Next Article in Journal
A Novel Multipurpose Self-Irrigated Green Roof with Innovative Drainage Layer
Previous Article in Journal
Water Cycles and Geothermal Processes in a Volcanic Crater Lake
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Evaluating Optimum Limited Irrigation and Integrated Nutrient Management Strategies for Wheat Growth, Yield and Quality

1
Department of Agronomy, Faculty of Agriculture and Environment, The Islamia University of Bahawalpur, Bahawalpur 63100, Pakistan
2
Department of Agronomy, University of Agriculture, Faisalabad 38040, Pakistan
3
Department of Engineering and Engineering Technology, Metropolitan State University of Denver, Denver, CO 80217, USA
4
Department of Botany, The Islamia University of Bahawalpur, Bahawalpur 63100, Pakistan
5
College of Agronomy, Northwest A & F University, Yangling, Xianyang 712100, China
6
Department of Agroforestry and Environmental Science, Sylhet Agricultural University, Sylhet 3100, Bangladesh
7
Department of Agronomy, Faculty of Agriculture, University of Kafrelsheikh, Kafrel-Sheikh 33516, Egypt
*
Authors to whom correspondence should be addressed.
Hydrology 2023, 10(3), 56; https://doi.org/10.3390/hydrology10030056
Submission received: 10 February 2023 / Revised: 23 February 2023 / Accepted: 24 February 2023 / Published: 25 February 2023
(This article belongs to the Special Issue Advances in Soil Moisture Dynamics across Scales)

Abstract

:
Agricultural productivity is significantly influenced by the restricted availability of irrigation water and poor soil health. To assess the influence of different potential soil moisture deficit (PSMD) regimes and integrated nutrient levels on the growth, yield, and quality of wheat, an experiment was carried out at the research area of the University of Agriculture, Faisalabad. The experiment includes three levels of PSMD (I1: 25 mm PSMD, I2: 50 mm PSMD, and I3: 75 mm PSMD) and four integrated nutrition levels (N1: 50% organic manure + 50% Inorganic NPK, N2: 75% organic manure + 25% inorganic NPK, N3: 100% application of organic manure, and N4: 100% application of inorganic NPK). Results of the experiment revealed that maximum grain yield (4.78 t ha−1) was obtained as a result of irrigation at 50 mm PSMD with the combined use of organic and inorganic sources in equal proportions. In contrast, the minimum yield was observed at I3: 75 mm PSMD with 100% application of organic manure. The highest plant height (99.11 cm), fertile tillers (284.4), 1000-grain weight (44.48 g), biological yield (14.82 t ha−1), radiation use efficiency for grain yield (RUEGY) (5.71 g MJ−1), and radiation use efficiency for total dry matter (RUETDM) (2.15 g MJ−1) were observed under N1: 50% organic manure with 50% inorganic NPK treatment. The highest value of these parameters was also observed in I2 (50 mm PSMD). The results of this study can be extended to arid and semi-arid regions, where deficit irrigation is a key strategy to address water crises and to meet sustainable development goals.

1. Introduction

Wheat (Triticum aestivum L.) is a major global dietary source, providing more than 70% of daily calories to people living in remote areas. It is highly nutritious, with substantial amounts of carbohydrates, minerals, proteins, and vitamins [1]. Around 21% of the world’s food needs are met through wheat and it is grown on more than 200 million hectares [2]. Water is a vital component for living beings and its availability is decreasing over time [3,4]. In plants, water has several functions, such as uptake from roots and assimilates translocation, maintaining cell turgidity and serving as a medium for biochemical reactions, physiological processes, and sequestration of salts and toxic elements inside or outside of the plant tissues [5,6,7]. One of the major difficulties faced in wheat production is the depletion of irrigation water resources at an alarming rate [8]. Photosynthates production is highly sensitive to water deficit, and ultimately affects grain development [9]. In this scenario, the emphasis should switch from increasing the cropped area to increasing production per unit of water [10]. In Pakistan, wheat crop is challenged due to drought stress and the seasonal closure of canals. This scarcity can be adjusted by rescheduling irrigation (decreasing the amount of water applied to crop) so that it does not disturb grain production significantly [11,12]. Under limited water conditions, deficit irrigation is a useful approach; it has several irrigation practices, such as potential soil moisture deficit (PSMD), that use low levels of irrigation water without adversely affecting crop production. The basic aim of this irrigation scheduling approach is to enhance crop water use efficiency by using less water [13,14].
Inequitable and consistent use of mineral fertilizers in modern farming has led to the reduction of nutrients in soil solution that has harmful impacts on soil fertility and productivity [15]. The sole use of inorganic or organic fertilizers has both positive and negative effects on plant growth, nutrient availability, and soil health. Organic fertilizers improve the physical and biological activities of the soil, but they are relatively low in nutrients, so larger amounts are needed for plant growth [16]. Moreover, their availability to plants is slow [17]. However, inorganic fertilizer is usually immediate used and contains all the necessary nutrients that are directly available to plants. But the continuous use of inorganic fertilizers themselves causes soil organic matter degradation, soil acidity, and environmental pollution [15]. Therefore, the integration of synthetic fertilizers and organic manures in proper proportions can be a beneficial and sustainable practice for better production and soil quality improvement [18]. Excessive dependence of inorganic fertilizers and ignorance of organic inputs under intensive cropping systems leads to degraded soil health and sub-optimal crop productivity [19]. Moreover, excessive use of chemical fertilizers results in contamination of groundwater [20,21]. Organic manure, along with chemical fertilizers, can make an impact on building soil fertility status and boosting crop productivity [22]. With integrated nutrient management, the organic matter of soil increases slowly; it may take several years but its contribution in boosting production is long-term and on a sustained basis [23]. Moreover, it aims to maintain the soil fertility and plant nutrient supply at an optimum level for sustaining the desired crop productivity through optimization of the benefits from all possible sources of plant nutrients in an integrated manner [24]. Therefore, the present study was planned to determine the best suitable combination of integrated nutrients and PSMD level to achieve higher growth and yield of wheat and to explore PSMD as an alternative approach for irrigation scheduling in wheat.

