Scientia Agricultura Sinica ›› 2025, Vol. 58 ›› Issue (2): 238-251.doi: 10.3864/j.issn.0578-1752.2025.02.003

• TILLAGE & CULTIVATION·PHYSIOLOGY & BIOCHEMISTRY·AGRICULTURE INFORMATION TECHNOLOGY • Previous Articles     Next Articles

The Impact of Diversified Crops and Wheat-Maize Rotations on Soil Quality in the North China Plain

ZHANG SiJia(), YANG Jie, ZHAO Shuai, LI LiWei, WANG GuiYan()   

  1. College of Agronomy, Hebei Agricultural University/State Key Laboratory of North China Crop Improvement and Regulation/Key Laboratory of Water-Saving Agriculture in North China, Ministry of Agriculture and Rural Affairs, Baoding 071000, Hebei
  • Received:2024-08-04 Accepted:2024-11-04 Online:2025-01-21 Published:2025-01-21
  • Contact: WANG GuiYan

Abstract:

【Objective】Based on the long-term experiment in the North China Plain (NCP), the differences in soil nutrient and aggregate nutrient distribution between diversified crops and wheat-maize rotation systems were investigated. Additionally, it provided a comprehensive evaluation of soil quality indices (SQI), offering a scientific basis for enhancing soil quality and productivity in the NCP. 【Method】Four diversified crop rotation systems were evaluated, including spring sweet potato-winter wheat-summer maize (Psw-WM), spring peanut-winter wheat-summer maize (Pns-WM), spring sorghum-winter wheat-summer maize (Ps-WM), with winter wheat-summer maize (WM-WM) serving as the control. The soil samples from the 0-40 cm depth were collected during the second rotation in 2022, at the flowering and harvesting stages of winter wheat. The soil enzymes activities, aggregate stability, organic matter, and concentrations of nitrogen, phosphorus, and potassium in soil and aggregates of different sizes (>2.00 mm, 0.50-2.00 mm, 0.25-0.50 mm, and <0.25 mm) were assessed. The SQI for each crop rotation system was then comprehensively evaluated. 【Result】Compared with WM-WM, the three other crop rotations increased soil inorganic nitrogen content. Psw-WM significantly enhanced organic matter in the 0-20 cm layer, total nitrogen in soil aggregates (>2.00 mm, 0-10 cm), and organic matter in soil aggregates (>2.00 mm and 0.50-2.00 mm, 0-10 cm), which also increased cellulase, catalase, and alkaline protease activities. Pns-WM improved organic matter in the 20-40 cm layer and available potassium in soil aggregates (0.25-0.50 mm and >2.00 mm, 10-20 cm), as well as organic matter in soil aggregates (0-10 cm, >2.00 mm and 10-20 cm, >0.50 mm), which also increased sucrase, urease, and alkaline protease activities. Psw-WM improved the stability of 0-10 cm soil aggregates, while Pns-WM improved the stability of 0-30 cm soil aggregates. Both Pns-WM and Psw-WM significantly improved the SQI, with Pns-WM showing a higher improvement than Psw-WM. The path analysis revealed that the average weight diameter (MWD) of aggregates was a direct and significant affecting SQI. It also had a significant indirect positive effect on SQI by influencing inorganic nitrogen. Additionally, the increased organic matter led to a higher proportion of large aggregates, which significantly affected SQI indirectly. 【Conclusion】Legume (peanut) and root crop (sweet potato) rotations with wheat-maize rotations could significantly improve soil quality and enhance the soil nutrient supply capacity in the NCP.

Key words: North China Plain, diversified crop rotation, soil aggregate, soil quality index, soil nutrient distribution, wheat, maize

Fig. 1

Average daily, daily maximum, daily minimum temperature and daily rainfall from 2018 to 2022"

Fig. 2

Soil nutrient content in different crop rotation systems"

Fig. 3

Soil enzyme activity in different crop rotation systems"

Table 1

Stability characteristics of soil aggregates in different crop rotation systems"

土层
Soil layer (cm)
轮作模式
Crop rotation pattern
平均质量直径
Mean weight diameter
(MWD) (mm)
几何平均直径
Geometric mean diameter
(GMD) (mm)
>0.25 mm粒级团聚体质量百分数
Mass percentage of aggregates
>0.25 mm (R>0.25) (%)
0—10 WM-WM 1.108±0.001c 0.836±0.002c 85.670±0.317b
Psw-WM 1.168±0.011b 0.894±0.012b 91.237±0.351a
Pns-WM 1.202±0.015a 0.952±0.014a 86.732±0.247b
Ps-WM 1.077±0.008c 0.802±0.010d 76.080±0.984c
10—20 WM-WM 1.174±0.004b 0.905±0.004b 86.396±0.082a
Psw-WM 1.216±0.017ab 0.943±0.019ab 82.934±0.378b
Pns-WM 1.249±0.027a 1.009±0.035a 86.757±1.354a
Ps-WM 1.269±0.009a 0.991±0.012a 83.689±0.755b
20—30 WM-WM 1.249±0.005bc 0.982±0.006bc 83.151±0.379c
Psw-WM 1.282±0.006ab 1.011±0.007ab 86.197±0.398b
Pns-WM 1.306±0.021a 1.050±0.025a 88.757±0.849a
Ps-WM 1.237±0.008c 0.963±0.007c 83.689±0.501c
30—40 WM-WM 1.204±0.012c 0.931±0.016c 85.872±1.093b
Psw-WM 1.248±0.004b 0.980±0.004b 91.957±0.266a
Pns-WM 1.200±0.015c 0.934±0.021c 86.121±1.278b
Ps-WM 1.308±0.006a 1.027±0.007a 85.903±0.212b

Fig. 4

Soil aggregate nutrient content in different crop rotations systems"

Fig. 5

Soil quality index (a) for each crop rotations and responses of soil biochemical properties to different crop rotation systems (b)"

Fig. 6

Structural equation model of soil physicochemical properties and soil quality indexes"

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