Scientia Agricultura Sinica ›› 2025, Vol. 58 ›› Issue (20): 4216-4230.doi: 10.3864/j.issn.0578-1752.2025.20.014

• ECOLOGICAL UTILIZATION OF SALINE-ALKALI LAND • Previous Articles     Next Articles

Synergistic Effects of Post-Wheat Green Manure Rotation and Nitrogen Reduction in Saline-Alkali Soil on Wheat Yield, Environmental Footprint, and Economic Benefit

ZHANG MengXuan1(), CHANG FangDi1, WEI HeYa1, LI XiaoHong2, WU LinMei2, ZHANG HongYuan1,3()   

  1. 1 State Key Laboratory of Efficient Utilization of Arid and Semi-Arid Arable Land in Northern China (Institute of Agricultural Resources and Regional Planning, Chinese Academy of Agricultural Sciences), Beijing 100081
    2 Bayannur Academy of Agricultural and Animal Husbandry Sciences, Bayannur 015000, Inner Mongolia
    3 National Center of Technology Innovation for Comprehensive Utilization of Saline-Alkali Land, Dongying 257347, Shandong
  • Received:2025-07-14 Accepted:2025-09-24 Online:2025-10-16 Published:2025-10-14
  • Contact: ZHANG HongYuan

Abstract:

【Objective】 This study aimed to investigate the impacts of post-wheat green manure rotation combined with nitrogen reduction on wheat yield, carbon and nitrogen footprints, and environmental-economic benefits in saline-alkali lands. It sought to drive the transition of agriculture in ecologically fragile regions from a "yield-oriented" model toward the coordinated achievement of three-dimensional goals-"resource conservation, environmental friendliness, and rational economic benefits", so as to provide a scientific basis and practical pathway for regional agricultural green transformation and efficient utilization of saline-alkali soils. 【Method】 A split-plot field experiment was conducted at the Yuanziqiao Experimental base of Bayannur Academy of Agricultural and Animal Sciences in the Hetao Irrigation District, Inner Mongolia. Main plots included green manure incorporation methods: green manure root stubble retention only (GMR) and full biomass incorporation (GMRS), while subplots comprised three nitrogen (N) application levels during the spring wheat season: conventional N (200 kg N·hm-2, N100), 10% N reduction (180 kg N·hm-2, N90), and 20% N reduction (160 kg N·hm-2, N80), and a control with post-wheat fallow (CK) was established, totaling seven treatments. 【Result】 Compared with CK, green manure incorporation (GMR and GMRS) under reduced N regimes increased wheat yield by 6.2%-23.5%. The range of carbon and nitrogen footprints of wheat production under green manure rotation was 0.23-0.52 kg CO2 eq·kg-1 and 4.53-7.89 g N·kg-1, respectively. Green manure treatments reduced carbon and nitrogen footprints by 13.0%-54.6% and 27.3%-47.6% relative to CK, respectively. The environmental damage cost under CK (caused by GHG emissions and reactive nitrogen losses) peaked at 5 053 CNY. Under N100, N90, and N80 regimes, GMRS increased damage costs by 5.0%, 7.7%, and 10.6% compared with GMR, respectively. Human health damage accounted for the largest proportion (47.1%-52.1%) of total costs. GMR significantly enhanced net ecosystem economic benefits by 6 742, 5 301, and 8 567 CNY (increases of 24.2%, 20.9%, and 35.9%) over GMRS, respectively, demonstrating superior economic-ecological synergies. 【Conclusion】 The post-wheat green manure system exhibited significant potential for environmentally friendly agriculture in saline-alkali ecosystems. Implementing “green manure incorporation + reduced N management,” particularly root stubble retention (GMR), ensures wheat yield, mitigated GHG and reactive nitrogen losses, increased economic returns, and provided a practical pathway toward sustainable intensification in ecologically vulnerable regions.

Key words: saline-alkali soil, wheat-green manure rotation, nitrogen reduction, wheat yield, carbon and nitrogen footprints, environmental-economic benefits, stubble retention

Fig. 1

Cumulative emissions of N2O and CH4 under different green manure incorporation methods combined with nitrogen application levels in 2022-2024"

Table 1

Soil organic carbon (SOC) content under different green manure incorporation methods combined with nitrogen application levels"

CK GMR GMRS
N100 N90 N80 N100 N90 N80
SOC (g·kg-1) 9.5±0.20e 10.6±0.15b 10.7±0.15b 11.2±0.20a 10.1±0.15cd 9.9±0.15d 10.2±0.55c

