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Article

Optimal Ridge–Furrow Ratio for Maximum Drought Resilience of Sunflower in Semi-Arid Region of China

1
College of Resources and Environmental Sciences, China Agricultural University, Beijing 100193, China
2
Wuchuan Scientific Observing and Experimental Station of Agro-Environment, Ministry of Agriculture, Wuchuan 011700, China
3
Integrated Water Management, Tetra Tech Inc, Fairfax, VA 22030, USA
*
Author to whom correspondence should be addressed.
Sustainability 2019, 11(15), 4047; https://doi.org/10.3390/su11154047
Submission received: 10 July 2019 / Revised: 19 July 2019 / Accepted: 24 July 2019 / Published: 26 July 2019
(This article belongs to the Section Sustainable Agriculture)

Abstract

:
Ridge–furrow planting is often applied in semi-arid regions to reduce the drought risk on crop yield under rain-fed conditions. Sunflower (Helianthus annuus L.) is widely planted in northern China and how to reduce the drought risk on sunflower production remains a significant issue. A three-year field experiment with seven treatments (a flat plot without mulching, three plastic film-mulching treatments and three non-film-mulching treatments with different ridge–furrow ratios (1.0 m:1.0 m, 1.0 m:0.5 m and 0.5 m:1.0 m)) was conducted to study the effects of the ridge–furrow rainwater harvesting system on the rain-fed sunflower. The results showed that the sunflowers in the film-mulched treatment with the larger ridge–furrow ratio (1.0 m:0.5 m) (M1R2) had greater growth advantage under drought conditions. In the dry year, M1R2 improved the yield and water use efficiency by 11.9%–107.5% and 13.8%–120.6%, respectively, and reduced the blight grain rate by 21.5%–32.5% with less evapotranspiration (ET) compared to other treatments. Based on the historical climatological data, the guarantee rate of sunflower water requirement for M1R2 was about 75%, while the guarantee rates for the other two film-mulched treatments were only about 40% and 50%. Based on the effects of drought resilience and the characteristics of precipitation, M1R2 is recommended to be the relatively optimal treatment for sunflower production in regions with similar climatic conditions to Wuchuan County in northern China.

1. Introduction

Crop growth and production in the semi-arid regions of China are restricted severely by water availability due to limited surface or ground water resources and limited rainfall with uneven temporal and spatial distribution [1,2,3,4]. The rising air temperature and more frequent and intense precipitation extremes have been observed and predicted under climate change projections in the northwestern semi-arid region of China [5,6,7]. This region has become warmer and drier with less groundwater resources [8,9,10], and the increasing variation of precipitation has led to fluctuating grain productions [11]. The projected changes of climate conditions increase the risks in rain-fed agricultural production [12]. To adapt to the warming and drying climate, highly effective utilization of precipitation is crucial for agricultural production in semi-arid areas.
The ridge–furrow rainwater harvesting system (RFRHS) has been proved to be an effective method to save water and increase water-use efficiency (WUE). The RFRHS usually results in high yields and high soil moisture; previous results showed that it improved the WUE of maize [13] by 9.2%, wheat [14] by 12%, potatoes [15] by 30% and alfalfa [16] by 70%. This is because that the RFRHS can change the micro-topography and thus cause the rain water redistribution in the field [17,18], and a mulched ridge can reduce evaporation and enhance soil temperature in the early growing season [19]. Due to its water retention and increments in yield, the RFRHS has been an important farming management measure for improving water use efficiency (WUE) and alleviating water shortages and has been widely used in the Loess Plateau and northwestern China [20,21,22].
The previous studies have shown that the ridge–furrow ratio and mulches are two major factors that impact crop yield, evapotranspiration (ET) and WUE in RFRHS [23,24,25,26]. For example, the optimal ridge–furrow ratio of Alfalfa was 35–36 cm:60 cm [27]. However, few studies have focused on the effects of RFRHS on oil seed crops like sunflower, not to mention optimal ridge–furrow ratio. As an important cash crop, sunflower is widely cultivated in semi-arid regions of northern China and is the second major oil seed crop in China. It is significant to study whether and how the RFRHS could efficiently improve the yield of the sunflower in semi-arid regions. In addition, previous studies mainly discussed the optimal RFRHS derived from a statistical approach [28,29,30]. The reduction of planting density caused by a wide ridge of RFRHS and whether the reduction would result in a decrease of total crop yield in some years were not discussed. However, decreasing planting density properly is necessary for increasing the drought resilience of crops in semi-arid regions during dry years.
The objective of this study was to examine the effects of ridge–furrow ratio in RFRHS on the sunflower growth and yield and to recommend the optimal ridge–furrow ratio for ensuring and stabilizing the sunflower yield in the semi-arid region, China.

