Quantitative analysis of ecological risk and human health risk of potentially toxic elements in farmland soil using the PMF model

Potentially toxic element (PTE) pollution in farmland soil is a global problem. It is vital to clarify the contributions of farmland soil PTE from different sources to potential ecological risk (PER) and human health risks (HHR), but the existing research methods were incomplete. This study explored...

Full description

Bibliographic Details
Main Authors: Cai, L.-M (Author), Chen, L.-G (Author), Hu, G.-C (Author), Huang, C.-C (Author), Jie, L. (Author), Mei, J.-X (Author), Wang, H.-Z (Author), Wen, H.-H (Author), Xu, X.-B (Author), Xu, Y.-H (Author)
Format: Article
Language:English
Published: John Wiley and Sons Ltd 2022
Subjects:
Online Access:View Fulltext in Publisher
LEADER 03240nam a2200505Ia 4500
001 10.1002-ldr.4277
008 220510s2022 CNT 000 0 und d
020 |a 10853278 (ISSN) 
245 1 0 |a Quantitative analysis of ecological risk and human health risk of potentially toxic elements in farmland soil using the PMF model 
260 0 |b John Wiley and Sons Ltd  |c 2022 
856 |z View Fulltext in Publisher  |u https://doi.org/10.1002/ldr.4277 
520 3 |a Potentially toxic element (PTE) pollution in farmland soil is a global problem. It is vital to clarify the contributions of farmland soil PTE from different sources to potential ecological risk (PER) and human health risks (HHR), but the existing research methods were incomplete. This study explored a comprehensive scheme that combined source contribution and risk assessment to quantitatively assess PER, HHR and the priority pollution sources. enrichment factor (EF) and pollution load index (PLI) were utilized to estimate the features of enrichment and contamination of PTE in farmland soil. Furthermore, spatial distribution characteristics of PTE and positive matrix factorization (PMF) were combined to distinguish and ascertain the sources of PTE, and the PER and HHR model based on PMF were applied to evaluate the ecological and human health risks in different sources. Taking Puning District as an example, four sources of farmland soil PTE were quantitatively allocated. For ecological risk, the study area was at moderate ecological hazard, with industrial activities (53.67%) contributing the most. The mean of Hg was 69.82, reaching medium ecological risk. For human health risks, both adults and children had no non-carcinogenic risk in the study area, and the natural source was the greatest contributor, followed by agricultural activities. The total carcinogenic risk index (TCRI) values for adults and children were 1.40E-05 and 2.75E-05, respectively, showing no significant carcinogenic risk. Furthermore, compared with adults, the health risks of children, whether non-carcinogenic or carcinogenic, were higher than those of adults. © 2022 John Wiley & Sons, Ltd. 
650 0 4 |a Carcinogenic risk 
650 0 4 |a Ecological risks 
650 0 4 |a Factorization 
650 0 4 |a farmland soil 
650 0 4 |a Farmland soils 
650 0 4 |a Farms 
650 0 4 |a Health 
650 0 4 |a Health risks 
650 0 4 |a Human health risks 
650 0 4 |a Positive Matrix Factorization 
650 0 4 |a Potential ecological risk 
650 0 4 |a potentially toxic element 
650 0 4 |a Potentially toxic elements 
650 0 4 |a Priority source 
650 0 4 |a priority sources 
650 0 4 |a Risk assessment 
650 0 4 |a risk evaluation 
650 0 4 |a Risk evaluation 
650 0 4 |a Soil pollution 
650 0 4 |a Soils 
650 0 4 |a source apportionment 
650 0 4 |a Source apportionment 
700 1 |a Cai, L.-M.  |e author 
700 1 |a Chen, L.-G.  |e author 
700 1 |a Hu, G.-C.  |e author 
700 1 |a Huang, C.-C.  |e author 
700 1 |a Jie, L.  |e author 
700 1 |a Mei, J.-X.  |e author 
700 1 |a Wang, H.-Z.  |e author 
700 1 |a Wen, H.-H.  |e author 
700 1 |a Xu, X.-B.  |e author 
700 1 |a Xu, Y.-H.  |e author 
773 |t Land Degradation and Development