2. Materials and Methods

The proposed trial was conducted at the research area of the University of Agriculture, Faisalabad, Pakistan, during 2014–2015. The experimental area is located at 31°25′ North latitude, 73°04′ East longitudes, 184 m altitude, and has a semi-arid climate. The prescribed experimental area was preferred due to canal water availability. Before initiating the experiment, soil samples (0–30 cm) were collected from the experimental site. Different soil parameters were assessed for samples. Samples were sieved through a 2-mm sieve after gently mixing, drying, and grinding. The soil physiochemical traits and nutrient status were analyzed using the protocol of George et al. [25] and presented in Table 1, along with a chemical analysis of farmyard manure and inorganic fertilizers. The mean monthly temperature and rainfall are described in Figure 1.

2.1. Experimental Treatments and Design

The proposed study was laid out in a randomized complete block design with a split-plot arrangement and with three replications. The experiment has two factors: irrigation levels in main plots and integrated nutrients in sub-plots. Irrigation has three PSMD levels (I1 = Irrigation at 25 mm PSMD, I2 = Irrigation at 50 mm PSMD, and I3 = Irrigation at 75 mm PSMD), while integrated nutrition is comprised of four levels (N1 = 50% organic manure (FYM) + 50% inorganic (NPK); N2 = 75% organic manure (FYM) + 25% inorganic (NPK); N3 = 100% organic manure (FYM), and N4 = 100% inorganic NPK).

2.2. Crop Husbandry

Seed of wheat cv. Galaxy-2013 was acquired from Wheat Research Institute, Faisalabad, and cultivated using the recommended seed rate at 100 kg ha−1 with a hand drill in rows that were 22.5 cm apart. The recommended doses of phosphorus (P) and potassium (K) were applied at sowing time. A half dose of nitrogen (N) was applied at the time of sowing and half was applied during the first irrigation. The sources of N, P, and K were urea, di-ammonium sulfate (DAP), and muriate of potash (MOP), respectively. All other cultural operations, such as intercultural practices, weeding, and plant protection measures, were kept constant in all treatments. For the application of irrigation, 25, 50, and 75 mm PSMD were referred to as standard. A standard model, “CROPWAT”, was used to calculate penman’s potential evapotranspiration. This model is developed by FAO [26]. It calculates that the total amount of water irrigated to crop is equal to the difference between the sum of rainfall and irrigation and potential evapotranspiration.
D =   ETo     ( I   +   R )
where D is deficit (mm), ETo is evapotranspiration, R is rainfall, and I is irrigation.
ETo was calculated by:
ETo =   Epan   ×   Kp
where Epan is equal to the mean daily pan evaporation and Kp is equal to the pan coefficient.
A cut-throat flume was used to calculate the discharge of the watercourse (Table 2) as follows:
t   =   A   ×   d / Q
where t is time in seconds for a pre-determined amount of irrigation, A corresponds to the area of the plot to be irrigated (m2), d is the depth of water to be applied (m), and Q is the discharge of the cut-throat flume (m3 sec−1).