2. Materials and Methods

2.1. Study Region

This study was conducted at the Scientific Experimental Station of Agro-environment (41°08′22.8″ N, 111°17′43.6″ E) in Wuchuan County, Inner Mongolia, which lies in the semi-arid region of northern China with typical temperate continental climate conditions [31]. Its elevation above sea level is 1589 m. The average annual precipitation is about 348 mm and 85.7% of which occurs from May to September with an uneven temporal–spatial distribution [32,33], and the average growth-period rainfall during 1961–2015 was 294.7 mm (Figure 1). The rainfall during the growth period (May–September) from 2013 to 2015 was 414.9 mm, 366.1 mm and 307.5 mm, respectively. In 2015, there was a severe drought in August, when the sunflower was in the flowering and maturity stage which are the critical stages of sunflower growth. Therefore, we defined 2015 as a dry year, and accordingly defined 2013 and 2014 as rainy years in this study. The soil type is chestnut soil (Haplic Krastazem, FAO) with a pH of 8.5, organic C of 10.3 g·kg−1, N of 0.79 g·kg−1, P of 0.45 g·kg−1, and K (total potassium) of 2.45 g·kg−1.

2.2. Experimental Design

This study focused on the ridge–furrow rainwater-harvesting system (RFRHS) in a sunflower field. A field experiment with seven treatment combinations was conducted in 2013–2015 (Figure 2), including control check (CK, a flat plot without mulching), plastic film-mulched with three ridge–furrow ratios treatments (M1R1 (1.0 m:1.0 m), M1R2 (1.0 m:0.5 m) and M1R0.5 (0.5 m:1.0 m)), and non-film-mulched with three ridge–furrow ratios treatments (M0R1 (1.0 m:1.0 m), M0R2 (1.0 m:0.5 m) and M0R0.5 (0.5 m:1.0 m)).
The experiments were in a randomized complete block design with three replicates for each treatment each year. Each plot was 8 m long and 6 m wide. The height of ridge was approximately 0.25 m, and the ridge surface was arched with a slope angle of approximately 40° (Figure 2). Sunflowers were planted in the furrows with the same row spacing (0.5 m) and plant distance in a row (0.5 m).
Fertilizer was applied to all the experiment plots before sowing with ammonium dihydrogen phosphate (75 kg·ha−1), urea (90 kg·ha−1) and potassium chloride (60 kg·ha−1), and no extra fertilizer was applied during the sunflower growth period. Sunflowers were sown in mid-May and harvested at the end of September each year. During the experiment, there was only one tillage before sowing and the stubble was retained in winter each year.
The soil moisture (10–100 cm) in every 10 cm layer was measured by a neutron probe (CPN-503DR). The oven drying method was used to measure the 0–10 cm soil moisture and calibrate the 10–100 cm soil moisture. The locations of measuring points were shown in Figure 2. The soil moisture in the ridges of M1R0.5 and M0R0.5 were not measured because the ridges were too narrow to setup the instrument. In order to protect the film on the ridge (M1R1 and M1R2), the 0–10 cm soil moisture was not measured in these treatments.
Dry biomass and leaf area were measured biweekly from the seedling stage. Three adjacent plants of each plot were measured as samples each time. Dry biomass was measured with the oven drying method (105 °C for 30 min, then 80 °C for 8h) and represented as dry-matter mass per plant (g/plant) in each plot. The plant leaf area was measured with the LI3000C when sampling. For yield measurement, 1/3 plants in each plot were collected at harvest time each year. The crop yield, hundred-grain weight, and blight grain rate were measured after drying. The crop yield data in 2013 were missing because all the sunflowers suffered wind damage.

