Research article

Effects of nitrogen reduction rates on grain yield and nitrogen utilization in a wheat-maize rotation system in yellow cinnamon soil

  • Received: 31 October 2023 Revised: 04 February 2024 Accepted: 04 February 2024 Published: 28 February 2024
  • Excessive nitrogen (N) fertilizer application severely degrades soil and contaminates the atmosphere and water. A 2-year field experiment was conducted to investigate the effects of different N fertilizer strategies on wheat-summer corn rotation systems in yellow-brown soil areas. The experiment consisted of seven treatments: no N fertilization (CK), conventional fertilization (FP), optimized fertilization (CF), reduced N rates of 10% (90% FP), 20% (80% FP), 30% (70% FP), and a combination of controlled release with conventional urea at 7:3 ratio (CRU). The results indicate that under the condition of 80% FP, both CF and CRU treatments can increase the yield of wheat and corn for two consecutive years. Compared with FP treatment, the wheat yield of CF and CRU treatments increased by 3.62–2.57% and maize yield by 3.53–1.85% with N fertilizer recovery rate (NRE) of crops by 46.2–37.8%. The agronomic N use efficiency (aNUE) under CF treatment increased by 35.4–37.7%, followed by CRU, which increased by 30.5–33.9%. Moreover, compared with FP treatment, both CF and CRU treatment increased the content of organic matter (OM), total N (TN), and hydrolyzed N (HN) in the topsoil layer, and 70% FP treatment significantly reduced the HN content. Both CF and CRU treatments significantly increased the NO3 concentrations in the 0–20 cm soil depth during the wheat and maize season at maturity stages and decreased the residual inorganic N below the plow layer (40–60 cm). During the corn season, the CF and CRU treatments significantly reduced the NO3 concentration in the 40–60 cm soil layer from seedling to jointing. Considering various factors, CRU treatment under 80% FP conditions would be the best fertilization measure for wheat-corn rotation in yellow-brown soil areas.

    Citation: Jun Du, Yi-chang Wei, Muhammad Rizwan Shoukat, Linyi Wu, Ai-ling He, Gao-yuan Liu, Zhong-yi Guo, Yaseen Laghari. Effects of nitrogen reduction rates on grain yield and nitrogen utilization in a wheat-maize rotation system in yellow cinnamon soil[J]. AIMS Agriculture and Food, 2024, 9(1): 317-335. doi: 10.3934/agrfood.2024019

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  • Excessive nitrogen (N) fertilizer application severely degrades soil and contaminates the atmosphere and water. A 2-year field experiment was conducted to investigate the effects of different N fertilizer strategies on wheat-summer corn rotation systems in yellow-brown soil areas. The experiment consisted of seven treatments: no N fertilization (CK), conventional fertilization (FP), optimized fertilization (CF), reduced N rates of 10% (90% FP), 20% (80% FP), 30% (70% FP), and a combination of controlled release with conventional urea at 7:3 ratio (CRU). The results indicate that under the condition of 80% FP, both CF and CRU treatments can increase the yield of wheat and corn for two consecutive years. Compared with FP treatment, the wheat yield of CF and CRU treatments increased by 3.62–2.57% and maize yield by 3.53–1.85% with N fertilizer recovery rate (NRE) of crops by 46.2–37.8%. The agronomic N use efficiency (aNUE) under CF treatment increased by 35.4–37.7%, followed by CRU, which increased by 30.5–33.9%. Moreover, compared with FP treatment, both CF and CRU treatment increased the content of organic matter (OM), total N (TN), and hydrolyzed N (HN) in the topsoil layer, and 70% FP treatment significantly reduced the HN content. Both CF and CRU treatments significantly increased the NO3 concentrations in the 0–20 cm soil depth during the wheat and maize season at maturity stages and decreased the residual inorganic N below the plow layer (40–60 cm). During the corn season, the CF and CRU treatments significantly reduced the NO3 concentration in the 40–60 cm soil layer from seedling to jointing. Considering various factors, CRU treatment under 80% FP conditions would be the best fertilization measure for wheat-corn rotation in yellow-brown soil areas.



    The nitrogen (N) fertilizer management practices are crucially important to increase crop yield while protecting the environment by decreasing losses [1,2,3,4]. Among nutrients, the N contributes the most to increasing grain yield in cereal crops by 40% [5]. The fertilizers used in China since the 1980s have resulted in a nearly 85% increase in grain yield. However, the amount of fertilizer has increased 4.5 times, far exceeding the rate of grain yield increase [6]. The excessive use of N fertilizer is common; approximately 20% of the area in a wheat-maize rotation suffers from excessive N fertilizer applications [7]. Consequently, over-fertilization resulted in soil compaction, soil acidification, and other types of soil degradation, as well as ecological and environmental problems, such as residual NO3 pollution [8,9]. The loss of N fertilizer in farmland is 40–50% [10,11,12]. Agricultural non-point source pollution caused by fertilizer residue has threatened the sustainable development of agriculture [13,14].

    Appropriate applications of N fertilizer can increase grain yield and N utilization while reducing environmental pollution risks [15,16]. Many studies have investigated the effects of reducing fertilizer use and increasing efficiency on grain yield and N utilization. Nie [17] showed that reducing N applications in wheat by 10% or 20% in a vertical rotary tillage system reduced fertilizer waste and increased grain yield without significantly affecting grain quality. Li et al. [18] found that reducing N fertilizer applications by 10% and incorporating straw residue combined with bacterial residue (60 m3/hm2) increased wheat yield and N utilization efficiency, resulting in optimal economic benefits. Xiao et al. [19] found that a 30% reduction in controlled-release N fertilizer increases maize yield and N utilization efficiency. Liu et al. [20] reduced N fertilizer under 40% lower wheat planting density and 42.9% higher maize planting density and recommended fertilizer amount of 180 kg/hm2.