2.3. Procedure to Record the Observations

Observations regarding plant height, spike-bearing tillers, grains per spike, 1000-grain weight, grain yield, and biological yield were recorded according to standard procedures. Data regarding radiation use efficiency for total dry matter (RUETDM gMJ−1) and grain yield (RUEGY gMJ−1) were recorded according to the formula [27]:
RUETDM = TDM / Sa
RUEGY = Grain   yield / Sa
where ‘TDM’ is total dry matter and ‘Sa’ is the amount of intercepted photosynthetically active radiations as calculated by multiplying ‘Fi’ with ‘Si’, where ‘Fi’ is a fraction of intercepted radiations and ‘Si’ is the daily incident photosynthetically active radiation [28].
Sa = Fi   ×   Si  
‘Fi’ was calculated by Beer’s law:
Fi = 1 exp   ( k   ×   LAI )
‘K’ is a coefficient whose value for wheat is 0.4 [29]. Furthermore, for the calculation of ‘Si’, there is a need to calculate solar radiations:
Si = Total   Rs / 2
Rs is equal to solar radiations that can be calculated by:
Rs = [ a + b   ( n / N ) ] ×   Ra
where ‘a’ and ‘b’ are constants and have values of 0.25 and 0.5, respectively, n is equal to actual sunshine hours while N is the maximum possible sunshine hours, and Ra is extra-terrestrial radiations.
Measurement of leaf area was performed at 15-day intervals by randomly selecting ten plants from every subplot. The first sample was taken 25 days after sowing. In every sampling, fresh weight of separated leaves was measured, and 10 g of sub-sample was used to measure leaf area. Leaf area was calculated using the following method.
Leaf   area = Length   ×   Width   ×   K
Leaf area index (LAI) was calculated by the following formula [30]:
Leaf   area   index = Leaf   area / Land   area
Leaf area duration (LAD) was measured as [31]:
LAD = ( LAI 1 +   LAI 2 ) × ( T 2   T 1 ) / 2
Crop growth rate (CGR) was calculated by the method of Beadle, [32]
CGR = ( W 2     W 1 ) / ( T 2     T 1 )
where W1 and W2 were the total dry weights harvested at times T1 and T2, respectively.
Total dry matter was determined after a regular interval of 15 days through a random selection of plants from each treatment and they were dried at 70 °C until constant weight was achieved, then they were weighed. Regarding quality characteristics, protein contents were determined using the Kjeldahl method [33]. Percent crude protein was determined using the following formula:
Crude   Protein   ( % ) = ( V 1     V 2 )   N / 100 W   × 6.25 × 14 × 100
where ‘V1’ is a sample of the titration, ‘V2’ is the titration of volume, ‘N’ is the normality of standardized sulfuric acid, and ‘W’ is the weight of the sample. The starch content of wheat was estimated using an Omeg Analyzer G (Kernelyzer, Germany). Wheat grains were placed in a machine sample hopper using an 18-mm sample spacer and digital reading of starch was noted on the instrument display [34].

2.4. Statistical Analysis

The recorded data were statistically analyzed using Fisher’s analysis of variance technique. Upon the signing of the treatments’ effect, the least significance difference (LSD) was used to compare the treatment means [35].