2.3. Calculation Method

The total soil water storage (SWS, mm) at each measured point was calculated as Equation (1) [31]:
S W S = i = 1 n ( 0.1 ρ i θ i h i ) ,
where n is the number of soil layers, ρiθi and hi are the soil bulk density (g·cm−3), gravimetric soil water content (%), and soil layer thickness (cm) in the soil layer i, respectively.
The leaf area index (LAI) is calculated as the equation below:
LAI = l e a f   a r e a   ( m 2 ) a r e a   p e r   p l a n t   ( m 2 ) .
We calculated the evapotranspiration (ET, mm) of the film-mulched treatments by Equation (3), and calculated the ET of the no-mulched treatments and CK by Equation (5) [26]:
E T = P f × N 2 N 1 + N 2 + S W 0 S W 1 ,
P f = P + E r N 1 N 2 P ,
E T = P + S W 0 S W 1 ,
where P f is the precipitation in the planted furrows (mm); P is precipitation during the growth period (mm); N1 and N2 are the ridge width (m) and the furrow width (m) respectively; SW0 and SW1 are soil water storages (mm) when sowing and harvesting, respectively; Er is the runoff coefficient.
Water use efficiency (WUE, kg·mm−1·ha−1) is the ratio of the unit area yield (Y, kg·ha−1) to the ET (mm) [34]:
W U E = Y / E T .
The precipitation guarantee rate is an important index of the yield guarantee rate of water requirement. Sorting the historic annual precipitation in descending order, the precipitation guarantee rate could be calculated as Equation (7) [35].
P gr = N 100 % / ( n + 1 )
where P gr is the precipitation guarantee rate, N is the sequence number of the annual precipitation in descending order; n is the sample size of the annual precipitation sequence.

2.4. Statistical Analyses

Analyses of variance was conducted using SPSS17.0 to compare the effects of RFRHS. Least significant differences (LSD) were used to detect the mean differences between the treatments. In all cases, p < 0.05 was used to determine the significance.

3. Results

3.1. The Effects of Different Treatments on Plant Growth

The variations in average plant biomass per area (Ba) and plot leaf area index (LAI) during the growth period are shown in Table 1 and Table 2. As shown in Table 1, Ba in the film-mulched treatments were greater than that in non-mulched treatments and the CK. Among the three film-mulched treatments, the Ba of M1R0.5 increased by 31%~70% compared to the CK, better than that of M1R1 and M1R2 in 2013 and 2014 (rainy years). However, in 2015, the Ba of M1R2 was greater than that of M1R1 and M1R0.5 in August (82–112 days after sowing) when a severe drought happened.
For all treatments, the LAI at the same development stage in 2013 were greater than those in 2014 and then greater than those in 2015 (Table 2). There were no significant differences in LAI among all treatments in 2013. In 2014 and 2015, the film-mulched treatments improved LAI greatly relatively to non-mulched treatments and the CK. In the pre-growth stage, the LAI of M1R0.5 was greater than that of M1R1 and M1R2, but in the filling stage, the LAI of M1R2 was the largest. The LAI of M1R2 increased by 168%~197% compared to the CK in 2014 and 2015, which means that M1R2 could improve the crop yield compare to the CK.

3.2. The Effects of Different Treatments on Sunflower Yield

The actual sunflower yield (kg·ha−1) and yield components are shown in Table 3. The sunflower yields in film-mulched treatments were improved greatly compared with the CK. Yields in non-mulched treatments were not improved significantly compared with the CK. The average crop yield in the film-mulched treatments and non-mulched treatments were 3007 kg·ha−1 and 2155 kg·ha−1 in 2014, and were 1638 kg·ha−1 and 1125 kg·ha−1 in 2015, respectively. The crop yield of the film-mulched treatments M1R1, M1R2 and M1R0.5 were 18.9%–31.9%, 45.1%–56.9% and 37.2%–49.6% greater than that of the non-mulched treatments with the same ridge–furrow ratio.
Among the three film-mulched treatments, the yield of the treatment M1R0.5 was the greatest in 2014 (a rainy year) while the yield of the treatment M1R2 was the greatest in 2015 (a dry year). According to Table 3, the 100-grain weight of the treatment M1R2 was the greatest followed by the treatment M1R1. The differences of the 100-grain weight between all treatments were not significant in 2013 (a rainy year), but M1R2 improved 100-grain weight significantly compared to other treatments except M1R1 in 2014 and 2015. Meanwhile, M1R2 reduced the blight grain rate by approximately 34.5% and 37.9% compared to CK in 2015. In general, the RFRHS showed better positive impacts on sunflower yield in dry year (2015) compared with the rainy years (2013 and 2014) (Table 3).

