Scientia Agricultura Sinica ›› 2024, Vol. 57 ›› Issue (24): 4907-4918.doi: 10.3864/j.issn.0578-1752.2024.24.007

• SOIL & FERTILIZER·WATER-SAVING IRRIGATION·AGROECOLOGY & ENVIRONMENT • Previous Articles     Next Articles

Effects of Long-Term Fertilization on Nitrogen Surplus and Deficit and Soil Alkali-Hydrolyzed Nitrogen in Red Soil Double-Cropping Rice System

HU DanDan1(), SONG HuiJie1, DUAN YingHua2, WU Yan1, HU ZhiHhua1, XU XiaoLin1, ZHANG WenJu2, HE XiaoLin3, LIU KaiLou1(), SU Peng4, HUANG QunZhao5   

  1. 1 Jiangxi Institute of Red Soil and Germplasm Resources/Key Laboratory of Acidified Soil Amelioration and Utilization, Ministry of Agriculture and Rural Affairs, Nanchang 331717
    2 Institute of Agricultural Resources and Regional Planning, Chinese Academy of Agricultural Sciences, Beijing 100081
    3 Jiangxi Agricultural Technology Extension Center, Nanchang 330046
    4 Shangrao Agricultural, Forestry and Water Science Research Center, Shangrao 334000, Jiangxi
    5 Meizhou Agricultural Comprehensive Service Center, Meizhou 514000, Guangdong
  • Received:2023-12-28 Accepted:2024-02-27 Online:2024-12-16 Published:2024-12-23
  • Contact: LIU KaiLou

Abstract:

【Objective】The analysis of rice yield, nitrogen use efficiency and the quantitative relationship between apparent nitrogen balance and soil alkali-hydrolyzed nitrogen under different nitrogen fertilizer management conditions could provide a more comprehensive understanding of the effects of long-term fertilization on soil fertility, so as to provide the theoretical guidance for efficient production and scientific nitrogen management of red soil paddy fields. 【Method】Based on the red soil double cropping rice long-term fertilization positioning experiment (started in 1981, located in Jinxian County, Jiangxi Province), five treatments were selected: no fertilizer (CK), nitrogen and phosphorus fertilizer (NP), nitrogen and potassium fertilizer (NK), nitrogen, phosphorus and potassium fertilizer (NPK), nitrogen, phosphorus and organic fertilizer (NPKM), and then the grain and straw yield and nitrogen uptake of rice in each season were investigated and analyzed, and the soil alkali-hydrolyzed nitrogen content was analyzed after late rice. The nitrogen uptake, nitrogen utilization rate, nitrogen apparent balance and the changes of soil alkali-hydrolyzed nitrogen were calculated and analyzed on a 10-year basis. 【Result】During the 40 years of experiment (1981-2020), the rice yield and nitrogen uptake under NPKM treatment were the highest, increased by 65.9%-108.4% and 85.1%-132.5% compared with CK, respectively, and increased by 19.3%-92.1% and 19.4%-99.8% compared with fertilizer treatments (NPK, NK and NP), respectively, showing significant differences. With the increase of the experimental period, the nitrogen use efficiency of fertilizer treatment gradually decreased, and the NPKM treatment also showed a decreasing trend in the first 30 years (1981-2010), but the rate was slower than that of fertilizer treatment, and increased in the recent 10 years (2011-2020), and from the lowest in the first 10 years (1981-1990) to the highest in the recent 10 years, increased by 25.3%-271.2% compared with fertilizer treatment. The nitrogen surplus was the highest under NPKM treatment during the 40 years of experiment, with an increase of 137.1%-577.2% compared with fertilizer treatment, but in the last 30 years (1991-2020), the nitrogen surplus gradually decreased with the increase of the experimental period. The soil alkaline hydrolyzed nitrogen content was the highest under NPKM treatment during the 40 years of experiment, increased by 7.1%-24.4% compared with CK, but the difference was not significant in the first 10 years, and increased by 11.0%-35.2% compared with fertilizer treatment, while there was no significant difference between fertilizer treatment and CK. Correlation analysis showed that the nitrogen surplus was significantly positively correlated with the soil alkaline hydrolyzed nitrogen content in the last 20 years (2001-2020). 【Conclusion】In the red soil double-cropping rice system, with the increase of fertilization years, the combined application of organic and inorganic fertilizers had better effects on rice yield, nitrogen uptake, nitrogen uptake and utilization, and soil alkali-hydrolyzed nitrogen content. Meanwhile, the increase of nitrogen surplus caused by long-term fertilization also further increased the soil alkali-hydrolyzed nitrogen content in the topsoil. The contribution capacity of nitrogen surplus to soil alkali-hydrolyzed nitrogen increased gradually.

Key words: red soil, long-term fertilization, double-cropping rice, apparent nitrogen balance, soil alkali-hydrolyzed nitrogen

Table 1

The annual nutrient input of each treatment (kg·hm-2)"

处理Treatment N P K
CK 0 0 0
NP 180 39 0
NK 180 0 125
NPK 180 39 125
NPKM 393 67 230

Fig. 1

The annual yield of rice under long-term different fertilization patterns Different lowercase letters within each time are significantly different among treatments (P<0.05). The same as below"

Fig. 2

The annual nitrogen uptake of riceunder long-term different fertilization patterns"

Table 2

The annual nitrogen use efficiency of rice in long-term different fertilization patterns (%)"

处理
Treatment
年份 Year
1981-1990 1991-2000 2001-2010 2011-2020
NP 29.14±7.14b 24.69±4.79b 21.09±4.54b 17.36±1.39b
NK 28.67±10.55b 14.23±8.60c 8.85±4.24d 7.06±3.94c
NPK 38.54±7.26a 31.13±6.65a 25.29±4.45a 20.93±5.11ab
NPKM 24.97±4.85b 21.49±5.44b 18.61±3.89c 26.22±2.05a

Table 3

The annual apparent nitrogen balance in long-term different fertilization patterns (kg·hm-2)"

处理
Treatment
年份 Year
1981-1990 1991-2000 2001-2010 2011-2020
CK -78.69±10.34d -69.84±10.71e -85±15.90e -77.78±10.28d
NP 48.86±10.71b 65.71±17.26c 56.08±20.56c 70.98±8.60c
NK 49.71±24.61b 84.55±21.20b 78.12±20.46b 89.51±10.63b
NPK 31.93±12.26c 54.13±21.85d 48.52±20.92d 64.55±11.82c
NPKM 216.25±14.54a 238.77±30.44a 233.99±26.80a 212.25±8.99a

Table 4

Alkali-hydrolyzed nitrogen content of topsoil in long-term different fertilization patterns (mg·kg-1)"

处理
Treatment
年份Year
1981-1990 1991-2000 2001-2010 2011-2020
CK 169.75±19.22ab 174.90±23.07b 182.68±24.95b 221.19±10.24b
NP 157.54±18.07b 160.90±17.62b 190.58±26.72b 218.53±32.88b
NK 159.75±18.17b 163.56±31.53b 187.77±24.37b 223.31±15.95b
NPK 163.80±21.94b 170.96±33.78b 191.25±25.84b 207.36±23.85b
NPKM 181.80±12.02a 217.52±24.50a 222.27±28.71a 258.51±6.83a

Fig. 3

The relationship between nitrogen surplus and alkali-hydrolyzed nitrogen of topsoil"

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