3. Results

Water deficit levels and integrated nutrition significantly affected the LAI of wheat and LAI steadily increased from the start until a maximum point was reached, attained 90 days after sowing; it then declined gradually. PSMD levels significantly affected the LAI when irrigation was applied at I2 (50 mm PSMD); this application most improved the LAI of wheat during the season, followed by treatment I1 (25 mm PSMD); the lowest LAI response was observed in the case of I3 (75 mm PSMD) (Figure 2A). In case of integrated nutrient levels, N1 treatment substantially improved the LAI during the whole season, and it was highest 90 days after sowing, followed by N4 as the next highest. On the other hand, the lowest LAI was recorded in treatment N3. The sole application of organic manure (N3) significantly reduced the LAI when compared to the combined use of organic and inorganic fertilizers (N1) (Figure 2B). Among deficit levels, a higher deficit leads to a considerable decline in LAI; among integrated nutrient levels, sole use of organic manure leads to low LAI of wheat. A balanced combination of organic and inorganic manure results in the highest LAI. LAD is the duration for which actual sunlight is absorbed by the leaf area of a crop. LAD was significantly affected by water deficit and integrated nutrition levels and the highest LAD (during the whole season) was observed with I2 treatment; treatment I3 resulted in the lowest LAD (Figure 3A). Among integrated nutrient levels, the highest LAD was observed with N1. In case of N3, there was lesser vegetative growth; as a result, the lowest LAD was recorded (Figure 3B). CGR also showed a similar trend and irrigation regimes differed significantly. Irrigation treatment I2 exhibited the highest CGR; the lowest CGR was recorded at a higher deficit level (I3) (Figure 4A). Among integrated nutrient levels, N1 resulted in higher CGR levels than other treatments (Figure 4B). The seasonal response of TDM was significantly influenced by irrigation regimes and different nutrition levels. The lowest TDM accumulation was noticed 25 days after sowing; after this point, it increased gradually, and it was highest after 90 days of sowing. Irrigation treatment I2 attained the highest TDM accumulation, and these results were statistically at par with treatment I1 (Figure 5A). Experimental plots treated with inorganic fertilizers in combination with FYM showed higher performance when compared to other treatments. The addition of 50% inorganic NPK and 50% FYM (N1) achieved the highest TDM accumulation; this is in contrast to the N3, that gave the lowest TDM accumulation (Figure 5B).
Plant height was significantly affected by both studied factors (irrigation levels and integrated nutrition) (Table 3) and the highest plant height (98.41 cm) was observed in I2, followed by treatment I1 (97.50 cm). Integrated nutrient levels differed significantly; it was highest with N4 treatment (103.12 cm), followed by the N1 treatment (99.11 cm). The lowest plant height was observed in treatment N3. The interaction of both factors for plant height was found to be significant and the highest plant height was noticed in the combination of I2 × N4. PSMD, integrated nutrient management, and the interaction of both factors showed a significant effect on yield and yield causative attributes. The significance of fertile tillers is evident from the fact that it directly influences grain production. The data regarding the spike-bearing tillers m−2, as influenced by different deficit and integrated nutrient levels, are presented in Table 4. Among PSMD levels, the highest number of fertile tillers (282.25) was obtained in I2 and the lowest number of productive tillers (222.83) was recorded in I3. Regarding the response of integrated nutrients, the highest spike-bearing plants (284.44) were obtained in N1, followed by N4 (261.22). The minimum number of productive tillers (220.0) were obtained in N3. The interactive effect of treatments for productive tillers was also significant