3.3. The Effects of Different Treatments on Soil Water Storage (SWS)

The average SWS in 2014 was the highest (134 mm) and the average SWS in 2015 was the least (117 mm) (Figure 3). Comparing the variation trends of SWS (10–100 cm) in different treatments, the SWS in the film-mulched treatment with the greatest ridge–furrow ratio (M1R2) was the highest, while the SWS in the non-mulched treatment with the greatest ridge–furrow ratio (M0R2) was lowest. The SWS in M1R2 increased by 10.4%–13.8% compared to the CK in 2013–2015. The SWS in M0R2 reduced by 2.9%–7.0% compared to the CK in 2013–2015. The SWS in film-mulched treatments were 0.4%–13.8% higher than CK in 2013–2015. Before the squaring stage, the significant increases were 24 mm and 17 mm for M1R2 in 2014 and 2015, and the increase was 18 mm for M1R1 in 2014. According to the SWS on sowing day in 2014 and 2015, it could also imply that the film-mulched treatment with a wider ridge (M1R2) stored more water in soil before sowing when the plastic film was mulched during the fallow period (Figure 3).
Compared to the CK, the furrow-SWS in the film-mulched treatments increased (Figure 4a,b) and the ridge-SWS in them decreased in the upper 50 cm soil layer (Figure 4c). The furrow-SWS of the film-mulched treatments performed as M1R2 > M1R1 > M1R0.5. The differences of SWS in each layer between treatments were not significant in 2013, but in 2014 and 2015, the furrow-SWS in M1R2 were significantly increased by 33 mm and 22 mm compared to the furrow-SWS in the CK, respectively, while the differences between the other treatments were not significant.

3.4. The Effects of Different Treatments on ET and WUE

In general, ET in the film-mulched treatments decreased significantly comparing with the non-mulched treatments (Table 4). There were no significant differences in ET between the CK and other treatments in 2013. In 2014, the ET in M1R1, M0R1 and M0R2 were greater than the CK, while the ET in M1R0.5 was less compared to the CK. In 2015, the ET in all the film-mulched treatments decreased compared with the CK. The WUE was determined by the ratio of yield to ET. Table 4 also showed that the WUE in the film-mulched treatments M1R1, M1R2, and M1R0.5 were improved by 36.7%–39.5%, 45.1%–56.9% and 37.2%–49.6%, respectively, compared with non-mulched treatments with the same ridge–furrow ratio. The WUE in M1R1, M1R2 and M1R0.5 increased by 18.9%–92.6%, 31.6%–120.6% and 55.4%–71.0% compared with CK in 2014–2015, respectively. In 2014, a relatively rainy year, M1R0.5 had higher (18.1%–84.0%) WUE than other treatments. However, in the dry year (2015), M1R2 had the greatest WUE which improved WUE by 13.8%–120.6% compared with other treatments.

4. Discussion

4.1. The Film-Mulched Treatments Can Improve the Growth of Sunflower Significantly Due to the Higher SWS

The film-mulched treatments improved Y, Ba, LAI and WUE compared with the CK, while the non-mulching treatments did not. This was because film mulching resulted in more runoff to furrow [36], increased soil moisture storage and reduced the evaporation [37,38]. This finding is in accordance with the studies on maize, potatoes and wheat in Shaanxi Province and Gansu Province [33,39,40,41]. In this study, the film-mulched treatments with a wider ridge (M1R1 and M1R2) increased SWS (Figure 3 and Figure 4) compared to non-mulching treatments and CK, while M1R0.5 did not. A wider ridge with larger drainage area can accumulate and redistribute more rainfall into the furrow, therefore it reduces ineffective evaporation more and has a lower planting density [22]. In this experiment, the plastic film mulching during the fallow period resulted in higher SWS in the film-mulched treatments before sowing. It improved the plant growing condition and even the crop yield. This result was also in accordance with previous research [42].