    Most studies on N fertilizer reduction and increased fertilizer efficiency focused on a single crop, with limited research on the annual reduction in N fertilizer use in different crop rotations. The wheat-maize rotation system is the main grain cropping system in Henan Province, with wheat accounting for 27.58% of the total national production and maize accounting for 8.38% [21,22]. High and stable yields of wheat and maize in this region are critical for ensuring national food security. Yellow cinnamon soil is the dominant soil in Henan Province, accounting for 15.38% of the soil in the province's cultivated land [23]. The aim of the study was to assess the potential for N fertilizer reduction in this rotation system and provide guidance for N fertilizer applications to achieve efficient and environmentally friendly production of grain crops and utilize nutrients efficiently while increasing grain yields.

    The field experiment was conducted from October 2018 to October 2020 in Lizhuang Village, Shunhe Office, Yicheng District, Zhumadian City, Henan Province, China (33º01'16" N, 114º 07'27" E), a yellow cinnamon soil region. The soil at the experimental site exhibited the following physicochemical properties: pH value of 5.03, organic matter (OM) content of 22.5 g/kg, total nitrogen (TN) content of 1.31 g/kg, hydro-lytic nitrogen (HN) content of 126 mg/kg, available phosphorus (P) content of 50.1 mg/kg, available potassium (K) content of 114 mg/kg, exchangeable calcium (Ca) content of 8.2 cmol/kg, and exchangeable magnesium (Mg) content of 1.25 cmol/kg.

    The Zhengmai7698 wheat and Zhengdan958 maize varieties were grown under seven different fertilizer management practices: no fertilization (CK); conventional fertilization (FP); optimized fertilization (CF); and 10% (90% FP), 20% (80% FP), and 30% (70% FP) reductions in N fertilizer application rate from conventional amount and made of mixture of urea with a nitrification inhibitor and urea at a ratio of 7:3 (CRU). The fertilizer rates and application methods are listed in Table 1. The urea fertilizers with a nitrification inhibitor (N, 43.6%) were produced by Henan Xinlianxin Fertilizer Co., Ltd. Regular urea (N, 46.0%), superphosphate (P2O5, 44%), and K chloride (K2O, 60%) were purchased from the local agricultural market. In each treatment, the P and K fertilizers were applied as basal fertilizers once for wheat and during the seedling stage for maize. The N fertilizers were applied as basal fertilizers or as top-dressing according to the requirements for wheat during the tillering or elongation stages and for maize during the seedling or tasseling stages. Each treatment was replicated three times in a randomized complete block design (RCBD). Each plot was 10.0 m long and 3.0 m wide, with an area of 30 m2. The row spacing for wheat was 0.2 m, with an interval of 0.6 m between plots. The interval between the rows was 0.4 m for maize, and the plot size was 20 m2. A distance of 1.0 m was left between replications, and protective rows were established around the plots. The sowing rate for wheat was 180.0 kg/hm2, and the planting density for maize was 67,500 plants/hm2. Trained workers carried out all field management practices on the same working day.

    Table 1.  Fertilization and application methods in the wheat-maize crop rotation.
    Treatments Fertilization method Wheat (NPK) Maize (NPK)
    T1 = CK No N fertilizer 0–90–60 0–60–90
    T2 = FP One-time N fertilization 225–90–60 225–60–90
    T3 = CF Recommended fertilization at intervals 180–90–60 180–60–90
    T4 = FP90% Reduced N rate by 10% 202.5–90–60 202.5–60–90
    T5 = FP80% Reduced N rate by 20% 180–90–60 180–60–90
    T6 = FP70% Reduced N rate by 30% 157.5–90–60 157.5–60–90
    T7 = CRU Controlled-release urea mixed with ordinary urea at 7:3 ratio 180–90–60 180–60–90
    Strategy: The ratio of base to top N fertilizer during the wheat period was 6:4, the seedling stage: the trumpet stage during maize period is 4:6 in the treatment (T3); Other test treatments: One-time application of wheat base fertilizer, One-time application in seedling stage of maize.

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    The soil samples from the 0–20 cm plow layer was collected using the Mei flower method before sowing to measure initial soil properties. Samples were air dried, ground, and sieved, and then the pH value and the organic matter, alkaline hydrolysis N, available P, and available K contents were determined. After sowing, soil samples were collected from the 0–20 cm, 20–40 cm, and 40–60 cm layers of each plot during the seedling, elongation, heading, and maturation stages of wheat and the elongation, tasseling, and maturation stages of maize to determine the NO3 content. A portion of the 0–20 cm soil sample was reserved after partial air-drying for laboratory analysis. The 2–3 plant samples were obtained from each plot, and their fresh weight was measured. After drying, their dry weight was measured, and representative samples were reserved for subsequent laboratory analysis. Plant samples were also collected during the maturation stage.