and the highest number of productive tillers (319.0) were recorded in I2 × N1. Grains per spike is an important yield contributing factor and its data are present in Table 4. Analysis of variance showed that water deficit and nutrition levels significantly differed and irrigation at I2 produced the highest number of grains per spike (44.47), followed by I1 (40.72) and I3 (39.95). Individual comparison of treatment means for integrated nutrients revealed that the highest number of grains per spike (44.81) was recorded with N1, followed by N4 treatment (42.18). The lowest number of grains per spike (39.05) was noticed in treatment N3. The interactive response I2 × N1 produced the highest number of grains per spike (49.73) (Table 4).
In PSMD levels, the highest 1000-grain weight (44.43 g) was obtained with treatment I2; the lowest weight (36.72 g) was observed with treatment I3 (Table 4). Various levels of integrated nutrients responded significantly; the highest 1000-grain weight (44.48 g) was found with N1, followed by N4 and N2. The lowest 1000-grain weight (35.97 g) was recorded in treatment N3. The total biomass produced by a crop from a unit area is termed as biological yield. This was significantly affected by deficit levels, integrated nutrients, and their interaction. The highest biomass (13.93 t ha−1) was attained with treatment I2 and minimum biological yield (13.39 t ha−1) was observed in treatment I3. Individual comparison of treatment means regarding integrated nutrients presented in Table 4 revealed that the highest biological yield (14.82 t ha−1) was found in treatment N1, followed by N4 and N2. The lowest total biomass was observed in treatment N3 (Table 4).
Analysis of variance for grain yield indicates that a significant response was achieved from irrigation and integrated nutrient treatments (Table 3). Regarding irrigation regimes, maximum yield (4.18 t ha−1) was obtained in I2, followed by treatments I1 (3.83 t ha−1) and I3 (3.67 t ha−1) (Table 4). Individual comparison of treatment means for different integrated nutrients revealed that the maximum value for grain yield (4.54 t ha−1) was attained by treatment N1, followed N4 (4.14 t ha−1) and N2 (3.77 t ha−1). Minimum grain yield (3.11 t ha−1) was recorded in treatment N3 (Table 4). Interaction between PSMD levels and integrated nutrient levels was also found to be significant and maximum grain yield (4.78 t ha−1) was recorded in I2 × N1. Meanwhile, minimum grain yield (3.02 t ha−1) was obtained from combination I3 × N3 (Table 4).
RUETDM and RUEGY showed a significant effect on water deficit and integrated nutrient levels. The highest value of RUETDM was attained in I2 (5.39 MJ−1 of intercepted radiation). The lowest RUETDM was observed where drought stress was high. With the comparison of treatment means of integrated nutrients, RUETDM varied from 3.84 to 5.36 MJ−1. Treatment N1 showed the highest RUETDM (5.36 MJ−1 of intercepted radiation); the lowest RUE (3.84 MJ−1 of intercepted radiation) was achieved in N3. RUEGY also differed significantly, and, in the case of integrated nutrients, it varied from 2.09 to 1.26 Mj−1 of intercepted radiation. It was highest in N1. For PSMD levels, the highest RUEGY was recorded in I2 and the minimum was recorded in I3 (Table 5).
Protein contents showed a significant effect on water deficit and integrated nutrient levels. Among irrigation levels, treatment I2 produced the highest protein contents (11.02%), followed by treatment I1 and I3, which produced 10.47% and 10.07%, respectively. Treatments regarding integrated nutrients also differed significantly for protein contents. Conversely from other parameters, in the case of protein contents, treatment N3 attained the highest protein contents (12.21%), followed by treatment N2 (11.13%). The lowest protein contents (8.67%) were observed in N4 (Table 5). Starch contents in wheat were significantly affected by integrated nutrient levels. In protein contents, treatment N3 showed the highest starch contents (59.37%) (Table 5).