4.2. The Output of Sunflower Is Determined by Precipitation and Ridge–Furrow Ratio

The film-mulched treatments with larger ridge–furrow ratio boosted growth of single plant, which resulted in greater 100-grain weight (Table 3). As the SWS was higher in M1R2 than other treatments (Figure 3), the single plant growth in M1R2 was boosted the most. In general, the Ba, LAI and crop yield of the film-mulched treatments were higher than the non-mulched treatments with the same ridge–furrow ratio. These results were similar to the results of the studies on maize [43,44], potato [45] and alfalfa [46]. However, the effect of treatments on the plant growth at plot scale were different in years with varied rainfall. In contrast to the above previous studies, treatments with a wider film-mulched ridge did not have greater yields than those with smaller ridges in rainy years. The treatment M1R0.5 had the better performance in rainy years (2013 and 2014), while the treatment M1R2 performed better in the dry year (2015) (Table 1, Table 2 and Table 3). It means that the growth advantages of the film-mulched treatments were greater in dry years comparing to the CK, especially the growth advantages in the treatments with larger ridge–furrow ratio. The main reason for this was the wider ridge reduced the planting area, and the increment due to the increase of crop production per plant cannot offset the decrease due to the reduction of plant area in rainy years. This result illustrates that the optimal ridge furrow ratio may be different with different precipitation patterns.
In this experiment, a large ridge–furrow ratio meant a small cultivated density, and the varied effects of RFRHS under different precipitation patterns led to the inter-annual changes in sunflower growth and production (Table 3). In 2013, there was comparatively enough rainfall for the water requirement of sunflower (Figure 1). This may result in the non-significant differences between the treatments in 2013 (Table 1, Table 2 and Table 3). In 2014, the single-plant growing advantage in treatment with wider ridge could not counteract the yield reduction caused by a smaller cultivated area in rainy years. Thus, the sunflower yield and WUE in M1R0.5 were higher than M1R2 (Table 3 and Table 4). In August 2015, the rainfall was not enough to satisfy the normal plant growth (Figure 1), and the film-mulched treatment M1R2 with the widest ridge maintained more available soil water and produced the largest crop yield and highest WUE (Table 3 and Table 4). It meant that the effect of RFRHS with larger ridge–furrow ratio on the sunflower yield was more effective in dry year. This result was consistent with the review of Bouma et al. [47] which point out that RFRHS is especially effective in low rainfall years. For sunflower at the study region, an appropriate small ridge–furrow ratio film-mulched treatment could have greater crop yield and WUE in rainy years, but a larger ridge–furrow ratio film-mulched treatment is recommended in dry years. Thus, the appropriate ridge–furrow ratio should be determined by considering both the influence of production increasing and the precipitation characteristics.

4.3. The Optimum Ridge–Furrow Ratio for Stable Sunflower Yield

Plant growth and production were closely dependent on precipitation at different growth stages [48]. According to previous studies, the average water requirements of sunflower in the growing season was approximately 400 mm, and the water requirement in seeding stage (mid-to-late May), elongation stage (early June to early July), squaring stage (July), flowering and filling stage (August) and ripening stage (September) was approximately 28 mm, 58 mm, 152 mm, 120 mm and 50 mm, respectively [49]. According to the precipitation guarantee rate, the accumulated frequency of precipitation (Figure 5), the water requirement in crucial stages (squaring stage, flowering and filling stage) could not be met in most years in this and similar semi-arid regions. There is severe drought risk in the study region. Maximizing the resilience of drought is crucial for ensuring the stability of the crop yields at this region. Under dry conditions, the film-mulched RFRHS could improve the effective precipitation markedly [50]. Therefore, the implementation of film-mulched RFRHS is recommended.
Based on the water requirement at each stage, the accumulated frequency of enough precipitation in M1R1, M1R2 and M1R0.5 is about 50%, 75% and 40%, respectively. In this experiment, treatment M1R2 reduced water consumption, greatly improved the WUE in the dry year (Table 4) and improved the yield and the grain quality compared to the CK in the rainy year (2014) and the dry year (2015) (Table 1). In addition, the increase of Ba, LAI and yield in M1R2 in 2015 proved that the treatment M1R2 is more resilient to droughts similar to that in August, 2015. Thus, a large ridge–furrow ratio RFRHS would be more practical for agricultural production in this study region. M1R2 (the film-mulching treatment with the ridge–furrow ratio 1.0 m:0.5 m) could be recommended as a better sunflower rainwater-harvesting pattern in Wuchuan as well as similar climatic regions where the precipitation guarantee rate of 300 mm is below 75% during the sunflower growing season. If the climate in some semi-arid regions is relatively wet, a narrower film-mulching ridge should be considered for farmers. Specifically, when the growth-season precipitation guarantee rate of 320 mm is above 75%, M1R0.5 (the film-mulching treatment with the ridge–furrow ratio 1.0 m:0.5 m) could be recommended in these semi-arid regions.
There were still some deficiencies and limitations in this study. The experiment was conducted under limited precipitation conditions, and the data collected by this experiment were not enough to establish statistical models about the relationship between precipitation and the ridge–furrow ratio. Further study is needed to investigate the quantitative relationship between ridge–furrow ratio and precipitation for the RFRHS extension under various precipitation conditions.