    Representative plants were selected from each plot for conventional yield assessment. After wheat maturity, the number of spikes per plant, number of grains per spike, and thousand–grain weight were statistically analyzed. Before the maize harvest, 10 cobs of each plot were air–dried to a standard moisture content (14%), and the cob length and diameter, length of the tip without kernels, number of rows per cob, and thousand-grain weight were measured. The plot yields were recorded, and the plant and grain samples were preserved for further analysis.

    The soil OM was determined using the potassium dichromate volumetric method with external heating. The TN content was obtained using the Kjeldahl method. The HN was analyzed using the alkaline diffusion method. Soil NO3 concentration was measured by calcium chloride extraction and a flow analyzer. The available P was determined using the Olsen method, and the available K concentration was measured using ammonium acetate extraction with flame photometry. In the case of plant sample analysis, the plant samples were boiled in concentrated sulfuric acid and hydrogen peroxide after pulverization. The TN contents in the straw and seeds were determined with conventional analytical methods. The N fertilizer recovery rate (NRE), agronomic N efficiency (aNUE), and N fertilizer partial productivity (NPFP) of crops were calculated as follows:

    (1)
    (2)
    (3)

    where NRE is N fertilizer recovery rate, %; aNUE is agronomic N efficiency, kg/kg; NPFP is N fertilizer partial productivity, kg/kg; N input is N fertilizer applied in fertilized plot, kg/hm2; Crop N uptakeFertilized plot is Crop N uptake in fertilized plot, kg/hm2; Crop N uptakeNone fertilized plot is Crop N uptake in none fertilized plot, kg/hm2; Crop YieldFertilized plot is Crop yield in fertilized plot, kg/hm2; and Crop YieldNone fertilized plot is Crop yield in none fertilized plot, kg/hm2.

    Soil Analysis of variance (ANOVA) was performed using SPSS 22 to determine the effects of different N fertilizer management practices on wheat and maize yields, NRE, aNUE, NPFP, OM, TN, HN, and soil N distributions at different growth stages. The differences between N fertilizer treatments were detected using Duncan's multiple range test at p < 0.05. The MS Excel 2019 (Microsoft, USA) origin 2023b (Origin Lab, USA) were used to visualize data graphically.

    The wheat yield was lower in 2020 than in the previous year, while the maize yield was higher (Table 2). This result was mainly attributed to the prolonged duration of the spring drought in the local area in 2020 resulting in a water imbalance. However, there was sufficient rainfall in the autumn of 2020. The CF involved a split application of fertilizers for wheat and maize, which significantly increased the yields of both crops. The CF treatment produced the highest annual wheat and maize yields, with 8630 kg/hm2 and 6458 kg/hm2 for wheat and 7835 kg/hm2 and 8555 kg/hm2 for maize. The CRU treatment resulted in slightly lower wheat and maize yields, but there was no significant difference compared to the CF treatment. The wheat yield was 3.62% and 2.57%, respectively, and the maize yield was 3.53% and 1.85% higher in the CF and CRU treatments than in the 80% FP treatment. However, the yield was lower in the 70% FP treatment.

    Table 2.  Wheat-maize crop yield under different treatments.
    Treatments 2018–2019 2019–2020
    wheat(kg/hm2) maize(kg/hm2) wheat(kg/hm2) maize(kg/hm2)
    CK 5103.5c 4427.5d 3927.0c 5247.5c
    FP 8369.0ab 7559.0ab 6203.0ab 8274.0ab
    CF 8630.0a 7835.0a 6458.0a 8555.0a
    90% FP 8465.5a 7484.5ab 6273.5ab 8090.5ab
    80% FP 7649.5b 7074.0b 5879.5ab 7625.5b
    70% FP 6858.5b 6338.5c 5277.5b 6809.0bc
    CRU 8534.0a 7674.0a 6398.0a 8454.0a
    Note: Different lowercase letters in the same column indicate significant differences among treatments at 0.05 level. CK is no fertilization; FP is conventional fertilization; CF is optimized fertilization; 90% FP, 80% FP, and 70% FP are applications of reduced N fertilizer by 10%, 20%, and 30%, respectively. CRU is the application rate from conventional amount and a mixture of urea with a nitrification inhibitor and urea at a ratio of 7:3.

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    The three N reduced treatments (90% FP, 80% FP, and 70% FP) had lower wheat and maize yields than the FP treatment in both years, with the following order: 90% FP > 80% FP > 70% FP. There was no significant difference in the winter wheat yield between the 90% FP and 80% FP treatments and between these two treatments and the FP treatment. However, the winter wheat yield was significantly different between the 70% FP treatment and the FP treatment in the second year. No significant difference in the maize yield was observed between the three N reduction treatments and the FP treatment in the second year, but the yields of the 80% FP and 70% FP treatments were significantly lower than that of the CF treatment. The maize yield of the 70% FP treatment was significantly lower than that of the FP and CF treatments in the first year. However, the 30% reduction resulted in a lower yield. Compared to the FP treatment, the wheat yield was 18.05% and 14.92% lower (average of 16.49%), and the maize yield was 16.15% and 17.71% lower (average of 16.93%) than FP treatment.

