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Comparison on responses of black soil microorganisms to exogenous carbon and nitrogen addition under no-tillage with straw mulching and combined application of organic and inorganic fertilizers
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Taoyi REN1, Xueru HUANG1, 2, *, Haolin SUN1, Hongtu XIE3, Zhongjun JIA2, Jingkuan WANG1, *
Acta Microbiologica Sinica | 2025, 65(8) : 3348 - 3364
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Acta Microbiologica Sinica | 2025, 65(8): 3348-3364
Microbiome in Black Soils
Comparison on responses of black soil microorganisms to exogenous carbon and nitrogen addition under no-tillage with straw mulching and combined application of organic and inorganic fertilizers
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Taoyi REN1, Xueru HUANG1, 2, *, Haolin SUN1, Hongtu XIE3, Zhongjun JIA2, Jingkuan WANG1, *
Affiliations
  • 1.College of Land and Environment, Shenyang Agricultural University, Shenyang, Liaoning, China
  • 2.State Key Laboratory of Black Soils Conservation and Utilization, Northeast Institute of Geography and Agroecology, Chinese Academy of Sciences, Changchun, Jilin, China
  • 3.Institute of Applied Ecology, Chinese Academy of Sciences, Shenyang, Liaoning, China
Published: 2025-08-04 doi: 10.13343/j.cnki.wsxb.20250145
Outline
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[Objective] Both no-tillage with straw mulching and combined application of organic and inorganic fertilizers can effectively enhance soil fertility. However, the mechanisms by which they influence microbial carbon and nitrogen turnover remain unclear. [Methods] Soil samples included conventional tillage (CK) as the control, along with two management treatments: soils under combined application of organic and inorganic fertilizers (CM) and no-tillage with straw mulching (CT). By employing DNA-stable isotope probing (DNA-SIP) with 13C-glucose in a laboratory microcosm incubation experiment, we investigated the responses of microbial activities in black soil to exogenous glucose and urea addition. Key processes examined included respiration, mineralization, dissimilatory decomposition (measured by 13C-CO2), assimilatory formation of stable organic carbon (measured by 13C-SOC), priming effects, N2O emissions, carbon neutrality, and active microorganisms. [Results] In the control treatment with water addition, soil microbial respiration and mineralization intensity followed the order of CK<CM<CT, which showed the maximum CO2 emission rates of 0.413, 0.589, and 0.615 µmol/(g⋅d), respectively. Exogenous carbon and nitrogen addition induced positive priming effect, with the intensity ranking as simultaneous carbon and nitrogen addition (Glu+N)>carbon-only addition (Glu)>nitrogen-only addition (N). However, the priming effect did not continuously enhance with the increase in the total amount of exogenous organic matter. Dissimilatory decomposition enhanced as the amount of exogenous addition increased, with cumulative 13C-CO2 emissions following the trend of CK (97.0 nmol/g)>CM (90.4 nmol/g)>CT (81.9 nmol/g). The content of stable 13C-SOC produced by microbial assimilation in CT was 296.4 nmol/g, higher than that in CM (263.5 nmol/g). The carbon use efficiency of soil in the three groups was approximately 80%, and about 30% of N2O emissions were offset by the formation of 13C-SOC. Carbon neutrality analysis revealed that the net CO2 emissions from CK and CT soil samples were 50% higher than those from the CM soil sample. Additionally, under the addition of exogenous carbon and nitrogen, the active ammonia-oxidizing microorganisms during microbial proliferation were primarily ammonia-oxidizing bacteria, specifically Nitrosospira. [Conclusion] CT demonstrates higher respiration, mineralization, and carbon sequestration capabilities and lower dissimilatory decomposition capability in enhancing soil fertility than CM, while it results in higher net CO2 emissions.

DNA-SIP  /  organic carbon turnover  /  active microorganisms  /  greenhouse gas  /  carbon neutrality
Taoyi REN, Xueru HUANG, Haolin SUN, Hongtu XIE, Zhongjun JIA, Jingkuan WANG. Comparison on responses of black soil microorganisms to exogenous carbon and nitrogen addition under no-tillage with straw mulching and combined application of organic and inorganic fertilizers[J]. Acta Microbiologica Sinica, 2025 , 65 (8) : 3348 -3364 . DOI: 10.13343/j.cnki.wsxb.20250145
  • National Key Research and Development Program of China(2022YFD1500205-2)
  • National Natural Science Foundation of China(42107317)
Year 2025 volume 65 Issue 8
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Article Info
doi: 10.13343/j.cnki.wsxb.20250145
  • Receive Date:2025-02-26
  • Online Date:2026-02-06
  • Published:2025-08-04
Article Data
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History
  • Received:2025-02-26
  • Accepted:2025-03-21
Funding
National Key Research and Development Program of China(2022YFD1500205-2)
National Natural Science Foundation of China(42107317)
Affiliations
    1.College of Land and Environment, Shenyang Agricultural University, Shenyang, Liaoning, China
    2.State Key Laboratory of Black Soils Conservation and Utilization, Northeast Institute of Geography and Agroecology, Chinese Academy of Sciences, Changchun, Jilin, China
    3.Institute of Applied Ecology, Chinese Academy of Sciences, Shenyang, Liaoning, China

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*E-mail: HUANG Xueru,
WANG Jingkuan,
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表12种不同金属材料的力学参数

Family
属数
Number of
genus
种数
Number of
species
占总种数比例
Percentage of
total species (%)

Genus
种数
Number of
species
占总种数比例
Percentage of total
species (%)
鹅膏菌科Amanitaceae 2 11 5.26 鹅膏菌属 Amanita 10 4.78
小菇科 Mycenaceae 2 12 5.74 丝盖伞属 Inocybe 5 2.39
多孔菌科 Polyporaceae 8 14 6.70 蜡蘑属 Laccaria 5 2.39
红菇科 Russulaceae 3 23 11.00 小皮伞属 Marasmius 6 2.87
小菇属 Mycena 11 5.26
光柄菇属 Pluteus 5 2.39
红菇属 Russula 17 8.13
栓菌属 Trametes 5 2.39
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