4. Discussion

Appropriate frequency and intensity of irrigation water is a critical factor for optimum crop growth and productivity [36]. In this study, drought stress significantly reduced dry matter accumulation, radiation use efficiency, and growth-related characters (leaf area index, leaf area duration, net assimilation, and crop growth rate). However, integrated use of FYM and NPK boosted the growth and yield in wheat. According to Gustav et al. [37], Farooq et al. [38], and Taiz and Zeiger [39], growth and development of plants primarily depends upon three phases: Cell division, elongation, and differentiation. These stages are linked with several physiological, biochemical, and morphological processes. Each of the described processes are adversely affected by drought stress. Drought stress reduces turgor pressure by disrupting water flow from the xylem toward surrounding cells, resulting in stunted leaves and lower LAI. Under drought conditions, a significant reduction in leaf area index occurs due to reduced leaf area [40,41]. The present study reported that the combined application of FYM and NPK in equal proportions expressed a significant tendency to improve the growth traits in wheat crops. Integrated use of organic and inorganic nutrient sources produced the highest LAI, LAD, and CGR. The combination of inorganic nutrients with FYM improves leaf growth, photosynthetic efficacy, chlorophyll contents, and assimilation capacity, eventually increasing the leaf surface area [42].
The present study indicates that drought stress significantly reduced the fraction of intercepted radiation and cumulative photosynthetically active radiations. The decrease in intercepted radiations under reduced irrigation regimes might be the consequence of the decline in the surface area of leaves. Hayatu et al. [43] reported that a reduction in leaf area index, cumulative PAR, and Fi are due to impaired canopy development, change in leaf orientation, and accelerated senescence of leaves. Moreover, the incorporation of NPK with FYM (50% FYM + 50% NPK) significantly affected the cumulative PAR in drought stress conditions. A higher cumulative PAR, achieved by improving the leaf expansion through the addition of FYM with inorganic NPK, leads to the greater availability of essential nutrients. Application and incorporation of FYM decreases the evaporation losses, possibly due to root zone softness caused by manure, leading to higher root proliferation in the soil to fulfill water requirements [44]. It is confirmed in several studies that integrated nutrient management boosted crop growth due to greater and readily available access to nutrients [45,46]. Furthermore, it improves the water-holding capacity and biological properties of soil [47,48]. The combination of FYM with NPK not only meets macronutrient requirement but also provides micronutrients to soil [49]. TDM was also significantly affected by moisture stress. A decrease in total biomass due to drought stress was evident in this experiment. The decrease in TDM production is linked with stomatal closure and leads to a decrease in CO2 fixation, consequently reducing cell division and elongation and limiting cellular metabolism [50]. TDM production was highest with the integrated application of inorganic NPK and FYM. Uikey et al. [51] described that the addition of FYM along with inorganic nutrients improves TDM production because the mechanism of release of nutrients from organic manures is slower; it helps microorganisms to decompose the manure and enhance nutrient availability that leads to the synthesis of protein and results in higher production of TDM.
In the current study, a significant decline in plant height was observed under drought (75 mm PSMD) as reported by Shehzad et al. [52]. According to Imam and Segha-Al-Islami [53] and Baroutzadeh et al. [54], deficit irrigation induces a reduction in plant height by reducing the plant respiration (less CO2 absorption and reduced turgor pressure). An increase in plant height was observed alongside an increase in soil moisture; this is attributed to an increase in the number of internodes per stem [8]. Maximum plant height was achieved with the recommended application of inorganic fertilizer, as mineral fertilizers readily enhance vegetative growth because of their quick availability to crop plants [55]. Tillering was also significantly influenced by drought stress. Tillering was inversely proportional to drought stress as tillering decreases when drought stresses increases and vice versa. Shehzad et al. [52] documented that, at a higher level of water stress, the number of spike-bearing tillers reduced. Khan et al. [56] reported that by increasing irrigation frequency, the number of fertile tillers increased. Integrated use of FYM and NPK improved the number of productive tillers. The combined application of organic and mineral fertilizers helps to improve the tillering capacity of wheat [57,58]. Results regarding grains per spike were also noticeably influenced by PSMD levels; with an increase in the level of deficit, the number of grains per spike reduced. Grains per spike was positively affected by the integrated use of FYM and inorganic NPK. Considering the results of 1000-grain weight, grain yield, and biological yield, these parameters were significantly affected by drought stress. At a mild level of deficit, these parameters performed better. Bashir et al. [13] justify these results by reporting that agronomic traits, such as fertile tillers, grains per spike, test weight, and biological and grain yield, gave better results at 45 mm PSMD treatment. All yield contributing traits gave the best results when they were fertilized with an equal combination of FYM and inorganic NPK, as additions of both organic and mineral sources provide micronutrients and secondary nutrients along with macronutrients [59]. Integrated nutrient management improves fertilizer use efficiency and ensures higher yield on a sustained basis [60].
A gradual reduction in RUETDM was observed with drought due to a decline in leaf canopy, an increase in leaf senescence, and a reduction in photosynthetic efficiency [61]. A combined application of FYM and inorganic NPK caused a positive response in RUETDM due to higher dry matter production through rapid leaf area development by maximum interception of PAR. The rapid development of leaf area leads to rapid coverage of the ground surface, higher carbon capturing, and improved plant growth [62]. In a recent study, it was reported that, under an integrated nutrient system, there is higher availability of plant nutrients because of faster mineralization of organic matter in soil, leading to higher RUETDM [63]. Significant differences in RUEGY were observed by irrigation regimes and integrated nutrients. We observed a substantial reduction in the RUEGY of drought-affected plants due to a decrease in the duration of developmental phases. Water shortage reduces the grain yield which, in turn, drops the RUEGY. Drought stress causes injury in various metabolic processes, such as a decrease in chlorophyll pigments leading to a reduction in RUEGY [64]. Proper application of water and fertilizer improves biomass accumulation, which is strongly linked with grain yield [65]. Integrated application of organic and mineral nutrients positively influenced the RUEGY because the combination of nutrients improved the mobilization of nutrients; the involvement of nutrients in vegetative and grain-filling organs ultimately increased the RUEGY [66].
Protein content in wheat grains was reduced with the increase in water stress and different levels of integrated nutrients. The highest protein percentage was recorded with the sole application of FYM manure. This is because organic manure leads to the accumulation of elevated amounts of seed components, such as CaCO3 and increased lipid metabolism, which functions to enhance protein content in seed [67]. Similarly, the application of organic manures improved wheat starch content and protein content [68,69]. The results of this study can be used to meet sustainable development goals in the era of climate change and water crisis [70,71,72].