    Results showed spikelet number was significantly higher in all fertilizer treatments than CK (Table 3). The three N reduced treatments (90% FP, 80% FP, and 70% FP) exhibited a decreasing trend in the spikelet number. The spikelet number was significantly lower in the 70% FP treatment than FP treatment. It was higher in the CRU treatment, but there was no significant difference compared to the FP treatment. The effective spikelet number and thousand-grain weight were significantly higher in the CF, 90% FP, and CRU treatments than CK, while there was no significant difference in these parameters between the different fertilizer treatments. The maize cob number was significantly higher in all fertilizer treatments than CK. All reduced N fertilizer treatments showed a decrease in cob number. The cob number was significantly lower in the 80% FP, followed by 70% FP treatments than FP treatment. The cob number was higher in the CRU treatment than FP treatment, but there was no significant difference. The hundred-grain weight in the first year was significantly higher in all fertilizer treatments than CK. The hundred-grain weight was significantly lower in the 70% FP treatment than FP treatment, while there was no significant difference between the X treatment and the other fertilizer treatments. In the second year, the hundred-grain weight was significantly higher in the FP, CF, 90% FP, and CRU treatments than CK, whereas there was no significant difference between the 80% FP and 70% FP treatments and the CK.

    Table 3.  Crop yield components in the wheat-maize rotation under different treatments.
    Year Treatments wheat maize
    Effective number of panicles (x 1000 ears/hm2) Grain number per ear (ear) 1000–grain weight (g) Effective number of panicles (x 1000 ears/hm2) Grain number per ear (Grain number/ear) 100–grain weight (g)
    2018–2019 CK 32.4b 30.7c 38.5b 6.695a 267.4c 26.5c
    FP 44.1ab 36.4ab 42.1a 6.735a 410.1a 29.6a
    CF 45.4a 37.6a 42.7a 6.740a 417.8a 30.9a
    90% FP 44.9a 37.2a 42.5a 6.730a 407.0ab 28.9ab
    80% FP 41.7ab 33.1b 40.5ab 6.715a 350.6b 28.4ab
    70% FP 39.7ab 31.8b 39.9ab 6.685a 307.9b 27.9bc
    CRU 44.3a 37.1a 42.3a 6.740a 413.8a 30.2a
    2019–2020 CK 29.6b 22.6c 43.7b 6.575a 304.8c 24.3b
    FP 40.6ab 37.6ab 43.5ab 6.695a 439.8ab 26.5a
    CF 42.4a 39.4a 45.8a 6.695a 453.9a 27.1a
    90% FP 42.0a 38.6a 45.5a 6.720a 435.8ab 26.2a
    80% FP 40.2ab 35.8ab 45.1a 6.705a 397.2b 25.2ab
    70% FP 39.2ab 33.4b 44.0ab 6.690a 357.9b 25.0ab
    CRU 41.8a 38.9a 45.2a 6.735a 454.1a 26.9a
    Note: CK is no fertilization; FP is conventional fertilization; CF is optimized fertilization; 90% FP, 80% FP, and 70% FP are applications of reduced N fertilizer by 10%, 20%, and 30%, respectively. CRU is the application rate from conventional amount and a mixture of urea with a nitrification inhibitor and urea at a ratio of 7:3.

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    The total N uptake in wheat and maize was significantly higher in all N fertilizer treatments than CK in both rotation (Table 4). No significant difference was observed in the total N uptake between all N fertilizer treatments and the FP treatment, except for a higher value in the 70% FP treatment. The three N reduction treatments (90% FP, 80% FP, and 70% FP) exhibited a decreasing trend in total N uptake. The total N uptake in wheat and maize was 18.32% and 16.56% lower (statistically significant) in the 70% FP treatment than FP treatment. The total N uptake in the two rotation years was 7.26% and 3.67% (4.48% and 5.63%) higher in the CF treatment (CRU treatment) than FP treatment.

    Table 4.  Annual N use efficiency of wheat-maize under different treatments.
    Year Treatment N uptake (kg/hm2) NRE (%) aNUE (kg/kg) NPFP (kg/kg)
    2018–2019 CK 165.4 c / / /
    FP 290.4 a 27.8bc 14.22bc 35.40b
    CF 311.5 a 40.6a 19.26a 45.74a
    90% FP 289.6 ab 30.7b 15.85b 39.38b
    80% FP 278.9 ab 31.5b 14.42bc 40.90ab
    70% FP 237.2 b 22.8c 11.64c 41.90ab
    CRU 303.4 a 38.3ab 18.55ab 45.02a
    2019–2020 CK 229.1 c / / /
    FP 343.0 a 25.3bc 11.78bc 32.17b
    CF 355.6 a 35.1ab 16.22a 41.70a
    90% FP 356.5 a 31.5ab 12.81b 35.47b
    80% FP 336.5 a 29.8b 12.03bc 37.51ab
    70% FP 286.2 b 18.1c 9.24c 38.37ab
    CRU 362.3 a 37.0a 15.77ab 41.26a
    Note: CK is no fertilization; FP is conventional fertilization; CF is optimized fertilization; 90% FP, 80% FP, and 70% FP are application of reduced N fertilizer by 10%, 20%, and 30%, respectively. CRU is the application rate from conventional amount and a mixture of urea with a nitrification inhibitor and urea at a ratio of 7:3.

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    The NRE, aNUE, and NPFP rates were higher in the CF and CRU treatments than in FP treatment in both rotation cycles. The NRE was 46.0% and 38.7% (37.8% and 46.2%) higher in the CF treatment (CRU treatment) than FP treatment. The aNUE was 35.4% and 37.7% (30.5% and 33.9%) higher in the CF treatment (CRU treatment) than FP treatment. The NPFP was 29.2% and 29.6% (27.2% and 28.3%) higher in the CF treatment (CRU treatment) than FP treatment. The three N reduced treatments (90% FP, 80% FP, and 70% FP) exhibited a decrease in the NRE and aNUE and an increase in the NPFP. The NPFP rate and aNUE were 18.0% and 28.5% and 18.1% and 21.6% lower in the 70% FP treatment than FP treatment in both rotation cycles, respectively.

