2016
DOI: 10.1016/j.gexplo.2016.05.006
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Potentially hazardous metals contamination in soil-rice system and it's spatial variation in Shengzhou City, China

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Cited by 42 publications
(10 citation statements)
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“…In the sediments, the concentrations of all metals were generally comparable to or higher than those in the AR-areas. The concentrations of Cu, Ni, Pb, and Zn in the vegetable samples were 1–2 orders of magnitude higher than those from the AR-areas, and the contamination of Cd and Cr in the AR-areas were comparable to those in this regulated site [ 72 , 73 , 74 ]. This indicated that the regulated e-waste recycling operations could reduce the release of metals to some extent, although the metal concentrations were still higher than those in the AR-areas.…”
Section: Resultsmentioning
confidence: 82%
See 1 more Smart Citation
“…In the sediments, the concentrations of all metals were generally comparable to or higher than those in the AR-areas. The concentrations of Cu, Ni, Pb, and Zn in the vegetable samples were 1–2 orders of magnitude higher than those from the AR-areas, and the contamination of Cd and Cr in the AR-areas were comparable to those in this regulated site [ 72 , 73 , 74 ]. This indicated that the regulated e-waste recycling operations could reduce the release of metals to some extent, although the metal concentrations were still higher than those in the AR-areas.…”
Section: Resultsmentioning
confidence: 82%
“…The following are available online, Sample preparation, Instrumental Analysis, Geoaccumulation index, Table S1: Exposure factors and values used in the non-carcinogenic risk estimation, Table S2: Reference dose of different exposure routes and skin absorption factors, Table S3: Polybrominated diphenyl ether concentrations in soils from the regulated e-waste recycling area and from other areas, Table S4: Polybrominated diphenyl ether concentrations in sediments from the regulated e-waste recycling area and from other areas, Table S5: Polybrominated diphenyl ether concentrations in vegetables from the regulated e-waste recycling area and from other areas, Table S6, Mean metal concentrations in soils from the regulated e-waste recycling area and from other areas, Table S7: Mean metal concentrations in sediments from the regulated e-waste recycling area and from other areas, Table S8: Mean metal concentrations in vegetables from the regulated e-waste recycling area and from other area, Table S9: Non-carcinogenic risks for individual polybrominated diphenyl ethers in soils, Figure S1: Map of the soil, sediment, vegetable sampling sites, Figure S2: Box plots of the geoaccumulation index for heavy metals in soils and sediments. References [ 28 , 36 , 37 , 38 , 39 , 40 , 41 , 42 , 43 , 44 , 45 , 46 , 47 , 48 , 49 , 50 , 51 , 52 , 53 , 56 , 58 , 59 , 60 , 61 , 62 , 63 , 64 , 65 , 66 , 67 , 68 , 69 , 70 , 71 , 72 , 73 , 74 , 80...…”
mentioning
confidence: 99%
“…As variáveis de temperatura e de umidade do ar no horário da manhã apresentaram os maiores graus de dependência espacial, 16% e 0%, respectivamente, com forte dependência espacial, enquanto que no período da tarde houve moderada dependência espacial. Esses resultados podem ser explicados pela minimização das diferenças dos valores meteorológicos das áreas sem vegetação e com vegetação, em função do maior tempo de exposição à insolação no período vespertino, refletindo em uma baixa heterogeneidade espacial do componente estocástico (Li et al, 2013;Gao et al, 2016), o que pode ser confirmado nos gráficos da distribuição do semivariograma (Figura 2). Já o IDT apresentou maior dependência espacial no período matutino.…”
Section: Resultsunclassified
“…; Gao et al. ). We used the Rook contiguity matrix for calculating the weights (order of contiguity = 3).…”
Section: Methodsmentioning
confidence: 98%