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Article

Subsoiling Improves the Photosynthetic Characteristics of Leaves and Water Use Efficiency of Rainfed Summer Maize in the Southern Huang-Huai-Hai Plain of China

1
Maize Research Center, Anhui Academy of Agricultural Sciences, Hefei 230001, China
2
School of Agronomy, Anhui Agricultural University, Hefei 230036, China
*
Author to whom correspondence should be addressed.
Agronomy 2020, 10(4), 465; https://doi.org/10.3390/agronomy10040465
Submission received: 16 February 2020 / Revised: 17 March 2020 / Accepted: 25 March 2020 / Published: 27 March 2020
(This article belongs to the Special Issue Stomata, Photosynthesis and Plant Water Use Efficiency)

Abstract

:
In the southern Huang-Huai-Hai (HHH) region, China, maize production is frequently threatened by waterlogging at the seedling stage and by drought at the big flare stage. A two-year field experiment was performed to explore whether subsoiling (SS) in the winter wheat season could improve the photosynthetic capacity and increase the water use efficiency (WUE) of summer maize using the variety, Luyu9105. A split design was adopted in the experiment. The main plots used tillage practices, including SS and rotary tillage (RT). The subplots consisted of two irrigation methods, i.e., applied supplemental irrigation at the big flare stage (I) and no irrigation at the big flare stage (NI). The results showed that the SS treatment significantly increased soil water content (SWC) in the 40–60 cm soil layer. The SS treatment improved green leaf area index (gLAI) by 15.1%–30.2%, and enhanced the ear-leaf net photosynthetic rate (Pn), stomatal conductance (gs), intercellular CO2 concentration (ci) and transpiration rate (Tr), and was accompanied by an increase in the grain-filling duration (T) by 5 days and the mean grain-filling rate (Va). The SS treatment decreased the stomatal limitation (Ls), indicating that RT treatment, which was under lower SWC, led to a decrease in Pn. Applied supplemental irrigation under RT treatment was able to compensate for the growth of leaves, but could not reverse the decreasing trend in the gLAI. Ultimately, the SS treatment improved WUE by 9.1%–9.9%, and increased grain yields by 10.0%–29.3%. Therefore, this study showed that in the southern Huang-Huai-Hai Plain, which has a yellow cinnamon soil type, the practice of SS can improve the photosynthetic characteristics of leaves and WUE of rainfed summer maize.

1. Introduction

The Huang-Huai-Hai (HHH) farming region is one of the most important maize-producing regions in China, accounting for 35.3% of China’s total maize yield from 1995 to 2007 [1,2,3]. Anhui Province is located in the southern HHH Plain. Shallow rotary tillage (RT) before the sowing of winter wheat and no-tillage of summer maize constitute the main cropping practices in this region [1,4,5]. However, the agricultural production in Anhui Province is mainly rainfed, and changes in the climate and variation in the annual and seasonal distribution of precipitation have affected water resources; this is threatening summer maize production [5,6,7].
Previous studies have shown that no-tillage or reduced-tillage practices are important climate-minded, conservation agriculture practices [8,9] and these methods have been promoted over the past few decades as sustainable farming practices that enhance the adaptive capacity of maize production under drought and heat stress [10]. In the semi-arid north China Plain, eleven years of no tillage has enhanced the mean percentage of macroaggregates and the macroporosity, particularly in dry years, and increased the soil organic matter and available nutrients in the top 10 cm soil layer [11]. However, in the southern HHH Plain which is characterized by yellow cinnamon soil, the uneven distribution of rainfall and no tillage in the long term may have adverse effects, including increased soil bulk density (SBD) in the top 10–20 cm soil layer and a reduction in the air-filled pore space, which prevents the infiltration and storage of water and aggravates water stress [1,3,12,13,14] especially in very wet seasons, which results in a decrease in the grain yield [10]. Moreover, topsoil is usually too loose to retain soil moisture under RT [15,16]. Under such conditions, one approach to achieve improved maize production is to minimize abiotic stress by adopting a proper soil tillage strategy such as subsoiling (SS) for winter wheat-summer maize double-cropping systems to improve the soil water content (SWC).
Subsoiling is an important strategy to break up the hardpan layer and reduce the SBD without turning over the infertile subsoil at the top [17,18,19]. In addition, by improving the soil structure, and establishing ideal conditions for root development and maintaining root activity, the practice of SS can effectively improve the water and nutrient supply to the aboveground portions of plants during grain filling [4]. This effectively delays plant senescence [20,21], and thereby increases yields and the water use efficiency (WUE) [22]. Sun [4] pointed out that SS tillage increased green leaf area index (gLAI), ear-leaf net photosynthetic rate (Pn) and the chlorophyll fluorescence characteristics by enhancing dry matter accumulation (DMA) at the post-silking stage. Wang [18] found that SS improved both root DMA and shoot DMA at the post-silking stage and increased the maximum and mean grain-filling rate (Va), thus increasing the grain yield.
However, previous studies have mainly focused on the effects of SS on the soil properties [23], and have been mainly located in the semi-arid North China Plain. Little is known about how SS tillage affects maize growth, especially in a rainfed area with an ample but uneven distribution of precipitation. Our study aims to clarify whether SS in the winter wheat season could improve the photosynthetic capacity of summer maize and increase WUE, thereby increasing the grain yield. In this context, we conducted this study with the objective of assessing SS practices in the winter wheat season in terms of its impact on (1) gLAI, photosynthetic capacity and chlorophyll fluorescence of leaves; (2) aboveground DMA and dry matter translocation (DMT); and (3) grain-filling, grain yield, yield components and WUE in the summer maize season.

2. Materials and Methods

2.1. Plant Materials and Culture Conditions

A field experiment was conducted at the experimental station of the Anhui Academy of Agricultural Sciences, China (31°57′ N, 117°11′ E), in 2016 and 2017. The region has a temperate continental monsoon climate. The annual mean temperature over the last 30 years is 15.7 °C, and the mean annual precipitation is 1000 mm. The monthly distribution of precipitation, the annual total precipitation and mean temperature in 2016 and 2017 at the experimental site are shown in Table 1. The soil is yellow cinnamon with a pH value of 5.6, and the nutrient conditions of the soil in the top 20 cm in 2016 are shown in Table 2. The soil available P was extracted with 0.5 mol/L NaHCO3, and the available K was extracted with 1 mol/L C2H7NO2, by using the Mo-Sb anti-spectrophotometer method and the flame photometry method. The SBD was measured prior to sowing using the cutting-ring method, the values for SBD and SWC in 2016 and 2017 at the beginning of the summer maize season are provided in Table 3.

