 639.2 46.8 105
14 396 140.0 536.0 73.9 122
15 267 92.8 359.8 74.2 84
16 504 358.4 862.4 58.4 294
17 378 51.3 429.3 88.1 176
18 416 32.0 448.0 92.9 85
19 265 129.6 394.6 67.2 387
20 550 119.0 669.0 82.2 347
Range 125–550 23.2–954.5 181–1370 26.8–92.9 78–459
Mean ± SD 359.1 ± 100 269.3 ± 300.3 628.4 ± 335.4 65.3 ± 19.5 219 ± 125.8
Median 364.5 134.8 536.0 68.2 164.5

Notes: a daily intake reference value for i-As: 149.8 µg i-As day−1 for > 20 age group; b including hot beverages, soup and juice: c t-As in urine (ng·mL−1) which include inorganic arsenic (AsIII + AsV) and organoarsenicals Controls: 24 ± 12.8 (n = 3).