    The soil OM content was higher in all N fertilizer treatments than CK during the maturity stage of wheat and maize (Figure 1). Significantly higher soil OM contents of wheat field were observed in the FP, CF, and CRU treatments than CK in both rotation cycles. Also, significantly higher soil OM contents of maize fields were observed in FP, CF, and CRU treatments in the first year and in the FP, CF, 90% FP, and CRU treatments in the second year than CK. However, there was no significant difference in this parameter between different N fertilizer treatments. The soil OM content was higher in the CF and CRU treatments than FP treatment. The OM was 2.87% and 5.64% higher at wheat maturity stage and 8.33% and 1.83% higher at maize stage in the CF treatment than FP treatment in the two rotation cycles, respectively. Whereas, OM was 1.72% and 1.02% higher at wheat maturity and 5.09% and 2.28% higher at maize maturity stage in the CRU treatment than FP treatment in the two rotation cycles, respectively. The three N reduction treatments (90% FP, 80% FP, and 70% FP) exhibited a decrease in the soil OM content during the wheat-maize rotation.

    Figure 1.  Soil organic matter content in the plough layer in different treatments at the maturity stage of wheat-maize. CK is no fertilization; FP is conventional fertilization; CF is optimized fertilization; 90% FP, 80% FP, and 70% FP are application of reduced N fertilizer by 10%, 20%, and 30%, respectively. CRU is the application rate from conventional amount and a mixture of urea with a nitrification inhibitor and urea at a ratio of 7:3.

    Figure 2 shows that the TN content in the soil at maturity stage of wheat in both rotation cycles was slightly higher in all N fertilizer treatments than CK. However, this effect was not significant in all N treatments and in both rotation years. The TN content was significantly lower in the 70% FP treatment than FP treatment, but there was no significant difference in this parameter among the other N fertilizer treatments. The TN content of mature maize in both rotation cycles was higher in all N fertilizer treatments than CK. The CRU treatment resulted in a significantly higher soil TN content than the CK. The TN content at maize maturity stage was 14.77% and 13.48% higher in the CRU treatment than FP treatment in the two rotation cycles, respectively. The three N reduced treatments (90% FP, 80% FP, and 70% FP) exhibited a decrease in the soil TN content during the wheat season but no consistent pattern in the maize season.

    Figure 2.  The total N content in the plough layer soil of different treatments at the maturity stage of wheat-maize. CK is no fertilization; FP is conventional fertilization; CF is optimized fertilization; 90% FP, 80% FP and 70% FP are application of reduced N fertilizer by 10%, 20%, 30%, respectively. CRU is the application rate from conventional amount and a mixture of urea with a nitrification inhibitor and urea at a ratio of 7:3.

    Figure 3 indicates that the treatments substantially affected the aSNC during wheat-maize rotation. The aSNC at the crop maturity stage was higher in all N fertilizer treatments than CK. In the first year of the wheat-maize rotation, the aSNC was significantly higher in the FP, CF, and CRU treatments than CK. In the second year of the wheat-maize rotation, the aSNC was significantly higher in the CF and CRU treatments than CK and FP treatments. On average, aSNC in wheat was 6.40% higher in the CF treatment than CK in both rotation cycles. It was 2.57% and 10.43% higher in maize in the two rotation cycles, respectively. The aSNC in the wheat was 15.29% higher in the CRU treatment than FP treatment. It was 7.85% and 5.45% higher in maize in the two rotation cycles, respectively. The three reduced N treatments (90% FP, 80% FP, and 70% FP) exhibited a decrease in the aSNC during the wheat-maize rotation.

    Figure 3.  The content of hydrolyzed N in tilth soil of different treatments at the maturity stage of wheat-maize. CK is no fertilization; FP is conventional fertilization; CF is optimized fertilization; 90% FP, 80% FP, and 70% FP are application of reduced N fertilizer by 10%, 20%, and 30%, respectively. CRU is the application rate from conventional amount and a mixture of urea with a nitrification inhibitor and urea at a ratio of 7:3.

    The NO3 distributions in different soil depths at different growth stages of wheat and maize are visualized in Table 5 and Table 6. The Tables show that the NO3 concentration was low in the CK in different soil layers during the wheat and maize seasons in different growth stages. The NO3 concentration was higher in all N fertilizer treatments than CK in different soil layers.

