Table 2.
Place | Pb | Cd | Cr | Mn | Times Samples collected | Unit | Reference |
---|---|---|---|---|---|---|---|
Soil | |||||||
Guiyu Environ: | |||||||
Mean | 448.73* | 0.71* | 63.90 | 806.54 | Repeated sampling (4 seasons) | mg/kg | This study |
Geo mean | 213.407 | 0.319 | 38.513 | 606.17 | ” | ||
Haojiang Environ: | |||||||
Mean | 101.19 | 0.12 | 41.74 | 704.06 | Repeated sampling (4 seasons) | mg/kg | This study |
Geo Mean | 91.734 | 0.074 | 31.730 | 613.03 | ” | ||
Manila, Philippines Soil from e-waste (outside) | 250 | - | - | - | once | μg/g wet | Fujimori and Takigami (2013) |
Manila, Philippines Soil e-waste | 7.57 | 0.039 | - | - | mg/kg | Fujimori et al. (2012) | |
Guiyu: Soil from e-waste area | 1431 | 31.96 | 153.6 | 374.1 | once | mg/kg dw | Alabi et al. (2012) |
Burnt plastic dump area Guiyu | 104 | 1.7 | 28.6 | - | once | mg/kg dw | Leung et al. (2006) |
Printer roller dump area Guiyu | 190 | 3.1 | 74.9 | - | once | mg/kg dw | Leung et al. (2006) |
Taizhou: Soil from e-waste area | 124.74 | 0.90 | 25.64 | - | once | mg/kg dw | Zhou et al. (2012) |
Guiyu soil (abandoned area) | 150 | 1.21 | 2600 | 300 | Once | mg/kg | Li et al. (2011) |
Guiyu soil residue from open burning | 480 | 10.02 | 320 | 500 | Once | mg/kg | Li et al (2011) |
* E-waste recycling area in slum in Bangal ore, India (BES) | 297 | 2.33 | 73 | 449 | Once | μg/g | Ha et al. (2009) |
* E-waste recycling facility in Bangalore, India (BEF) | 126 | 0.478 | 54 | 619 | Once | μg/g | Ha et al. (2009) |
Area near the open-burning area of e-waste in Guiyu, China | 97.8–123 | ND | 7.02–155 | - | μg/g | Wong et al. (2007) | |
Area at the open-burning area of e-waste in Guiyu, China | 856–7038 | 5.51–42.9 | 137–477 | - | μg/g | Wong et al.(2007) | |
Road dust | |||||||
Guiyu | |||||||
Mean | 589.74* | 1.94* | 69.71 | 693.74 | Repeated sampling (4 seasons) | mg/kg | This study |
Geo Mean | 391.955 | 1.134 | 55.410 | 528.64 | |||
Haojiang | |||||||
Mean | 115.61 | 1.23 | 85.38 | 552.48 | Repeated sampling (4 seasons) | mg/kg | This study |
Geo Mean | 95.481 | 0.356 | 64.908 | 490.42 | |||
Around Manila, Philippines | 6.44 | 0.044 | - | - | Once | Fujimori et al.(2012) | |
E-waste - indoor dust | 1467 | 59.0 | - | - | Once | mg/kg | Zheng J et al. (2013) |
E-waste - outdoor dust | 4489 | 120. | - | - | Once | mg/kg | Zheng J et al.(2013) |
E-waste PCB baking workshop dust; Guiyu | 1910 | 2.4 | 67 | 761 | Once | mg/kg | Zhu et al. (2012) |
E-waste plastic processing workshop dust; Guiyu | 323 | 1.7 | 56 | 800 | once | mg/kg | Zhu et al. (2012) |
Chinaa | SEPA (1995) | ||||||
Grade I (natural background) | 35 | 0.2 | 90 | - | mg/kg | ||
Grade II (agricultural and related use) | 300 | 0.3 | 200 | - | |||
Grade III (industrial activity) | 500 | 1 | 300 | - | |||
Dutch standard optimum | 85 | 0.8 | 100 | - | mg/kg | VROM (1994) | |
Action | 530 | 12 | 380 | - |
Reported values for authors are mean except Ha et al. (2009) which is geometric mean
T-test analysis with log transformed values to compare exposed area and reference area (P<0.05; two tailed)
Standard Reference in China