2.2. Experimental Design

The experiment involved a two-factor split-plot design. The soil tillage practice was the main plot factor, and irrigation at the big flare stage was the subplot factor. The two tillage practices were SS tillage (40 cm deep) and RT (15 cm deep), which were applied in the winter wheat season. In the summer maize season, each tillage practice comprised two irrigation patterns: supplemental irrigation applied at the big flare stage (I) and no supplemental irrigation at the big flare stage (rainfed) (NI). The four treatments were SS + I, RT + I, SS + NI and RT + NI, with four replicates. The length and width of each plot was 12 m × 12 m, each plot being 144 m2.
The winter wheat variety was Annong 0711, and the summer maize cultivar Luyu9105 were chosen for this study, as it is widely grown in Anhui Province and is high-yielding, multi-resistant and highly adaptable. After the maize and wheat were harvested, the straw was chopped into small pieces at lengths of less than 10 cm and returned to the soil of the experimental plots using a combine harvester. In the winter wheat season, the size of each plot was also 12 m × 12 m, the row spacing was 20 cm, and there was no supplemental irrigation in the winter wheat season. The maize was sown manually using a seed planting machine at a planting density of 75,000 plants ha−1 with a row spacing of 60 cm. The planting dates were June 25, 2016 and June 18, 2017, and the harvesting dates were October 18, 2016, and October 8, 2017. The N fertilizer was urea (N 46%) and compound fertilizer (NPK 15:15:15), and the application rate in winter wheat and summer maize was 240 kg ha−1, respectively. The application rate of P and K fertilizer were 105 kg ha−1 and 135 kg ha−1, respectively, using the compound fertilizer. Due to insufficient K fertilizer, we applied K2SO4 as a supplement. All the fertilizer was applied per plot prior to sowing. Weeds, disease, and insect pests were rigorously controlled.
At the big flare stage (11–12 visible leaves, on July 25 in 2016 and July 18 in 2017) of summer maize, 300 m3 ha−1 of supplemental irrigation was applied, and a sprinkler system was used for all the irrigation treatments. The gap between the two adjacent SS and RT treatment plots was 1.5 m to avoid the interference of supplemental irrigation. No further irrigation during maize growth was used in any of the treatments.

2.3. gLAI

The leaves were grouped into three leaf layers, i.e., ear leaves (three-ear leaves), above-ear leaves (the leaves above the three-ear leaves), and below-ear leaves (the leaves below the three-ear leaves). At the big flare stage and silking stage, three plants were randomly selected per plot to determine the gLAI [24]. The gLAI was calculated as follows:
gLAI = Σ (A × B × 0.75) × C / D
where A is the leaf length, B is the maximum leaf width, C is the plant density, and D is the planted soil area.

2.4. Leaf Gas Exchange Characteristics

At the big flare (July 25 in 2016, July 18 in 2017), silking (August 10 in 2016, August 5 in 2017) and mid-filling (Autumn 30 in 2016, Autumn 28 in 2017) stages, the Pn, stomatal conductance (gs), intercellular CO2 concentration (ci) and transpiration rate (Tr) of the ear leaves were measured using a portable gas exchange system (LI-6400, LI-COR, Lincoln, USA), and the stomatal limitation (Ls) was calculated. Six plants from each plot were measured on clear days from 9:30–11:00 a.m. Consistent measurement conditions were used: an LED light source, a photosynthetically active radiation (PAR) value of 1400 μmol m−2 s−1, a flow rate of 500 cm3 min−1, a constant CO2 concentration of 400 μmol mol−1, an air temperature of 30 °C, and a relative humidity of 65% [25].
The chlorophyll fluorescence was determined for the ear leaves by nondestructively measuring the photophysiological parameters using pulse amplitude modulation fluorometry (PAM-2500, Walz, Germany) at the big flare and silking stages. The initial fluorescence (Fo) and maximal fluorescence (Fm) were measured after 30 min of dark adaptation. The maximal PSII photochemical efficiency (Fv/Fm), the potential PSII photochemical efficiency (Fv/Fo), effective quantum yield of PSII (ΦPSII) and photochemical fluorescence quenching coefficients (qP) were also recorded.

2.5. DMA and DMT

In the middle of each plot, three adjacent plants were manually cut at ground level at the silking and maturity stages in the three replicates. Fresh dry matter samples were heated in an oven for 30 min at 105 °C to deactivate the enzymes and were then dried at 80 °C to a constant weight to measure their DMA. The DMT from the vegetative organs to the grain between silking and maturity, the DMA at the post-silking stage and the contribution of dry matter at the post-silking stage to the grain weight (CDMGW) were calculated following the methods of Wu et al. [5].
DMT = DMA at the silking stage – DMA at the maturity stage
The DMA at the post-silking stage = Grain weight at maturity stage − DMT
CDMGW = DMA   at   the   post silking   stage   Grain   yield   ×   100

2.6. Grain-Filling Characteristics

The silking date was recorded when the silks emerged in 50% of the plants in a plot. Four ears in each plot were randomly selected. The plants were harvested at 11, 18, 26, 34, 40, 43, 46, and 49 days after silking, and 100 grains were cut and removed from the middle of each sampled ear [26]. The dry weight of 100 grains for each ear was measured after drying to a constant weight in a forced-air oven at 80 °C.
The dynamics of grain weight during grain filling followed the Richards growth equation [25,27]:
Y = K 1 + e A + B t    
where Y is the grain weight, K is the ultimate grain weight, t is the day after pollination, and A and B are the coefficients determined by the regression. The early grain-filling period (t1), the middle grain-filling period (t2), the late grain-filling period (t3), the duration of the early grain-filling period (T1), the duration of the middle grain-filling period (T2), the duration of the late grain-filling period (T3), the grain-filling duration (T), the mean grain-filling rate (Va), the maximum grain-filling rate (Vm), the grain weight during the early grain-filling period (W1), the grain weight during the middle grain-filling period (W2), the grain weight during the late grain-filling period (W3), the grain-filling rate during the early grain-filling period (V1), the grain-filling rate during the middle grain-filling period (V2) and the grain-filling rate during the late grain-filling period (V3) were calculated using the following equations:
t 1 = A ln ( 2 + 1.732 ) ( B )
t 2 = A + ln ( 2 + 1.732 ) ( B )
t 3 = ( 4.59512 + A ) B
T1 = t1
T2 = t2 – t1
T3 = t3 – t2
T = t3
Va = K / t3
Vm = (–B × K) / 4
W 1 = K 1 + e A + B t 1
W 2 = K 1 + e A + B t 2     K 1 + e A + B t 1
W 3 = K 1 + e A + B t 3     K 1 + e A + B t 1
V1 = W1 / T1
V2 = W2 / T2
V3 = W3 / T3

2.7. Grain Yield

At the maturity stage, 30 ears were harvested from three rows (12 m2) at the center of each plot to determine the yield and ear characteristics, including the row number, and kernel number per row. All the kernels were air-dried, and grain yield was calculated at 14% moisture, which is the standard for maize storage or sale in China (GB/T29890-2013). The grain yield was calculated as follows [25]:
The grain yield(kg ha−1) = A × B × C × (1−14%) / 106 × (1–D)
where A is the harvested ears (ears ha−1); B is the kernel number per ear; C is the 1000-grain weight (g 1000 grains−1); D is the sample moisture content (%).