    Table 5.  NO3 concentration in the soil profile during the wheat growth period in two cropping systems.
    Treatments Layers (cm) 2018–2019
    NO3 concentration (mg/kg)
    2019–2020
    NO3 concentration (mg/kg)
    Seedling stage Jointing stage Heading date Maturity Seedling stage Jointing stage Heading date Maturity
    CK 0–20 6.48c 6.01c 3.93c 2.39d 6.92d 5.69b 3.30c 3.21d
    20–40 5.19c 4.63c 1.18c 0.40c 4.05d 3.67ab 1.78c 2.40c
    40–60 4.30c 3.97d 0.57c 0.19c 3.76c 2.14ab 0.20d 0.72c
    FP 0–20 29.69a 11.84b 8.31b 10.46b 37.83a 6.62b 7.37ab 11.86b
    20–40 26.16a 9.36ab 5.52a 5.07a 11.21b 4.01a 6.63a 7.77a
    40–60 11.21a 7.75ab 4.54a 1.74a 10.06a 3.34a 2.92a 2.01a
    CF 0–20 18.59b 18.15a 10.54a 22.03a 10.43c 9.60a 8.91a 17.98a
    20–40 14.21b 5.91bc 3.01bc 4.24ab 7.45c 3.53ab 5.87a 4.31b
    40–60 5.79c 5.43c 1.65b 1.75a 4.39c 1.34bc 1.72b 1.60ab
    90% FP 0–20 26.34a 13.15b 6.33b 4.48c 30.33b 6.59b 8.36a 7.65c
    20–40 14.06b 10.60a 3.36b 2.15b 13.59ab 2.93b 5.79a 2.15c
    40–60 8.35ab 9.58a 1.46b 1.86a 5.12b 1.33bc 1.08c 1.74a
    80% FP 0–20 24.10ab 9.77b 4.16c 6.01c 30.49b 3.85c 7.93a 7.24c
    20–40 22.99a 6.75bc 2.19bc 3.48b 12.22ab 2.36b 4.71b 2.59c
    40–60 9.15ab 4.94cd 1.27b 1.52ab 6.04b 1.63b 1.49bc 1.83a
    70% FP 0–20 26.63a 10.48b 3.47c 7.79bc 29.35b 5.79b 5.68b 7.70c
    20–40 21.68a 9.32ab 1.37c 5.28a 15.04a 2.06b 2.70c 1.84c
    40–60 7.30b 6.61bc 1.21b 1.81a 6.92b 1.37bc 1.72b 1.29b
    CRU 0–20 17.21b 16.45ab 9.38ab 17.78a 11.51c 8.36ab 7.90a 15.42a
    20–40 13.61b 7.02b 2.80bc 5.26a 10.30b 3.38ab 5.68ab 6.07a
    40–60 6.33bc 5.38c 1.15b 1.27b 4.73c 1.05c 1.87b 1.28b
    Note: CK is no fertilization; FP is conventional fertilization; CF is optimized fertilization; 90% FP, 80% FP, and 70% FP are applications of reduced N fertilizer by 10%, 20%, and 30%, respectively. CRU is the application rate from a conventional amount and a mixture of urea with a nitrification inhibitor and urea at a ratio of 7:3. Different lowercase letters in the same growth period and soil layer indicate significant differences at 0.05 level.

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    Table 6.  NO3 concentration in the soil profile during maize growth period in two cropping systems.
    Treatments Layers (cm) 2019
    NO3 concentration (mg/kg)
    2020
    NO3 concentration (mg/kg)
    Seedling stage Jointing stage Male withdrawal period Maturity Seedling stage Jointing stage Male withdrawal period Maturity
    CK 0–20 10.61d 8.09d 7.90f 1.42d 8.08d 5.37d 4.95d 1.50d
    20–40 4.85d 5.68c 6.73ab 0.97d 4.94d 3.69d 2.11c 0.85c
    40–60 1.30d 1.18c 1.02c 0.64c 1.37d 1.25d 1.18b 0.48c
    FP 0–20 76.08a 22.07b 15.75b 23.85c 52.27a 17.32b 10.43b 15.45b
    20–40 14.94bc 8.93b 7.92a 14.50a 15.99a 12.94b 4.51ab 12.91a
    40–60 9.37a 5.90a 4.36a 3.08ab 3.90a 5.82ab 2.47a 2.98ab
    CF 0–20 43.55c 35.39a 22.36a 33.01a 41.68c 31.81a 17.32a 26.30a
    20–40 19.78ab 18.34a 6.09b 15.38a 12.09b 18.06a 4.35b 14.91a
    40–60 4.01c 2.99b 2.26b 2.80b 2.80b 3.75c 2.51a 2.15b
    90% FP 0–20 64.24b 11.30cd 11.24c 20.29d 47.75ab 16.49bc 5.26cd 11.67bc
    20–40 15.57b 6.79bc 6.64ab 8.15b 16.92a 5.56c 2.92c 4.18b
    40–60 5.72bc 5.65a 3.84ab 3.55a 3.36ab 5.28b 2.46a 3.09a
    80% FP 0–20 57.03b 12.21c 12.36c 15.60e 45.99b 15.62bc 6.15c 10.15c
    20–40 12.57c 6.76bc 6.30b 8.78b 10.19bc 6.57c 2.95c 4.41b
    40–60 9.41a 2.32b 3.89ab 3.30a 1.90cd 6.71a 2.17ab 3.14b
    70% FP 0–20 57.65b 12.37c 12.84bc 12.65e 39.75c 14.98c 6.25c 8.74c
    20–40 23.17a 5.01c 5.24b 4.67c 8.52c 7.73c 2.78c 4.04b
    40–60 7.53ab 2.38b 3.29b 2.17bc 1.12d 6.76a 2.03ab 2.28b
    CRU 0–20 40.31c 23.06b 19.45ab 27.10b 39.67c 30.30a 14.14ab 23.69a
    20–40 16.14b 7.05b 6.94ab 14.85a 10.37bc 19.60a 5.15a 14.68a
    40–60 7.47b 2.95b 4.43a 3.28ab 2.47bc 3.05c 2.29a 1.99b
    Note: CK is no fertilization; FP is conventional fertilization; CF is optimized fertilization; 90% FP, 80% FP, and 70% FP are applications of reduced N fertilizer by 10%, 20%, and 30%, respectively. CRU is the application rate from a conventional amount and a mixture of urea with a nitrification inhibitor and urea at a ratio of 7:3. Different lowercase letters in the same growth period and soil layer indicate significant differences at 0.05 level.

