共 46 条
Response of soil heavy metal forms and bioavailability to the application of microplastics across five years in different soil types
被引:2
|作者:
Jiang, Wei
[1
,8
]
Wang, ZhenYu
[2
]
Xiao, Haoyan
[4
]
Abou-Elwafa, Salah Fatouh
[5
]
Alshehri, Mohammed Ali
[6
]
Wu, Yusen
[7
]
Yu, Hanxia
[2
,3
]
Tan, Wenbing
[3
]
机构:
[1] Xianghu Lab, Hangzhou 311231, Peoples R China
[2] Guangdong Acad Agr Sci, Key Lab Green Prevent & Control Fruits & Vegetable, Guangdong Prov Key Lab High Technol Plant Protect, Plant Protect Res Inst,Minist Agr & Rural Affairs, Guangzhou 510640, Guangdong, Peoples R China
[3] Chinese Res Inst Environm Sci, State Key Lab Environm Criteria & Risk Assessment, Beijing 100012, Peoples R China
[4] Fujian Normal Univ, Sch Geog Sci, Fuzhou 350007, Peoples R China
[5] Assiut Univ, Fac Agr, Agron Dept, Assiut 71526, Egypt
[6] Univ Tabuk, Fac Sci, Dept Biol, Tabuk 71491, Saudi Arabia
[7] Western Sydney Univ, Sch Nursing & Midwifery, Penrith, NSW 2751, Australia
[8] Nanjing Agr Univ, Coll Agr, Nanjing 210095, Peoples R China
关键词:
Microplastics;
Heavy metal bioavailability;
Chemical speciation of metals;
Different soil types;
Maize;
ADSORPTION;
D O I:
10.1016/j.jhazmat.2024.136068
中图分类号:
X [环境科学、安全科学];
学科分类号:
08 ;
0830 ;
摘要:
Microplastics (MPs) potentially alter physicochemical and transformation of heavy metals (HMs) in soils, which may depend on the specific characteristics of soil types. However, the dynamical and long-term mechanisms remain to be elucidated. A five-year incubation experiment was conducted to evaluate the influence of MPs on the chemical speciation of Pb, Ni, Cu, Cr, Cd, and As in the meadow, tidal, cinnamon, saline-alkali, and brown soils. From the first year to the fifth year, the clay value of the meadow, tidal, cinnamon, and saline-alkali soils was increased by 31.35 %, 9.63 %, 30.12 %, and 33.12 %, respectively; the pH values of the cinnamon and saline-alkali soils were increased by 15.02 % and 15.86 %, respectively. Besides, speciation distribution results suggested that the application of MPs reduced the liable available (LB) form (F2-dissolved and F3-ion exchangeable) of HMs and increased the potentially available (PB) form (F5-minerals and F6-organic-bound fraction) of HMs in all soils. Compared with other forms, F2 HMs fraction was the most responsive to MPs. Furthermore, the average bioconcentration factor (BCF) of Cr and Pb decreased by 73.75 % and 70.41 % in soils, respectively. Interestingly, soil type showed more impact on the form of HMs, which was associated with the different physicochemical parameters of soils, while application time displayed more impact on the bioavailability of HMs. Moreover, our results suggested that soils with higher clay content and pH values (such as cinnamon and saline-alkali soils) may mitigate the bioavailability of HMs more effectively in the presence of MPs, while soils with lower clay content may be more vulnerable to HMs contamination over time. This work highlights the importance of long-term monitoring of the impact of MPs on HMs dynamics for effective mitigation of soil contamination risks. Our study provides valuable guidance for soil remediation strategies and environmental quality management across different soil types.
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页数:12
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