1.
Introduction
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.
2.
Material and methods
2.1. Experimental site
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.
2.2. Experimental design
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.
2.3. Sample collection and analytical methods
2.3.1. Sample collection
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.
2.3.2. Yield measurement and planting evaluation
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.
2.3.3. Parameters and lab 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:
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.
2.4. Statistical analysis
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.
3.
Results
3.1. Wheat and maize yields
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.
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.
3.2. Yield attributes of wheat and maize
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.
3.3. The nitrogen (N) uptake and utilization of wheat and maize
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.
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.
3.4. Soil organic matter (OM) content during wheat and maize maturity
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.
3.5. Total nitrogen (TN) content during wheat and maize rotation
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.
3.6. Available soil nitrogen content (aSNC) during wheat-maize rotation
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.
3.7. Nitrate (NO3-) distribution in different soil layers during different crop growth stages of wheat and maize
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.
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.
4.
Discussion
4.1. Effects of reduced N fertilizer applications on wheat and maize yields
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.
4.2. Effects of reduced N fertilizer applications on N uptake and utilization of wheat and maize
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.
4.3. Effects of reduced N fertilizer applications on OM content of wheat and maize fields
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.
4.4. Effects of reduced N fertilizer on soil NO3 concentration in wheat and maize fields at different growth stages
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.
5.
Conclusions
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.
Use of AI tools declaration
The authors declare they have not used Artificial Intelligence (AI) tools in the creation of this article.
Conflict of interest
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.
Funding
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).
Acknowledgments
We appreciate and thank the anonymous reviewers and Journal Editor Board for their constructive comments, which helped us improve the manuscript.