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    The NO3 concentration in the 0–20 cm soil layer of wheat from the seedling to the heading stages was not significantly lower in the three reduced N treatments (90% FP, 80% FP, and 70% FP) than FP treatment. However, it was significantly lower at the maturity stage, with no significant differences between the three treatments. The NO3 concentration in the 20–40 cm soil layer of wheat was not significantly lower in the reduced N treatments from the seedling to the elongation stages but was significantly lower from the heading to the maturity stages, with no significant differences between the three treatments. A significant difference in the NO3 concentration was observed in the 40–60 cm soil layer from the seedling to the heading stages. However, there was no significant reduction at the maturity stage, with no significant differences between the three treatments.

    For maize, NO3 concentration in the 0–20 cm soil layer was significantly lower in the 90% FP and 80% FP treatments from the tasseling to maturity stages and in the 70% FP treatment at all growth stages. The NO3 concentration in the 20–40 cm soil layer was significantly lower in the 90% FP treatment at maturity stage and from the tasseling to the maturity stages in the 80% FP treatment, and from the elongation to the maturity stages in the 70% FP treatment. No significant differences occurred in the NO3 concentration in the 40–60 cm soil layer in all growth stages, but the three reduced N treatments showed a decrease in the NO3 concentration with decreasing N fertilizer input.

    The NO3 concentration in all soil layers during the wheat season at the seedling stage was significantly lower in the CF treatment than FP treatment. The NO3 distributions were 110.61% and 51.60% higher in the 0–20 cm soil layer at the maturity stage and 16.37% and 44.53% lower in the 20–40 cm soil layer during the two rotation cycles, respectively. In contrast, NO3 was no significant difference in the 40–60 cm soil layer. During the maize season, the NO3 concentration was significantly lower in the CF treatment in the 0–20 cm soil layer at the seedling stage. It was 38.41% and 70.23% higher in the elongation to the maturity stages. There were no significant differences in the 20–40 cm soil layer, but a significant decrease occurred in the NO3 concentration from the seedling to the elongation stages in the 40–60 cm soil layer, with decreases of 57.20–49.32% and 28.21–35.57%, respectively, during the two rotation cycles. No significant differences were observed from the tasseling to the maturity stages.

    Compared to FP treatment, the NO3 concentration was significantly lower in the CRU treatment in all soil layers during the wheat season at the seedling stage. It was 69.98% and 30.02% higher in the 0–20 cm soil layer at the maturity stage during the two rotation cycles, respectively. There were no significant differences in the 20–40 cm soil layer but a significant decrease in the 40–60 cm soil layer. The NO3 concentration was 27.01% and 36.32% lower during the two rotation cycles, respectively. During the maize season, the NO3 concentration was significantly lower in the CRU treatment in the 0–20 cm soil layer at the seedling stage. However, it significantly increased from elongation to maturity by 13.63% and 55.33%. There were no significant differences in the NO3 concentration between the treatments in the 20–40 cm soil layer, but a significant decrease occurred from the seedling to the elongation stages in the 40–60 cm soil layer, with decreases of 20.28–50.00% and 36.67–47.59% during the two rotation cycles, respectively. No significant differences occurred in the NO3 concentration from the tasseling to the maturity stages.

    Appropriate amounts of N fertilizer can substantially increase the effective spike number, grain number, and grain weight per unit area of crops. A moderate reduction in the N fertilizer application can increase the yield and improve fertilizer utilization efficiency. However, an excessive reduction in the N fertilizer amount can reduce the yield [24,25,26]. This is true for most types of soil. We found N fertilizer application was reduced by 20%, and a split fertilizer application under optimized conditions using controlled-release urea would increase wheat and maize yields by promoting yield attributes. While 30% reduced N fertilization showed an obvious decline in yield. The N is an essential nutrient for wheat growth and has a significant impact on wheat yield [27,28,29]. Results of this study are consistent with previous research works conducted in the Huang-Huai-Hai wheat region have shown that reducing the N amount from 240 kg/hm2 to 180 kg/hm2 did not significantly decrease the wheat yield, but a substantial yield loss occurred when the N application was further reduced to 120 kg/hm2 [30]. The most common N reduction management practices include deep placement and controlled-release fertilizers for one-time application to reduce fertilizer dosage and increase efficiency [31,32,33]. Jianjun et al. [34] observed that using controlled-release N fertilizer increased maize biomass accumulation and significantly increased maize grain yield compared to using urea. Li et al. [35] demonstrated a significant increase in maize yield when the N fertilizer amount was reduced by 35% (N195 kg/hm2). The N fertilizer input in the wheat-maize rotation system in the North China Plain is 588 kg/hm2 per year, significantly higher than in other countries [36]. Qin et al. [37] showed that reducing the N fertilizer amount by 150 kg/hm2 did not decrease wheat and maize yields compared to conventional fertilization when only chemical fertilizer or a 10% proportion of biogas slurry were used as substitutes.

