共 90 条
Polylactic acid microplastics induced negative priming and improved carbon sequestration via microbial processes in different paddy soils
被引:10
作者:
Chen, Liying
[1
]
Han, Lanfang
[1
]
Wang, Fayuan
[2
]
Chen, Qi'ang
[1
]
Huang, Hongkai
[1
]
Wang, Jie
[3
]
Ma, Chuanxin
[1
]
Sun, Ke
[4
]
Rillig, Matthias C.
[5
,6
]
Kuzyakov, Yakov
[7
,8
]
Yang, Zhifeng
[1
]
机构:
[1] Guangdong Univ Technol, Guangdong Basic Res Ctr Excellence Ecol Secur & Gr, Sch Ecol Environm & Resources, Guangdong Prov Key Lab Water Qual Improvement & Ec, Guangzhou 510006, Peoples R China
[2] Qingdao Univ Sci & Technol, Coll Environm & Safety Engn, Qingdao 266042, Shandong, Peoples R China
[3] China Agr Univ, Coll Resources & Environm Sci, Beijing Key Lab Farmland Soil Pollut Prevent & Rem, Beijing 100193, Peoples R China
[4] Beijing Normal Univ, Sch Environm, State Key Lab Water Environm Simulat, Beijing 100875, Peoples R China
[5] Free Univ Berlin, Inst Biol, Berlin, Germany
[6] Berlin Brandenburg Inst Adv Biodivers Res BBIB, Berlin, Germany
[7] Univ Gottingen, Dept Soil Sci Temperate Ecosyst, Dept Agr Soil Sci, D-37077 Gottingen, Germany
[8] Peoples Friendship Univ Russia RUDN Univ, Moscow 117198, Russia
基金:
美国国家科学基金会;
中国国家自然科学基金;
关键词:
Biodegradable microplastic;
Stable carbon isotope signature;
Priming effect;
Soil microbial community;
ORGANIC-MATTER;
MECHANISMS;
NITROGEN;
BIOMASS;
PLA;
D O I:
10.1016/j.soilbio.2024.109653
中图分类号:
S15 [土壤学];
学科分类号:
0903 ;
090301 ;
摘要:
Biodegradable microplastics (MPs), which are starting to be used in large quantities in croplands, may affect the mineralization of soil organic carbon (SOC). These priming effects induced by biodegradable MPs are a very new issue, and their mechanisms as well as consequences for various soils are nearly unknown. Using stable carbon isotope signature (delta 13C), we quantified the priming effects by adding corn (C4 plant) -based polylactic acid (PLA, delta 13C = 11.9 parts per thousand) MPs to three paddy soils with solely C3 signature: Ferralsol, Alfisol and Mollisol at two rates (0.5 and 1.0 wt%, based on the mass of MPs). After the incubation (180 days), PLA-MPs reduced the SOC mineralization in all three soils, triggering a negative priming effect. This negative priming effect was strongest in Mollisol (210-220 mg CO2-C kg-1). The net C balance in Mollisol was positive and clearly larger than the C amounts initially added with PLA-MPs to soils, indicating C accrual. The two main mechanisms of the negative priming effects were: i) sorptive protection of SOC and especially of dissolved organic carbon (DOC) by PLA-MPs, and ii) reduction of microbial biomass and fungal diversity after PLA-MPs addition. Additionally, "switching of microbial decomposition from SOC to PLA-MPs" was pronounced in Mollisol, indicated by more PLA-MPs being mineralized. PLA-MPs thus changed the soil C stock and dynamics mediated in part by the changes of microbial biomass, diversity, and community composition, switch of utilization to new resources and decrease of SOC mineralization, all of them leading to C accumulation in soil.
引用
收藏
页数:12
相关论文