Table 2

The damage costs of reactive nitrogen (Nr) and greenhouse emissions (GHG) to the ecosystems, human health and climate warming"

指标
Items
生态系统
Ecosystems
人体健康
Human health
气候变化
Climate change
参考文献
References
氨挥发 NH3 volatilization (yuan/kg N) 13.2 24.3 / [21-22]
氧化亚氮排放 N2O emission (yuan/kg N) / 2.1 81.6 [22]
硝态氮淋溶 Nitrate nitrogen leaching (yuan/kg N) 7.9 1.4 / [19,21,23]
温室气体排放 GHG emission (yuan/ t CO2 eq) / / 83.4 [20]

Fig. 2

Effects of different green manure incorporation methods combined with nitrogen application levels on wheat yield Capital and lowercase letters indicate significant differences (P<0.05) between different green manure return strategies, and between different fertilization levels within the same green manure return strategy, respectively. The same as Fig. 3"

Fig. 3

Carbon and nitrogen footprints of wheat production under different green manure incorporation methods combined with nitrogen application levels"

Fig. 4

The damage costs of wheat production under different green manure incorporation methods and nitrogen application rates Lowercase letters indicate significant differences (P<0.05) between different fertilization levels within the same green manure return strategy"

Table 3

Net ecosystem economic benefit of wheat production under different green manure incorporation methods and nitrogen application levels"

处理
Treatments
投入成本 Input costs (×104 yuan) 产值 Value (×104 yuan) 损害成本
Damage cost
(×104 yuan)
NEEB
(×104 yuan)
小麦种子
Wheat
seed
绿肥种子
Green manure seed
氮肥
Nitrogen
fertilizer
磷肥Phosphate fertilizer 柴油
Diesel
人工
Labor
小麦
Wheat
绿肥
Green
manure
CK 0.19 0.00 0.10 0.11 0.00 0.29 3.63±0.05B 0.00 0.51 2.43±0.06B
GMR+N100 0.19 0.15 0.13 0.16 0.02 0.44 4.48±0.09Aa 0.56 0.48 3.46±0.09Aa
GMR+N90 0.19 0.15 0.11 0.16 0.02 0.44 4.01±0.05Ab 0.56 0.42 3.07±0.05Ab
GMR+N80 0.19 0.15 0.09 0.16 0.02 0.44 4.12±0.15Ab 0.55 0.36 3.25±0.15Aab
GMRS+N100 0.19 0.15 0.13 0.16 0.02 0.44 4.38±0.11Aa 0.00 0.50 2.78±0.11Ba
GMRS+N90 0.19 0.15 0.11 0.16 0.02 0.44 4.07±0.05Ab 0.00 0.46 2.54±0.05Bb
GMRS+N80 0.19 0.15 0.09 0.16 0.02 0.44 3.85±0.05Ac 0.00 0.40 2.39±0.05Bb

Table 4

Comparison of wheat carbon footprints across different regions"

研究区域
Study area
系统边界
System boundary
小麦碳足迹
Carbon footprint of
wheat (kg CO2 eq·kg-1)
参考文献References
中国 China 从农业投入品生产运输到小麦收获运输阶段,包括土壤固碳
From the production and transportation of agricultural inputs to the harvesting and transportation of wheat, including soil carbon sequestration
0.50 [39]
中国 China 从农业投入品生产运输到小麦收获运输阶段,不包括土壤固碳
From the production and transportation of agricultural inputs to the harvesting and transportation of wheat, excluding soil carbon sequestration
0.51 [42]
中国东部
Eastern China
小麦播种到收获运输阶段
From wheat sowing to harvesting and transportation
0.66 [43]
中国 China 小麦播种到收获运输阶段 From wheat sowing to harvesting and transportation 0.45 [38]
全球 Global / 0.58 [44]
意大利 Italy 从农业投入品生产运输到小麦收获阶段,不包括土壤固碳
From the production and transportation of agricultural inputs to the harvesting of wheat, excluding soil carbon sequestration
0.48 [45]
内蒙古
Inner Mongolia
从农业投入品生产运输到小麦收获运输阶段,包括土壤固碳
From the production and transportation of agricultural inputs to the harvesting and transportation of wheat, including soil carbon sequestration
0.85 [39]
河北 Hebei 从农业投入品生产运输到小麦收获运输阶段,不包括土壤固碳
From the production and transportation of agricultural inputs to the harvesting and transportation of wheat, excluding soil carbon sequestration
0.52 [46]

Fig. 5

Effects of post-wheat green manure cultivation on net ecosystem economic benefit (NEEB)"

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