2.8. SWC and WUE

The SWC was measured by the oven-drying method. Soil samples were collected manually using a soil auger (with a 5 cm diameter) at 10 cm increments to a depth of 40 cm in 2016 and 20 cm increments to a depth of 60 cm in 2017 in all experimental plots to measure the SWC. Measurements were performed before irrigation at the big flare stage and the harvest season of summer maize. SWC was defined as follows [28]:
SWC = W f r e s h W d r y W d r y × 100
where W f r e s h   and   W d r y are soil fresh weight and soil dry weight, respectively.
The seasonal maize evapotranspiration (ETa) (mm) and WUE (kg ha−1 mm−1) were calculated according to Wang et al. [29].
ETa = P + I + C r     R     D   ±   Δ S
WUE = Y / ETa
where P is the seasonal total precipitation (mm), I is the seasonal irrigation (mm), Cr is the seasonal upward capillary flow into the root zone (mm), R is the seasonal runoff (mm), and D is the downward flux below the crop root zone. The Cr, R, and D were considered to be zero because the surface runoff was nonexistent, and there was negligible capillary rise from 20–30 m below the soil surface during the growing season. The seasonal change in the soil water storage at 0–100 cm is ΔS, and Y is the maize grain yield (kg ha−1).

2.9. Statistical Analysis

Data were analyzed by analysis of variance (ANOVA) at the 5% significance level to determine the differences between the different treatments using SPSS 13.0 (SPSS, Chicago, IL, USA). The differences were determined by least significant difference (LSD) multiple-range tests at the 5% significance level. All of the figures were drawn using SigmaPlot 10.0 (Sigmaplot, California, CA, USA).

3. Results

3.1. gLAI

The SS treatment significantly improved the gLAI by 15.1 and 17.5% in 2016, and 30.2 and 17.5% in 2017, compared to the RT treatment (Figure 1). The RT + I treatment increased the gLAI values by 19.7% and 17.3% at the silking stage in 2016 and 2017, respectively, compared with the RT + NI treatment (Figure 1). The SS + I treatment significantly increased the gLAI values by 19.6% and 17.4% in 2016 and by 43.3% and 38.0% in 2017, compared to RT + I and RT + NI treatments, respectively (Figure 1). However, there was no significant difference between the SS + NI and RT + I treatments.
At the silking stage, the gLAI values at the different leaf layers were ranked as follows: below-ear leaves > ear leaves > above-ear leaves (Figure 2). The gLAI values in the SS treatment were significantly increased by 11.1% in the above-ear leaves, 30.2% in the ear leaves, and 36.8% in the below-ear leaves in 2016 and by 22.7%, 17.5%, and 17.5%in 2017, compared to those under the RT treatment. The RT + I treatment significantly increased gLAI in 2016 and 2017, by 8.4% and 25.6% in the above-ear leaves, 9.5% and 13.6% in the ear leaves, and 39.8% and 14.8% in the below-ear leaves, respectively, compared to those in the RT + NI treatment. In addition, compared with the RT + I treatment, the SS + NI treatment significantly improved the gLAI values of the ear leaves and below-ear leaves, although there was no significant difference in the above-ear leaves.

3.2. Leaf Photosynthetic Capacity

In the growing season, the Pn values were ranked as follows: SS + I > RT + I > SS + NI > RT + NI (Table 4). The SS treatment led to a significant increase in Pn by 4.4%, 15.6%, and 18.6% in 2016 and by 4.8%, 11.5%, and 18.8% in 2017 at the big flare stage, silking stage and mid-filling stage, respectively. Increases in gs, ci and Tr were observed in the SS treatment, while, Ls was decreased by 7.5 and 13.3% in 2017 at the big flare and mid-filling stage, respectively. The RT + I treatment significantly increased Pn by 2.0, 7.9 and 9.0% at different stages, respectively, compared to the RT + NI treatment, and this was accompanied by a decrease in gs, ci and Tr values and a decrease in Ls.
The SS treatment significantly improved the Fv/Fm and Fv/Fo (Figure 3), compared with the RT treatment. The SS treatment increased the ΦPSII by 7.4% and 3.5% in 2016, and 2.4% and 1.5% in 2017, and increased qP by 7.0% in 2016, and 0.5% and 2.4% in 2017, respectively (Table 5). However, the application of supplemental irrigation at the big flare stage could alleviate the adverse effects on the Fv/Fm and Fv/Fo.

3.3. DMA and DMT

The DMA weight after the silking stage accounted for 54.0%–59.0% in 2016 and 56.2%–58.0% in 2017 (Figure 4). The SS treatment significantly increased the DMA at the silking and maturity stages by 9.8% and 8.2% in 2016, and by 8.4% and 10.5% in 2017, respectively. Compared with the RT + NI treatment, the RT + I treatment significantly increased DMA by 27.2% and 25.8% in 2016 and by 21.8% and 12.0% in 2017, respectively. The SS + I treatment decreased the DMT and the contribution of DMT before the silking stage to the grain stage. The RT + NI treatment increased the DMT and the contribution of DMT before the silking stage to the grain stage (Table 6).

3.4. Grain-Filling Characteristics

The SS treatment had a significant influence on the 100-grain weight, which was 10.4% higher than that in the RT treatment (Figure 5). The RT + I treatment significantly improved the 100-grain weight by 13.5%, compared to the RT + NI treatment, while there was no significant difference between the RT + I and SS + NI treatments.
The SS treatment improved the T, Vm and Va (Table 7), while RT resulted in a decrease in K, T, Va and Vm. Compared to the RT treatment, the SS treatment increased the T by 5 days, especially the duration of the middle (T2) and late grain-filling periods (T3) and the grain-filling rate of the early period (V1). The results showed that SS can prolong the T and increase the Va, which resulted in a significant increase in the grain weight.