5. Conclusions

In this study, the results of the three-year field experiment confirmed that the rainwater harvesting system with film-mulching and with optimal ridge and furrow ratio is an effective way to improve drought resilience of crops, thus ensure yields in the semi-arid area in northern China. The film-mulched treatments increased the soil moisture, LAI, dry biomass and yield of sunflower. A small ridge–furrow ratio rainwater harvesting system with film-mulching is good for a relatively high yield in a rainy year, while a larger ridge–furrow ratio is recommended in a dry year. The appropriate ridge–furrow ratio should be determined by considering both the effect of production increasing and the precipitation characteristics in the study region. In this study, the film-mulched RFRHS with the ridge–furrow ratio 1.0 m:0.5 m (M1R2) ensured an adequate supply of moisture to maintain and even increase yield. In the regions like Wuchuan where the precipitation guarantee rate of 300 mm is below 75%, the RFRHS M1R2 could be recommended to be an optimal sunflower farming practice. However, when the growth-season precipitation guarantee rate of 320 mm is above 75%, M1R0.5 (the film-mulching treatment with the ridge–furrow ratio 1.0 m:0.5 m) is more proper in these semi-arid regions.

Author Contributions

Methodology, Y.P., X.P., and Q.H.; Formal Analysis, Y.P. and Z.P.; Investigation, Y.P., J.W., and G.L.; Data Curation, Y.P.; Writing – Original Draft Preparation, Y.P.; Writing – Review & Editing, Y.P., Z.T., J.W, and Z.P.; Visualization, Y.P.; Supervision, Z.P.

Funding

This study was supported by the National Natural Science Foundation of China (No.41871086) and the National Key R&D Program of China (2017YFD0300906-05, 2018YFD0300502, 2018YFA0606303).

Conflicts of Interest

The authors declare no conflict of interest.