5. Conclusions

The physiological availability of water to plants is a key factor in crop production worldwide. The data suggest that there is still great scope to increase wheat productivity by sensible use of deficit irrigation. It is concluded from the study that deficit irrigation significantly influences crop growth and productivity. However, the combined use of organic and inorganic fertilizers showed a considerable response in the growth and yield of wheat under water deficit conditions. The result of the experiment indicated that integration of 50% FYM and 50% NPK produced the highest grain yield at 50 mm PSMD. Moreover, higher growth and radiation use efficiency was also achieved from integrated nutrients (50% FYM and 50% NPK) and irrigation at 50 mm PSMD. The results of this study have the potential to be expanded in arid and semi-arid areas where deficit irrigation is necessary to deal with water crises and to meet future food demands.

Author Contributions

Conceptualization, U.Z.; methodology, U.Z. and M.A.; software, M.I.; validation, U.Z., M.F.M. and M.A.; formal analysis, M.I. and R.I.; investigation, U.Z.; resources, U.Z.; data curation, M.V. and R.I.; writing—original draft preparation, U.Z.; writing—review and editing, U.Z., M.F.M., M.F.A. and M.V.; visualization, R.R. and A.E.S. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Informed Consent Statement

Not applicable.

Data Availability Statement

All the data are available upon request.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Moshawih, S.; Abdullah Juperi, R.N.A.; Paneerselvam, G.S.; Ming, L.C.; Liew, K.B.; Goh, B.H.; Al-Worafi, Y.M.; Choo, C.Y.; Thuraisingam, S.; Goh, H.P.; et al. General Health Benefits and Pharmacological Activities of Triticum aestivum L. Molecules 2022, 27, 1948. [Google Scholar] [CrossRef] [PubMed]
  2. Food and Agriculture Organization (FAO), United Nations. FAO Stat. 2010. Available online: http://faostat.fao.org (accessed on 28 December 2022).
  3. Sutcliffe, C.; Knox, J.; Hess, T. Managing irrigation under pressure: How supply chain demands and environmental objectives drive imbalance in agricultural resilience to water shortages. Agric. Water Manag. 2021, 243, 106484. [Google Scholar] [CrossRef]
  4. Preet, M.S.; Kumar, R.; Valipour, M.; Singh, V.P.; Singh, A.K.; Iqbal, R.; Zafar, M.U.; Sharma, R.; Singh, S.V.; Kumari, A.; et al. Soil nutrient status and morphometric responses of guava under drip irrigation and high-tech horticultural techniques for sustainable farming. Hydrology 2022, 9, 151. [Google Scholar] [CrossRef]
  5. Araya, Y.N.; Garcia-Baquero, G. Ecology of Water Relations in Plants; eLS, John Wiley & Sons, Ltd.: Hoboken, NJ, USA, 2014. [Google Scholar] [CrossRef] [Green Version]
  6. Bassiouni, M.; Manzoni, S.; Vico, G. Optimal plant water use strategies explain soil moisture variability. Adv. Water Resour. 2023, 173, 104405. [Google Scholar] [CrossRef]
  7. Salisbury, F.B.; Ross, C.W. Plant Physiology; Eastern Press Pvt. Ltd.: Bangalore, India, 2005. [Google Scholar]
  8. Meena, R.P.; Karnam, V.; Tripathi, S.C.; Jha, A.; Sharma, R.K.; Singh, G.P. Irrigation management strategies in wheat for efficient water use in the regions of depleting water resources. Agric. Water Manag. 2019, 214, 38–46. [Google Scholar] [CrossRef]
  9. Ishfaq, M.; Zulfiqar, U.; Ahmad, M.; Mustafa, C.B.; Hamed, A.; Aslam, M.S.; Anjum, M.Z. Quantification of radiation use efficiency and yield of wheat as influenced by different levels of nitrogen and water stress under semi-arid conditions of Faisalabad. Agric. Sci. 2018, 9, 873–887. [Google Scholar] [CrossRef] [Green Version]
  10. Hatfield, J.L.; Dold, C. Water-use efficiency: Advances and challenges in a changing climate. Front. Plant Sci. 2019, 10, 103. [Google Scholar] [CrossRef] [Green Version]
  11. Anjum, M.M.; Arif, M.; Riaz, M.; Akhtar, K.; Zhang, S.Q.; Zhao, C.P. Performance of hybrid wheat cultivars facing deficit irrigation under semi-arid climate in Pakistan. Agronomy 2021, 11, 1976. [Google Scholar] [CrossRef]
  12. Hussain, T.; Hussain, N.; Tahir, M.; Raina, A.; Ikram, S.; Maqbool, S.; Fraz Ali, M.; Duangpan, S. Impacts of drought stress on water use efficiency and grain productivity of rice and utilization of genotypic variability to combat climate change. Agronomy 2022, 12, 2518. [Google Scholar] [CrossRef]
  13. Bashir, M.U.; Wajid, S.; Ahmad, A.; Iqbal, M. Potential soil moisture deficit: An alternative approach for irrigation scheduling in wheat. Int. J. Agric. Biol. 2016, 18, 16–22. [Google Scholar] [CrossRef]