3.5. Grain Yield and WUE

The SS treatment significantly increased grain yield by 9.0% in 2016 and 12.0% in 2017 (Table 8), compared with that of the RT treatment. The application of supplemental irrigation at the big flare stage effectively alleviated the reduction in grain yield induced by the RT treatment, which increased by 10.1% and 13.7% in 2016 and 2017, respectively, compared with that of the RT + NI treatment. However, there was no significant difference between the SS + NI and RT + I treatments. The SS + I treatment enhanced grain yield by 6.9% and 17.7% in 2016 and by 13.7% and 29.3% in 2017, compared to the RT + I and RT + NI treatments. Moreover, the number of kernels per plant was higher in the SS treatments than in the RT treatment by 11.8% in 2016 and 11.0% in 2017.
The SS treatment significantly increased the SWC by 5.4%, 4.9%, 9.3% and 9.0% in the 0–10 cm, 10–20 cm, 20–30 cm and 30–40 cm soil layers, respectively, in 2016. The SWC values increased by 4.3%, 3.8% and 11.5% in the 0–20 cm, 20–40 cm and 40–60 cm soil layers, respectively, in 2017 (Figure 6), compared to the RT treatment. The SS treatment significantly increased the WUE by 9.1% in 2016 and by 9.9% in 2017, compared to the RT treatment. With supplemental irrigation at the big flare stage, the RT + I treatment significantly increased the WUE by 4.8% in 2016 and 5.9% in 2017, compared to the RT + NI treatment. The SS + I treatment significantly increased the WUE by 2.2% in 2016 and 9.5% in 2017, compared to the SS + NI treatment (Table 8).

4. Discussion

4.1. Subsoiling Practice to Improve gLAI and Leaf Photosynthetic Function

Optimized tillage practices can alter the soil environment by facilitating both the physical and chemical characteristics of the soil, thereby improving the root function and increasing crop biomass [1,17]. The gLAI is an important indicator of canopy architecture at different growth stages, and a longer gLAI duration at the post-silking period is one of several morphophysiological traits associated with the improvement of maize yields [30]. However, until now, few studies have been conducted to determine how different leaf layers are affected by tillage practices. Our results indicated that SS treatment enhanced the gLAI. Supplemental irrigation applied under the RT treatment could compensate for the adverse effects of water deficiency on the gLAI, but the compensatory effect was still weaker than the effect of the SS + NI treatment. This finding illustrates that SS tillage could improve the storage of water in deeper soil and influence root growth and distribution in the soil [31]. The spatial distribution of the root system in a soil profile has a great influence on the absorption of soil water and nutrients [18,32,33]. In the experimental location, during June in 2016 and June 2017, the precipitation amount was 191 mm and 54 mm, respectively. However, from July 16 to August 2 in 2016, the total rainfall was only 22.5 mm, and from July 10 to August 1 in 2017, the total rainfall was only 7.9 mm, and this was accompanied by high temperatures, which may induce water and heat stress. The SS treatment decreased the soil bulk density of the deep soil layer and improved the SWC in the 30–40 cm soil layer, especially in 2016, under high precipitation at the seedling stage of the maize. In 2017, with lower precipitation at the silking stage, the SS practice enhanced the SWC in the 40–60 cm soil layer, which was necessary in the later growing season. With the improvement in deep SWC, the gLAI was improved, whereas long-term RT management caused soil compaction, the soil bulk density increased and water penetration was reduced [12,13,14]. Even when supplemental irrigation was applied at the big flare stage, a higher soil bulk density reduced water infiltration, which resulted in an increase in surface runoff; therefore, the soil water storage in the deep soil decreased. This resulted in an undesirable soil water environment for summer maize, especially for root growth [22,34,35], which may lead to abnormal growth of shoot parts [6,31] and decreased gLAI.
A higher gLAI can provide a larger source of photosynthate at the post-silking stage. Our study showed that SS caused a significant increase in Pn, gs, ci and Tr, accompanied by a significant decrease in Ls, indicating that under conditions of water stress, the stomata closed to decrease the transpiration, and save water. Stomatal closure was the main reason for the decline in Pn under conditions of water stress. Under the RT treatment, the lower SWC and gLAI resulted in a decrease of Pn, which may be due to the deficiency of soil water and N content in the soil [36]. Moreover, SS treatment had a positive effect on Fv/Fm. The SS treatment improved both Pn and chlorophyll fluorescence characteristics in the growing season, especially in the later growing season, which resulted in higher grain filling characteristics in the grain-filling stage.

4.2. Subsoiling Practice to Increase Grain Yield and WUE

Optimum canopy function is a key factor in achieving a higher yield. Photosynthesis supplies carbohydrates for maize DMA and grain yield formation [7]. Previous studies have shown that without supplemental irrigation throughout the whole growing season, the SS practice can improve grain yields by up to 46% compared to conventional tillage. However, under irrigation conditions, there is no significant difference between the SS and conventional tillage treatments [15,37]. Our study in yellow cinnamon soil showed that the SS + I treatment decreased the DMT to the grain and the contribution of DMT to the grain before the silking stage. However, the SS + I treatment enhanced the DMA and increased the contribution of DMA to the grain at the post-silking stage. This phenomenon may occur due to the higher gLAI and Pn in the grain-filling stage, accompanied by an increase in the grain-filling rate in the later reproductive stage and longer grain-filling duration, especially the middle grain-filling period, which resulted in the higher DMA at the post-silking stage and had a strong influence on the yield formation, which is consistent with the results of Zhai [1]. However, long-term RT treatment caused high soil bulk density, which affects the soil microbial populations and enzyme activities and limits both root growth and uptake of moisture and nutrients, ultimately affecting crop growth and productivity [18,22,38]. The availability of soil water for plants is a major determinant in the yield potential [39]. Our results showed that with the decrease in soil bulk density, the SWC in the deep soil layer increased and WUE was enhanced, which may occur because SS, as a proper tillage practice, is able to break up the plow pan [40,41].
Consequently, our results indicate that the SS treatment can improve the soil water content in the deep soil layer, which then increases the gLAI, Pn, post-silking DMA and DMT, grain-filling rate and grain-filling duration, thereby improving the grain yield and WUE. When the seasonal rainfall distribution is inconsistent, the practice of SS may alleviate heat and drought damage, and improve the maize growth, which reduces the input cost [42]. However, the annual SS practice may increase the mechanical operation consumption, regardless of the agronomic input cost, compared with the RT practice. Therefore, in the future, we will further research new tillage modes, for example, one year of SS practice plus one year of no tillage practice, or a longer no tillage practice in order to reduce the input costs. Additionally, we will further our research on the root and nitrogen content in the soil profile response to the different tillage practices to confirm our hypothesis.

5. Conclusions

The SS practice decreased the soil bulk density, enhanced SWC in the soil, and improved gLAI and Pn. Under RT treatment, which may cause water stress, stomatal closure is the main reason for the decline in Pn. Applying supplemental irrigation under RT treatment can compensate for this via the improved growth of leaves, although it still cannot reverse the decreasing trend. Ultimately, the SS treatment improved the WUE, which resulted in an increase in grain yield.

Author Contributions

W.W. and H.C. designed the research. W.W., S.W., L.Z., C.P., L.J. and H.C. performed the research. W.W., S.W., L.Z., J.L., Y.S., C.P., X.C. and H.C. analyzed the data. W.W., S.W., and H.C. wrote the article. W.W., S.W., L.Z., J.L., Y.S., C.P., X.C., L.J. and H.C. revised the article. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by the National Key Research and Development Program of China (2017YFD0301307) and (2018YFD0300901), and Innovation Team Project of the Anhui Academy of Agricultural Sciences.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Zhai, L.C.; Xu, P.; Zhang, Z.B.; Li, S.K.; Xie, R.Z.; Zhai, L.F. Effects of deep vertical rotary tillage on dry matter accumulation and grain yield of summer maize in the Huang-Huai-Hai Plain of China. Soil Till. Res. 2017, 170, 167–174. [Google Scholar] [CrossRef]
  2. Liu, Y.; Wang, Y.; Yang, X.G. Trends in reference crop evapotranspiration and possible climatic factors in the North China Plain. Acta Ecol. Sin. 2010, 4, 923–932. [Google Scholar]
  3. Yang, X.L.; Gao, W.S.; Shi, Q.H.; Chen, F.; Chu, Q.Q. Impact of climate change on the water requirement of summer maize in the Huang-Huai-Hai farming region. Agric. Water Manag. 2013, 124, 20–27. [Google Scholar] [CrossRef]
  4. Sun, X.F.; Ding, Z.S.; Wang, X.B.; Hou, H.P.; Zhou, B.Y.; Yue, Y.; Ma, W.; Ge, J.Z.; Wang, Z.M.; Zhao, M. Subsoiling practices change root distribution and increase post-anthesis dry matter accumulation and yield in summer maize. PLoS ONE 2017, 12, e0174952. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  5. Wu, W.M.; Chen, H.J.; Wang, S.J.; Wei, F.Z.; Li, J.C. Effects of nitrogen fertilization application regime on dry matter, nitrogen accumulation and transportation in summer maize under waterlogging at the seedling stage. Acta Agron. Sin. 2015, 41, 1246–1256. [Google Scholar] [CrossRef]
  6. Ren, B.C.; Zhang, J.W.; Li, X.; Fan, X.; Dong, S.T.; Liu, P.; Zhao, B. Effects of waterlogging on the yield and growth of summer maize under field conditions. Can. J. Plant. Sci. 2014, 94, 23–31. [Google Scholar] [CrossRef]
  7. Ren, B.C.; Dong, S.T.; Liu, P.; Zhao, B.; Zhang, J.W. Ridge tillage improves plant growth and grain yield of waterlogged summer maize. Agric. Water Manag. 2016, 177, 392–399. [Google Scholar] [CrossRef]
  8. Richards, M.; Sapkota, T.; Stirling, C.; Thierfelder, C.; Verhulst, N.; Friedrich, T.; Kienzle, J. Conservation Agriculture: Implementation guidance for policymakers and investors. Clim. Smart Agric. 2014. [Google Scholar] [CrossRef]
  9. Kafesu, N.; Chikowo, R.; Mazarura, U.; Gwenzi, W.; Snapp, S.; Zingore, S. Comparative fertilization effects on maize productivity under conservation and conventional tillage on sandy soils in a smallholder cropping system in Zimbabwe. Field Crop. Res. 2018, 218, 106–114. [Google Scholar] [CrossRef]
  10. Steward, P.R.; Dougill, A.J.; Thierfelder, C.; Pittelkow, C.M.; Stringer, L.C.; Kudzala, M.; Shackelford, G.E. The adaptive capacity of maize-based conservation agriculture systems to climate stress in tropical and subtropical environment: A meta-regression of yield. Agric. Ecosyst. Environ. 2018, 251, 194–202. [Google Scholar] [CrossRef]
  11. He, J.; Li, H.W.; Rabi, G.R.; Wang, Q.J.; Cai, G.H.; Su, Y.B.; Qi, X.D.; Liu, L.J. Soil properties and crop yield after 11 years of no tillage farming in wheat-maize cropping system in North China Plain. Soil Till. Res. 2011, 113, 48–54. [Google Scholar] [CrossRef]
  12. Hou, X.Q.; Li, R.; Jia, Z.K.; Han, Q.F.; Wang, W.; Yang, B.P. Effects of rotational tillage practices on soil properties: Winter wheat yields and water-use efficiency in semi-arid areas of north-west China. Field Crop. Res. 2012, 129, 7–13. [Google Scholar] [CrossRef]
  13. Václav, S.; Radek, V.; Jana, C.; Helena, K.; Pavel, R. Winter wheat yield and quality related to tillage practice: Input level and environmental conditions. Soil Till. Res. 2013, 132, 77–85. [Google Scholar] [CrossRef]
  14. Zhang, Y.J.; Wang, R.; Wang, S.L.; Wang, H.; Xu, Z.G.; Jia, G.C.; Wang, X.L.; Li, J. Effects of different sub-soiling frequencies incorporated into no-tillage systems on soil properties and crop yield in dryland wheat-maize rotation system. Field Crop. Res. 2017, 209, 151–158. [Google Scholar] [CrossRef]
  15. Liu, Z.D.; Qin, A.Z.; Zhao, B.; Ata-UI-Karim, S.T.; Xiao, J.F.; Sun, J.S.; Ning, D.F.; Liu, Z.G.; Nan, J.Q.; Duan, A.W. Yield response of spring maize to inter-row subsoiling and soil water deficit in northern China. PLoS ONE 2016, 11, e0153809. [Google Scholar] [CrossRef]
  16. Sang, X.G.; Wang, D.; Lin, X. Effects of tillage practices on water consumption characteristics and grain yield of winter wheat under different soil moisture conditions. Soil Till. Res. 2016, 163, 185–194. [Google Scholar] [CrossRef]
  17. Piao, L.; Qi, H.; Li, C.F.; Zhao, M. Optimized tillage practices and row spacing to improve grain yield and matter transport efficiency in intensive spring maize. Field Crop. Res. 2016, 198, 258–268. [Google Scholar] [CrossRef]
  18. Wang, X.B.; Zhou, B.Y.; Sun, X.F.; Yue, Y.; Ma, W.; Zhao, M. Soil tillage management affects maize grain yield by regulating spatial distribution coordination of roots, soil moisture and nitrogen status. PLoS ONE 2015, 10, e0129231. [Google Scholar] [CrossRef] [Green Version]
  19. Singh, K.; Choudhary, O.P.; Singh, H. Effects of sub-soiling on sugarcane productivity and soil properties. J. Sugarcane Res. 2013, 2, 32–36. [Google Scholar] [CrossRef]
  20. Qin, H.L.; Gao, W.S.; Ma, Y.C.; Ma, L.; Yin, C.M. Effects of subsoiling on soil moisture under no-tillage 2 years later. Sci. Agric. Sinica. 2008, 41, 78–85. [Google Scholar] [CrossRef]
  21. Liang, J.F.; Qi, Q.Z.; Jia, X.H.; Gong, S.J.; Huang, Y.F. Effects of different tillage managements on soil properties and corn growth. Ecol. Environ. Sci. 2010, 19, 945–950. [Google Scholar] [CrossRef]
  22. Shi, Y.; Yu, Z.W.; Man, J.G.; Ma, S.Y.; Gao, Z.Q.; Zhang, Y.L. Tillage practices affect dry matter accumulation and grain yield in winter wheat in the North China Plain. Field Crop. Res. 2016, 160, 73–81. [Google Scholar] [CrossRef]
  23. Hu, H.Y.; Ning, T.Y.; Li, Z.J.; Han, H.F.; Zhang, Z.Z.; Qin, S.J.; Zheng, Y.H. Coupling effects of urea types and subsoiling on nitrogen–water use and yield of different varieties of maize in northern China. Field Crop. Res. 2013, 142, 85–94. [Google Scholar] [CrossRef]
  24. Qi, W.Z.; Liu, H.H.; Liu, P.; Dong, S.T.; Zhao, B.Q.; So, B.H.; Li, G.; Liu, H.D.; Zhang, J.W.; Zhao, B. Morphological and physiological characteristics of corn (Zea mays L.) roots from cultivars with different yield potentials. Eur. J. Agron. 2012, 38, 54–63. [Google Scholar] [CrossRef]
  25. Wu, W.M.; Wang, S.J.; Chen, H.J.; Song, Y.H.; Zhang, L.; Chen, P.; Jing, L.L.; Li, J.C. Optimal nitrogen regimes compensate for the impacts of seedling subjected to waterlogging stress in summer maize. PLoS ONE 2018, 13, e0206210. [Google Scholar] [CrossRef] [PubMed]
  26. Gambin, B.L.; Borras, L.; Otegui, M.E. Source-sink relations and kernel weight differences in maize temperate hybrids. Field Crop. Res. 2006, 95, 316–326. [Google Scholar] [CrossRef]
  27. Shen, X.S.; Zhu, Y.J.; Guo, T.C.; Li, G.Q.; Qu, H.J. Effects of sulphur application on characteristics of grain filling and grain yield of winter wheat cultivar Yumai 50. Acta Bot. Boreal Occident. Sin. 2007, 27, 1265–1269. [Google Scholar]
  28. Ma, S.; Yu, Z.W.; Shi, Y.; Gao, Z.Q.; Luo, L.P.; Chu, P.F.; Guo, Z.J. Soil water use, grain yield and water use efficiency of winter wheat in a long-term study of tillage practices and supplemental irrigation on the North China Plain. Agric. Water Manag. 2015, 150, 9–17. [Google Scholar] [CrossRef]
  29. Wang, T.C.; Wei, L.; Wang, H.Z.; Ma, S.C.; Ma, B.L. Responses of rainwater conservation, precipitation-use efficiency and grain yield of summer maize to a furrow planting and straw-mulching system in northern China. Field Crop. Res. 2011, 124, 223–230. [Google Scholar] [CrossRef]
  30. Duvick, D.N. The contribution of breeding to yield advances in maize (Zea mays L.). Adv. Agron. 2005, 86, 83–145. [Google Scholar] [CrossRef]
  31. Doussan, C.; Pierret, A.; Garrigues, E.; Pagès, L. Water uptake by plant roots: II-modelling of water transfer in the soil root-system with explicit account of flow within the root system-comparison with experiments. Plant. Soil. 2006, 283, 99–117. [Google Scholar] [CrossRef]
  32. Amato, M.; Ritchie, J.T. Spatial distribution of roots and water uptake of maize (Zea mays L.) as affected by soil structure. Crop. Sci. 2002, 42, 773–780. [Google Scholar] [CrossRef]
  33. Wei, S.S.; Wang, X.Y.; Shi, D.Y.; Li, Y.H.; Zhang, J.W.; Liu, P.; Zhao, B.; Dong, S.T. The mechanisms of low nitrogen induced weakened photosynthesis in summer maize (Zea mays L.) under field conditions. Plant. Physiol. Bioch. 2016, 105, 118–128. [Google Scholar] [CrossRef] [PubMed]
  34. Nyakudya, I.W.; Stroosnijder, L. Conservation tillage of rainfed maize in semi-arid Zimbabwe: A review. Soil Till. Res. 2015, 145, 184–197. [Google Scholar] [CrossRef]
  35. He, J.; Li, H.; Wang, X.Y.; McHugh, A.D.; Li, W.Y.; Gao, H.W.; Kuhn, N.J. The adoption of annual subsoiling as conservation tillage in dryland maize and wheat cultivation in northern China. Soil Till. Res. 2007, 94, 493–502. [Google Scholar] [CrossRef]
  36. Zong, Y.Z.; Shangguan, Z.P. Nitrogen deficiency limited the improvement of photosynthesis in maize by elevated CO2 under drought. J. Integr. Agric. 2014, 1, 73–81. [Google Scholar] [CrossRef] [Green Version]
  37. Verhulst, N.; Nelissen, V.; Jespers, N.; Haven, H.; Sayre, K.D.; Raes, D.; Deckers, J.; Govaerts, B. Soil water content, maize yield and its stability as affected by tillage and crop residue management in rainfed semi-arid highlands. Plant. Soil. 2011, 344, 73–85. [Google Scholar] [CrossRef]
  38. Li, C.H.; Ma, B.L.; Zhang, T.Q. Soil bulk density effects on soil microbial populations and enzyme activities during the growth of maize (Zea mays L.) planted in large pots under field exposure. Can. J. Plant. Sci. 2002, 82, 147–154. [Google Scholar] [CrossRef] [Green Version]
  39. Karuma, A.; Mtakwa, P.; Amuri, N.; Gachene, C.K.; Gicheru, P. Enhancing soil water content for increased food production in semi-arid areas of Kenya. J. Agric. Sci. 2014, 6, 125–134. [Google Scholar] [CrossRef] [Green Version]
  40. Christian, B.H.; Jesper, R.; Carsten, S. Kemink subsoiling before and after planting. Soil Till. Res. 2005, 80, 59–68. [Google Scholar] [CrossRef]
  41. Harun, Y.; Engin, C. Tillage effects and energy efficiencies of subsoiling and direct seeding in light soil on yield of second crop corn for silage in Western Turkey. Soil Till. Res. 2006, 90, 250–255. [Google Scholar] [CrossRef]
  42. Raper, R.L.; Reeves, D.W.; Shaw, J.N.; Santen, E.V.; Mask, P.L. Benefits of site specific subsoiling for cotton production in Coastal Plain soils. Soil Till. Res. 2007, 96, 174–181. [Google Scholar] [CrossRef]
Figure 1. Effects of different tillage practices on the green leaf area index (gLAI) in maize. Different small letters in the same growing stage indicate significant differences between tillage practices.
Figure 1. Effects of different tillage practices on the green leaf area index (gLAI) in maize. Different small letters in the same growing stage indicate significant differences between tillage practices.
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Figure 2. Effects of different tillage practices on the gLAI of different leaf layers in maize. Different small letters under the same leaf layer indicate significant differences between tillage practices.
Figure 2. Effects of different tillage practices on the gLAI of different leaf layers in maize. Different small letters under the same leaf layer indicate significant differences between tillage practices.
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Figure 3. Effects of different tillage practices on the Fv/Fm and Fv/Fo of summer maize at different growth stages. Different small letters under the same growth stage indicate significant differences between tillage practices.
Figure 3. Effects of different tillage practices on the Fv/Fm and Fv/Fo of summer maize at different growth stages. Different small letters under the same growth stage indicate significant differences between tillage practices.
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Figure 4. Aboveground dry matter accumulation (DMA)of different soil tillage practices. Different letters above the bars indicate significant differences between tillage practices.
Figure 4. Aboveground dry matter accumulation (DMA)of different soil tillage practices. Different letters above the bars indicate significant differences between tillage practices.
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Figure 5. Effects of different tillage methods on grain weight accumulation and grain-filling rate.
Figure 5. Effects of different tillage methods on grain weight accumulation and grain-filling rate.
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Figure 6. SWC in the 0–60 cm soil layer under different tillage practices at the big flare stage. Different small letters under the same soil layer indicate significant differences between tillage practices.
Figure 6. SWC in the 0–60 cm soil layer under different tillage practices at the big flare stage. Different small letters under the same soil layer indicate significant differences between tillage practices.
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Table 1. The monthly distribution of precipitation and mean temperature in 2016 and 2017.
Table 1. The monthly distribution of precipitation and mean temperature in 2016 and 2017.
Month20162017
Total Precipitation (mm)Mean Temperature (°C)Total Precipitation (mm)Mean Temperature (°C)
January49.43.460.95.4
February17.66.740.66.4
March57.411.968.410.8
April139.418.064.218.0
May12520.7123.623.1
June19124.649.925.7
July29528.863.530.8
August60.429.4243.228.1
September12924.4111.623.2
October268.117.897.516.4
November9611.210.816.4
December73.77.013.611.8
Amount during June and September675.4468.2
Total amount1502947.8
“−”Means there was no date.
Table 2. The nutrient conditions of the top 20 cm soil layer in 2016.
Table 2. The nutrient conditions of the top 20 cm soil layer in 2016.
Soil NutrientContent
Organic matter (g kg−1)21.6
Hydrolysable N (mg kg−1)118.4
Available phosphorus (mg kg−1)25.4
Available K (mg kg−1)269.6
Table 3. Soil bulk density and soil water content in 2016 and 2017.
Table 3. Soil bulk density and soil water content in 2016 and 2017.
Soil Depth (cm)
0–1010–2020–3030–4040–5050–60
2016SSSBD (g cm−3)1.47 c1.49 bc1.57 ab1.62 a1.55 ab1.51 b
SWC (%)19.27 b19.86 b20.24 ab21.69 a22.80 a23.61 a
RTSBD (g cm−3)1.57 a1.64 b1.58 a1.56 a1.56 a1.57 a
SWC (%)19.69 a19.47 a20.10 a21.45 a21.56 a22.30 a
2017SSSBD (g cm−3)1.46 c1.49 bc1.52 ab1.58 a1.51 ab1.49 b
SWC (%)14.52 b15.36 b16.75 a17.42 a17.96 a18.29 a
RTSBD (g cm−3)1.59 a1.62 a1.61 a1.58 a1.57 a1.57 a
SWC (%)14.53 a15.21 a15.89 a16.74 a16.87 a17.02 a
Values followed by different letters are significantly different in terms of soil bulk density (SBD) and soil water content (SWC) of different tillage practices.
Table 4. Effects of different tillage practices on the photosynthetic capacity of summer maize at different growth stages.
Table 4. Effects of different tillage practices on the photosynthetic capacity of summer maize at different growth stages.
Growth StageTreatment20162017
Pn
μmol m−2 s−1
gs
mmol m−2 s−1
ci
μmol mol−1
Tr
mmol m−2 s−1
LsPn
μmol m−2 s−1
gs
mmol m−2 s−1
ci
μmol mol−1
Tr
mmol m−2 s−1
Ls
Big Flare StageSS + I29.7 ± 2.1 a169.4 ± 25.9 b69.0 ± 15.4 c6.6 ± 0.8 a82.735.4 ± 1.6 a258.1 ± 30.4 a109.3 ± 18.3 a8.8 ± 0.7 a72.7
RT + I27.7 ± 1.3 ab168.6 ± 30.8 b112.4 ± 16.0 b5.4 ± 0.4 b71.933.5 ± 2.3 ab214.2 ± 43.8 b83.5 ± 22.1 b7.0 ± 1.0 ab79.1
SS + NI27.2 ± 1.8 ab144.7 ± 35.4 c157.0 ± 21.0 c5.6 ± 0.4 b60.734.2 ± 1.9 a244.7 ± 24.9 a112.2 ± 33.7 a5.6 ± 0.4 b72.0
RT + NI26.8 ± 1.4 b210.9 ± 36.8 a153.4 ± 16.8 a7.0 ± 0.7 a61.632.9 ± 2.6 b199.0 ± 28.0 b91.3 ± 16.2 b6.6 ± 0.6 b77.2
Silking StageSS + I36.5 ± 2.6 a398.1 ± 21.3 a179.2 ± 23.1 a5.5 ± 0.1 a55.232.1 ± 2.6 a327.0 ± 26.7 a171.2 ± 4.2 a4.8 ± 0.2 a57.2
RT + I30.5 ± 3.0 b281.1 ± 25.4 b172.3 ± 25.4 a3.8 ± 0.2 b56.927.8 ± 1.2 b251.8 ± 11.4 b171.0 ± 21.5 a3.6 ± 0.1 a57.2
SS + NI27.3 ± 1.5 bc145.2 ± 29.4 d142.1 ± 21.0 b2.5 ± 0.1 b64.527.7 ± 2.4 b212.2 ± 38.7 c158.1 ± 22.1 b3.8 ± 0.7 a60.5
RT + NI24.7 ± 2.7 c204.8 ± 30.1 c175.8 ± 23.8 a3.2 ± 0.3 b56.125.8 ± 1.8 b208.1 ± 38.1 c175.5 ± 12.4 a3.1 ± 0.4 a56.1
Mid-
filling Stage
SS + I31.7 ± 1.2 a241.6 ± 26.5 a144.4 ± 20.8 b4.3 ± 0.4 a63.933.4 ± 2.3 a281.6 ± 26.1 a241.8 ± 8.9 a4.3 ± 0.4 b39.5
RT + I24.0 ± 1.5 b163.6 ± 24.1 b153.0 ± 24.4 b2.2 ± 0.1 b61.726.9 ± 1.0 b234.9 ± 26.5 b195.2 ± 15.7 b2.9 ± 0.3 b51.2
SS + NI22.5 ± 1.1 b281.6 ± 27.1 a144.9 ± 23.4 a4.1 ± 0.2 a 63.827.9 ± 1.3 b239.0 ± 28.2 b178.1 ± 21.3 c6.3 ± 0.5 a55.5
RT + NI21.7 ± 1.2 b145.9 ± 22.5 b142.1 ± 22.0 b2.3 ± 0.3 b64.524.7 ± 1.1 c240.5 ± 31.2 b166.4 ± 20.0 c3.0 ± 0.5 b58.4
Values followed by different letters are significantly different in terms of the photosynthetic characteristics of different tillage practices.
Table 5. Effects of different tillage practices on the ΦPSII and qP of summer maize at different growth stages.
Table 5. Effects of different tillage practices on the ΦPSII and qP of summer maize at different growth stages.
Growth StageTreatment20162017
ΦPSIIqPΦPSIIqP
Big flare stageSS + I0.562 ± 0.006 a0.81 ± 0.008 a0.598 ± 0.008 a0.824 ± 0.006 a
RT + I0.515 ± 0.008 b0.772 ± 0.006 b0.583 ± 0.034 a0.881 ± 0.032 a
SS + NI0.573 ± 0.007 a0.798 ± 0.006 a0.589 ± 0.009 a0.842 ± 0.015 a
RT + NI0.542 ± 0.010 c0.731 ± 0.006 c0.577 ± 0.015 a0.808 ± 0.026 a
Silking stageSS + I0.620 ± 0.005 a0.812 ± 0.010 ab0.629 ± 0.005 a0.882 ± 0.023 a
RT + I0.601 ± 0.008 ab0.805 ± 0.009 ab0.626 ± 0.005 ab0.835 ± 0.016 ab
SS + NI0.615 ± 0.006 ab0.803 ± 0.006 b0.618 ± 0.001 ab0.814 ± 0.006 ab
RT + NI0.592 ± 0.009 b0.842 ± 0.018 a0.614 ± 0.002 b0.806 ± 0.005 b
Values followed by different letters are significantly different in terms of the ΦPSII and qP of different tillage practices.
Table 6. Dry matter translocation (DMT) from vegetative organs to grain and accumulation amount at the post silking stage.
Table 6. Dry matter translocation (DMT) from vegetative organs to grain and accumulation amount at the post silking stage.
TreatmentDMT before the Silking Stage
(kg ha−1)
Contribution of DMT before the Silking Stage to Grain (%)DMA at the Post Silking Stage
(kg ha−1)
CDMGW (%)
2016
SS + I1651.916.98147.283.1
RT + I1664.617.37976.782.7
SS + NI1807.018.87779.881.2
RT + NI2290.226.16499.973.9
2017
SS + I1784.816.88867.683.2
RT + I2247.222.57746.477.5
SS + NI3159.730.37256.369.7
RT + NI2573.930.75822.469.3
Table 7. Effects of different tillage methods on grain-filling characteristic parameters.
Table 7. Effects of different tillage methods on grain-filling characteristic parameters.
TreatmentSimulative EquationR2KTmVmTVaT1T2T3V1V2V3
SS + IY = 35.8164 / (1 + e(1.9395 − 0.114032x))0.988435.6217.011.0257.310.635.4623.1028.751.390.900.51
RT + IY = 32.7234 / (1 + e(1.9054 − 0.117603x))0.968332.7216.200.9655.280.595.0022.4027.871.380.840.48
SS + NIY = 33.4501 / (1 + e(2.1150 − 0.12783x))0.970833.4517.371.0255.100.616.5521.6326.921.080.890.51
RT + NIY = 31.7224 / (1 + e(2.0912 − 0.127825x))0.942331.7216.361.0152.310.616.0620.6125.651.110.890.51
CV (%) 2.883.012.133.495.292.142.147.213.013.01
Table 8. Effects of different tillage methods on grain yield.
Table 8. Effects of different tillage methods on grain yield.
TreatmentYield (kg ha−1)100-kernel Weight (g)Kernels Per YearYield Increase Rate (%)WUE (%)
2016
SS + I9003.4 ± 264.0 a38.0 ± 2.2 a490.7 ± 9.2 a17.714.0 ± 1.3 a
RT + I8418.1 ± 243.1 a37.9 ± 1.4 a452.9 ± 5.3 b10.113.0 ± 0.5ab
SS + NI8509.2 ± 156.9 a37. 9 ± 0.6 a465.3 ± 3.8 b11.213.7 ± 0.1 ab
RT + NI7649.3 ± 189.4 b37.1 ± 1.1 a401.9 ± 2.9 c12.4 ± 0.3 b
2017
SS + I9520.0 ± 141.1 a36.4 ± 1.0 a465.8 ± 19.5 a29.322.0 ± 0.3 a
RT + I8370.0 ± 511.2 b36.1 ± 1.5 a421.5 ± 44.5 b13.719.7 ± 0.4 b
SS + NI8100.0 ± 365.0 bc36.0 ± 0.8 a443.4 ± 32.2 a10.020.1 ± 0.9b
RT + NI7363.3 ± 296.0 c36.1 ± 0.5 a397.3 ± 21.9 b18.6 ± 0.6 b
Values followed by different small letters are significantly different at different tillage practices.