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Figure 1. Monthly mean temperature (°C) and rainfall (mm) in May–September in 2013, 2014, 2015, and the long-term (1961–2010) averages at the experimental station.
Figure 1. Monthly mean temperature (°C) and rainfall (mm) in May–September in 2013, 2014, 2015, and the long-term (1961–2010) averages at the experimental station.
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Figure 2. The different experimental ridge–furrow ratio treatments and the measuring points of soil moisture.
Figure 2. The different experimental ridge–furrow ratio treatments and the measuring points of soil moisture.
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Figure 3. Soil water content (10–100 cm) (mm) in different treatments during the growth period in 2013–2015. Error bars are the LSD at p = 0.05.
Figure 3. Soil water content (10–100 cm) (mm) in different treatments during the growth period in 2013–2015. Error bars are the LSD at p = 0.05.
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Figure 4. Profile of soil moisture in the upper 0–100 cm layer at increments in 10 cm at different observation points in all treatments. The observation points included (a) the point in the middle of the furrow, (b) the point at the ridge–furrow junction and (c) the point in the middle of the ridge. Error bars are the least significant differences (LSD) at p = 0.05.
Figure 4. Profile of soil moisture in the upper 0–100 cm layer at increments in 10 cm at different observation points in all treatments. The observation points included (a) the point in the middle of the furrow, (b) the point at the ridge–furrow junction and (c) the point in the middle of the ridge. Error bars are the least significant differences (LSD) at p = 0.05.
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Figure 5. The precipitation guarantee rate in July, August and the total year.
Figure 5. The precipitation guarantee rate in July, August and the total year.
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Table 1. The average plant biomass per area (Ba, g·m−2) under the different rainwater harvesting treatments during 2013–2015.
Table 1. The average plant biomass per area (Ba, g·m−2) under the different rainwater harvesting treatments during 2013–2015.
Growth StageElongation StageSquaring StageFlowering and Filling Stage
2013 days after sowing46 587390
M1R152ab 265a625ab922bc
M0R149abc 189b593ab795cd
M1R244bc 234ab577ab909bc
M0R236c 193b516b674d
M1R0.559a 276a754a1178a
M0R0.546ac 252a705a1067ab
CK48abc 198a573ab893bc
2014 days after sowing3751658095110
M1R17.6b80bc343ab538ab832ab896bc
M0R16.7b63c218cd454bc550c722cd
M1R26.9b71c313abc593ab936a1021ac
M0R26.5b48c160d309c505c618d
M1R0.513.3a110a385a700a1012a1182a
M0R0.59.5ab104ab297abc472bc603bc652cd
CK6.0b77bc272bc516b630bc696cd
2015 days after sowing3550658296112
M1R12.9b31ab138a428a672ab691ab
M0R12.1c13c75b232b305c380c
M1R22.7b28b142a474a756a733a
M0R21.5d12c57b198b286c344c
M1R0.53.7a38a162a466a592b576b
M0R0.52.3c16c75b222b328c349c
CK2.3c15c74b257b346c298c
Note: values within a column and in one year with different letters were significantly different (p < 0.05).
Table 2. The leaf area index (LAI) under the different rainwater harvesting treatments in 2013–2015.
Table 2. The leaf area index (LAI) under the different rainwater harvesting treatments in 2013–2015.
Growth StageElongation StageSquaring StageFlowering and Filling Stage
2013 days after sowing46 587390
M1R10.45ab 1.87a2.41ab2.56a
M0R10.41abc 1.51a2.22abc2.33a
M1R20.37bc 1.93a2.41bc2.61a
M0R20.33c 1.65a1.95c2.18a
M1R0.50.50a 1.97a2.46a2.69a
M0R0.50.42abc 1.76a2.27abc2.42a
CK0.41abc 1.77a2.40abc2.52a
2014 days after sowing3751658095110
M1R10.09b0.73ab1.44ab1.50ab1.28ab0.72a
M0R10.06b0.59ab0.87cd1.17bc0.84c0.39bc
M1R20.07b0.64ab1.30ab1.54ab1.46a0.83a