  14. Khan, S.; Rasool, A.; Irshad, S.; Hafeez, M.B.; Ali, M.; Saddique, M.; Asif, M.; Hasnain, Z.; Naseem, S.; Alwahibi, M.S.; et al. Potential soil moisture deficit: A useful approach to save water with enhanced growth and productivity of wheat crop. J. Water Clim. Change 2021, 12, 2515–2525. [Google Scholar] [CrossRef]
  15. Alessandrino, L.; Gervasio, M.P.; Vincenzi, F.; Colombani, N.; Castaldelli, G.; Mastrocicco, M. Nutrients and carbon fate in two lowland contrasting soils amended with compost. Catena 2021, 206, 105493. [Google Scholar] [CrossRef]
  16. Cen, Y.; Guo, L.; Liu, M.; Gu, X.; Li, C.; Jiang, G. Using organic fertilizers to increase crop yield, economic growth, and soil quality in a temperate farmland. PeerJ 2020, 8, e9668. [Google Scholar] [CrossRef]
  17. Yang, Z.; Ha, L. Analysis and comparison of nutrient contents in different animal manures from Beijing suburbs. Agric. Sci. 2013, 4, 50–55. [Google Scholar] [CrossRef] [Green Version]
  18. Randhawa, M.S.; Maqsood, M.; Wajid, S.; Anwar-ul-Haq, M. Effect of integrated plant nutrition and irrigation scheduling on yield and yield components of maize (Zea mays L.). Pak. J. Agric. Sci. 2012, 49, 267–273. [Google Scholar]
  19. Kopittke, P.M.; Menzies, N.W.; Wang, P.; McKenna, B.A.; Lombi, E. Soil and the intensification of agriculture for global food security. Environ. Int. 2019, 132, 105078. [Google Scholar] [CrossRef] [PubMed]
  20. Srivastav, A.L. Chemical fertilizers and pesticides: Role in groundwater contamination. In Agrochemicals Detection, Treatment and Remediation; Butterworth-Heinemann: Oxford, UK, 2020; pp. 143–159. [Google Scholar]
  21. Busico, G.; Mastrocicco, M.; Cuoco, E.; Sirna, M.; Tedesco, D. Protection from natural and anthropogenic sources: A new rating methodology to delineate “Nitrate Vulnerable Zones”. Environ. Earth Sci. 2019, 78, 104. [Google Scholar] [CrossRef]
  22. Iqbal, A.; He, L.; Khan, A.; Wei, S.; Akhtar, K.; Ali, I.; Ullah, S.; Munsif, F.; Zhao, Q.; Jiang, L. Organic manure coupled with inorganic fertilizer: An approach for the sustainable production of rice by improving soil properties and nitrogen use efficiency. Agronomy 2019, 9, 651. [Google Scholar] [CrossRef] [Green Version]
  23. Abid, M.; Batool, T.; Siddique, G.; Ali, S.; Binyamin, R.; Shahid, M.J.; Rizwan, M.; Alsahli, A.A.; Alyemeni, M.N. Integrated nutrient management enhances soil quality and crop productivity in maize-based cropping system. Sustainability 2020, 12, 10214. [Google Scholar] [CrossRef]
  24. Ahmad, S.; Hussain, I.; Ghaffar, A.; Saleem, M.Z.; Yonas, M.W.; Hussnain, H.; Ikram, R.M.; Arslan, M. Organic amendments and conservation tillage improve cotton productivity and soil health indices under arid climate. Sci. Rep. 2022, 12, 14072. [Google Scholar] [CrossRef]
  25. George, E.; Rolf, S.; John, R. Methods of Soil, Plant, and Water Analysis. A Manual for the West Asia and North Africa Region; International Center for Agricultural Research in the Dry Areas: Aleppo, Syria, 2013. [Google Scholar]
  26. FAO. CLIMWAT for CROPWAT: A Climatic Database for Irrigation Planning and Management. Irrigation and Drainage Developed by: Martin Smith; Food and Agriculture Organization of the United Nations: Rome, Italy, 1993; p. 49. [Google Scholar]
  27. Monteith, J.L. Climate and efficiency of crop production in Britain. Philos. Trans. R. Soc. Lond. B 1977, 281, 277–294. [Google Scholar]
  28. Szeicz, G. Solar radiation for plant growth. J. Appl. Ecol. 1974, 11, 617–636. [Google Scholar] [CrossRef]
  29. Monteith, J.L.; Elston, J.F. Performance and productivity of foliage in the field. In The Growth and Functioning of Leaves; Dale, J., Milthorpe, F.L., Eds.; Cambridge University Press: Cambridge, UK; Butterworths: London, UK, 1983; pp. 499–518. [Google Scholar]
  30. Watson, D.J. The physiological basis of variation in yield. Adv. Agron. 1952, 4, 101–145. [Google Scholar]
  31. Hunt, R. Plant Growth Analysis; Edward Arnold: London, UK, 1978; pp. 26–38. [Google Scholar]
  32. Beadle, C.L. Plant Growth Analysis. In Techniques in Bio-productivity and Photosynthesis, 2nd ed.; Coomlos, J.D.O., Long, S., Scurlock, J., Eds.; Pergamon Press: Oxford, NY, USA, 1987; pp. 21–23. [Google Scholar]
  33. Bremner, J.M. Organic forms of nitrogen. In Methods of Soil Analysis, Part-2 C; Norman, A.G., Ed.; American Society of Agronomy Inc.: Medison, WI, USA, 1964; Volume 9, pp. 1235–1255. [Google Scholar]
  34. Alina, T.; Lazureanu, A. The influence of dose fertilizer on the qualitative corn hybrid Pr35P12. J. Hortic. Sci. Biotechnol. 2011, 15, 215–217. [Google Scholar]
  35. Steel, R.G.D.; Torrie, J.H.; Dickey, D.A. