Nitrogen addition accelerates litter decomposition and arsenic release of Pteris vittata in arsenic-contaminated soil from mine

被引:1
作者
Wang, Wenjuan [1 ,2 ]
Meng, Dele [1 ,2 ]
Tan, Xiangping [3 ]
Zheng, Mianhai [3 ]
Xiao, Juanjuan [4 ]
Li, Shuoyu [1 ,2 ]
Mo, Qifeng [5 ]
Li, Huashou [1 ,2 ]
机构
[1] South China Agr Univ, Coll Nat Resources & Environm, Guangdong Prov Key Lab Agr & Rural Pollut Abatemen, Guangzhou 510642, Peoples R China
[2] Minist Agr China, Key Lab Agroenvironm Trop, Guangzhou 510642, Peoples R China
[3] Chinese Acad Sci, Key Lab Vegetat Restorat & Management Degraded Eco, South China Bot Garden, Guangzhou 510650, Peoples R China
[4] Chinese Acad Sci, Res Ctr Ecoenvironm Sci, Beijing 100085, Peoples R China
[5] South China Agr Univ, Coll Forestry & Landscape Architecture, Guangzhou 510642, Peoples R China
基金
中国国家自然科学基金;
关键词
Arsenic release; Hyperaccumulator; Litter decomposition; N addition; Enzyme activity; Microbial community; MICROBIAL COMMUNITIES; METAL CONTAMINATION; GLOBAL PATTERNS; FOLIAR LITTER; DEPOSITION; BACTERIAL; NUTRIENT; FUNGAL; PLANTS; CHINA;
D O I
10.1016/j.ecoenv.2024.115959
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
The arsenic (As) release from litter decomposition of As-hyperaccumulator (Pteris vittata L.) in mine areas poses an ecological risk for metal dispersion into the soil. However, the effect of atmospheric nitrogen (N) deposition on the litter decomposition of As-hyperaccumulator in the tailing mine area remains poorly understood. In this study, we conducted a microcosm experiment to investigate the As release during the decomposition of P. vittata litter under four gradients of N addition (0, 5, 10, and 20 mg N g-1). The N10 treatment (10 mg N g-1) enhanced As release from P. vittata litter by 1.2-2.6 folds compared to control. Furthermore, Streptomyces, Pantoea, and Curtobacterium were found to primarily affect the As release during the litter decomposition process. Additionally, N addition decreased the soil pH, subsequently increased the microbial biomass, as well as hydrolase activities (NAG) which regulated N release. Thereby, N addition increased the As release from P. vittata litter and then transferred to the soil. Moreover, this process caused a transformation of non-labile As fractions into labile forms, resulting in an increase of available As concentration by 13.02-20.16% within the soil after a 90-day incubation period. Our findings provide valuable insights into assessing the ecological risk associated with As release from the decomposition of P. vittata litter towards the soil, particularly under elevated atmospheric N deposition.
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页数:11
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