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Wu, W.; Wang, S.; Zhang, L.; Li, J.; Song, Y.; Peng, C.; Chen, X.; Jing, L.; Chen, H. Subsoiling Improves the Photosynthetic Characteristics of Leaves and Water Use Efficiency of Rainfed Summer Maize in the Southern Huang-Huai-Hai Plain of China. Agronomy 2020, 10, 465. https://doi.org/10.3390/agronomy10040465

AMA Style

Wu W, Wang S, Zhang L, Li J, Song Y, Peng C, Chen X, Jing L, Chen H. Subsoiling Improves the Photosynthetic Characteristics of Leaves and Water Use Efficiency of Rainfed Summer Maize in the Southern Huang-Huai-Hai Plain of China. Agronomy. 2020; 10(4):465. https://doi.org/10.3390/agronomy10040465

Chicago/Turabian Style

Wu, Wenming, Shiji Wang, Lin Zhang, Jincai Li, Youhong Song, Chen Peng, Xiang Chen, Lili Jing, and Hongjian Chen. 2020. "Subsoiling Improves the Photosynthetic Characteristics of Leaves and Water Use Efficiency of Rainfed Summer Maize in the Southern Huang-Huai-Hai Plain of China" Agronomy 10, no. 4: 465. https://doi.org/10.3390/agronomy10040465

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