M0R20.07b0.40b0.74d0.88c0.78c0.38bc
M1R0.50.14a0.93a1.55a1.88a1.58a0.62ab
M0R0.50.09b0.90a1.23ab1.29bc0.89c0.36bc
CK0.10ab0.67ab1.16bc1.33b0.98bc0.31c
2015 days after sowing3550658296112
M1R10.03b0.21b0.65a1.10a0.89a0.60ab
M0R10.02c0.09c0.31b0.61b0.42b0.31bc
M1R20.03b0.20b0.65a1.09a1.00a0.67a
M0R20.01d0.09c0.28b0.56b0.42b0.23c
M1R0.50.04a0.27a0.69a1.09a0.88a0.35bc
M0R0.50.02c0.12c0.36b0.59b0.42b0.26c
CK0.02c0.11c0.34b0.68b0.50b0.23c
Note: values within a column and in one year with different letters were significantly different (p < 0.05).
Table 3. The actual yield of sunflower (kg·ha-1) under the different rainwater harvesting treatments in 2013–2015.
Table 3. The actual yield of sunflower (kg·ha-1) under the different rainwater harvesting treatments in 2013–2015.
TreatmentsYield (kg·ha−1)Variation Compared to CK (%)100-Grain Weight (g)Variation Compared to CK (%)Blighted Grain Rate (%)
2013
M1R1————17.1 ± 1.0 a0.915.2
M0R1————16.8 ± 1.4 a–1.216.1
M1R2————18.4 ± 0.8 a8.517.8
M0R2————16.8 ± 0.3 a–0.722.3
M1R0.5————16.8 ± 0.2 a–0.915.6
M0R0.5————16.8 ± 2.0 a–0.920.6
CK————17.0 ± 1.3 a——15.8
2014
M1R12742 ± 101bc22.918.1 ± 0.3 ab58.319.5 *
M0R12005 ± 423d–10.113.8 ± 1.2 cd20.822.8
M1R22971 ± 26ab33.119.4 ± 1.5 a70.220.0 *
M0R22047 ± 181d–8.314.8 ± 2.4 bc29.325.6
M1R0.53310 ± 154a48.315.4 ± 1.3 bc34.721.6
M0R0.52413 ± 84bcd8.113.4 ± 0.4 cd17.522.9
CK2231 ± 233cd——11.4 ± 1.0 d——26.9
2015
M1R11628 ± 195ab85.415.1 ± 0.9 ab50.929.7
M0R11234 ± 369abc40.612.7 ± 1.1 cd26.830.8
M1R21822 ± 252a107.516.3 ± 0.6 a62.823.3 *
M0R21161 ± 324abc32.214.8 ± 0.5 bc47.333.2
M1R0.51465 ± 28abc66.912.7 ± 0.8 bc27.232.8
M0R0.5979 ± 12bc11.510.6 ± 1.3 cd5.834.5
CK878 ± 380c——10.0 ± 0.8 d31.3
Note: Values within a column and in one year with different letters were significantly different (p < 0.05). * means this value was significantly different compared to CK (p < 0.05).
Table 4. The evapotranspiration (ET) and water-use efficiency (WUE) of sunflower under the different rainwater harvesting treatments in 2013–2015.
Table 4. The evapotranspiration (ET) and water-use efficiency (WUE) of sunflower under the different rainwater harvesting treatments in 2013–2015.
TreatmentsPrecipitation (mm)ΔW (mm)ET (mm)WUE (kg·mm−1·ha−1)
2013
M1R1414.975.1463.9——
M0R1414.959.5474.4——
M1R2414.957.6444.8——
M0R2414.964.2479.1——
M1R0.5414.968.8469.9——
M0R0.5414.991.0505.9——
CK414.960.4475.3——
2014
M1R1366.124.1371.9 *7.4 *
M0R1366.116.9383.0 **5.2
M1R2366.122.4364.18.2 **
M0R2366.115.9382.0 **5.4
M1R0.5366.1–10.3343.6 **9.6 **
M0R0.5366.1–10.4355.76.8
CK366.1–6.2360.06.2
2015
M1R1307.5–10.5281.7 **5.8 *
M0R1307.5–10.1297.44.2
M1R2307.5–12.0275.0 **6.6 **
M0R2307.5–12.1295.43.9
M1R0.5307.5–12.3284.9 *5.1*
M0R0.5307.5–12.9294.63.3
CK307.5–14.2293.33.0
Note: * means this value was significantly different from it in the CK (p < 0.05), and ** means the different was very significant (p < 0.01).

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Pan, Y.; Pan, X.; Zi, T.; Hu, Q.; Wang, J.; Han, G.; Wang, J.; Pan, Z. Optimal Ridge–Furrow Ratio for Maximum Drought Resilience of Sunflower in Semi-Arid Region of China. Sustainability 2019, 11, 4047. https://doi.org/10.3390/su11154047

AMA Style

Pan Y, Pan X, Zi T, Hu Q, Wang J, Han G, Wang J, Pan Z. Optimal Ridge–Furrow Ratio for Maximum Drought Resilience of Sunflower in Semi-Arid Region of China. Sustainability. 2019; 11(15):4047. https://doi.org/10.3390/su11154047

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Pan, Yuying, Xuebiao Pan, Tan Zi, Qi Hu, Jing Wang, Guolin Han, Jialin Wang, and Zhihua Pan. 2019. "Optimal Ridge–Furrow Ratio for Maximum Drought Resilience of Sunflower in Semi-Arid Region of China" Sustainability 11, no. 15: 4047. https://doi.org/10.3390/su11154047

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