    The uptake and utilization efficiency of N fertilizer are critical indicators of effective fertilizer management practices. This study indicates that the optimized fertilization under CF treatment and the controlled-release urea under CRU significantly increased. However, the TN accumulation in the crop plants, the N utilization and aNUE rates were lower, and the NPFP was higher in the 90% FP, 80% FP, and 70% FP treatments compared to control. Results are consistent with previous studies that have shown that an appropriate reduction in chemical N fertilizer combined with controlled-release N fertilizers or organic fertilizers can produce high yields by improving aNUE in a wheat-maize rotation system. Liping et al. [38] demonstrated that a one-time application of controlled-release N fertilizer (180 kg/hm2 N, with conventional fertilizer application of 280 kg/hm2) significantly improved wheat yield and aNUE. Li et al. [39] found that reducing the N fertilizer application by one-third (compared to a conventional N application rate of 288 kg/hm2) and combining it with organic fertilizer significantly improved aNUE and WUE in maize.

    The soil nutrient content reflects fertility and is crucial for crop growth and yield [40,41,42]. Studies have shown that long-term inappropriate N fertilizer applications can decrease soil OM content. These adverse effects can be mitigated by incorporating organic and inorganic fertilizers, such as straw [43], or increasing the application of organic fertilizers [44] to enrich OM content in soil. This study also showed that the OM, TN content and HN in the topsoil were higher in the CF and CRU treatments than FP treatment, whereas the TN content was significantly lower in the 30% N reduced treatment. This result indicates that excessive N reduction reduces crop yield and decreases the N supply in the soil, consistent with the findings of Zhang [47]. Liu et al. [45] found that reducing the N amount by 15% and applying humic acid increased the TN and alkaline N content in the soil significantly. Zeng et al. [46] reported that the N, P and K nutrients in maize fields significantly increased after reducing the N amount by 20% and plowing under winter green manure.

    The soil NO3 concentrations in different soil depths at different growth stages indicate how much applied N fertilizer is utilized and unutilized by the crop. Generally, higher NO3 accumulation below the root zone or in an ineffective soil layer is considered a loss, leading to the risk of leaching [50,51,52]. Subsequently, groundwater is contaminated through drainage after heavy doses of irrigation [48,49]. This study showed that the NO3 concentration in the topsoil, middle and bottom layers were significantly lower in the three N reduction treatments of 90% FP, 80% FP, and 70% FP than FP at the maturity stage of wheat from the heading stage to the maturity stage, and from the seedling stage to the heading stages, respectively. In the maize growing season, the NO3 concentration was significantly lower in the 90% FP and 80% FP treatments in the 0–20 cm soil layer from the tasseling stage to maturity and in the 70% FP treatment at all growth stages. The NO3 concentration was significantly lower in the 90% FP treatment at the maturity stage, in the 80% FP treatment from the tasseling stage to the maturity stage, and in the 70% FP treatment from the elongation stage to the maturity stage in the 20–40 cm soil layer. At the same growth stage, the NO3 concentration in the 40–60 cm soil layer decreased as the N fertilizer input decreased. These results are consistent with Jiang et al. [53] who observed that reducing the N amount by 25% for three consecutive years did not significantly affect maize yield, nutrient quality, or N uptake. It improved the N fertilizer utilization efficiency and significantly reduced the accumulation of NO3 concentration in the soil profile. Lu et al. [54] found that reducing N applications by 25–45% maintained the crop yield and reduced the accumulation of NO3 in the deep soil layer. Cao Bing et al. [55] demonstrated a 10–20% reduced N fertilizer, resulting in increased summer maize yield and reduced residual NO3 in deep soil layers. The finding of present study indicates that an appropriate N reduction can significantly reduce the residual inorganic N concentration in the soil below the plow layer and reduce the probability of leaching.

    We assessed the potential reduction in N fertilizer amounts in a wheat-maize rotation system in the yellow cinnamon soil region. The wheat and maize yields were significantly lower in the 80% FP and CRU treatments than CK for two consecutive years. The wheat yields were 3.62–2.57% higher and maize yields were 3.53–1.85% higher in the CF and CRU treatments than 80% FP treatment. However, a substantial yield reduction occurred when N fertilizer was reduced by 30%. The NRE, aNUE and NPFP were significantly higher in the CF and CRU treatments than FP treatment. Specifically, the NRE rate was 46.0% and 38.7% higher in the CF treatment and 37.8% and 46.2% higher in the CRU treatment in the two years. The OM, TN, and HN content in the topsoil were higher in the CF and CRU treatments than FP treatment. In addition, the NO3 concentration in the 0–20 cm soil layer during the wheat growing season was significantly higher in the CF and CRU treatments. These same treatments increased NO3 concentration from the elongation stage to the mature stage. In both treatments, the NO3 concentration in the 40–60 cm soil layer decreased significantly from the seedling to the elongation stage. Considering all factors, the CRU treatment with a 20% N reduction would be optimal fertilization for the wheat-maize rotation system in the yellow cinnamon soil region. However, further research is needed to investigate the long-term effects of N reduction.

    The authors declare they have not used Artificial Intelligence (AI) tools in the creation of this article.

    The authors declare no conflict of interest. The funders had no role in the design of the study; in the collection, analyses, or interpretation of data; in the writing of the manuscript; or in the decision to publish the results.

    This work was supported by the State Key Research and Development Program (No.2021YFD1700900: Processes and Regulatory Mechanisms of Nitrogen Non-point Source Pollution in Intensive Agricultural Areas in Northern China).

    We appreciate and thank the anonymous reviewers and Journal Editor Board for their constructive comments, which helped us improve the manuscript.



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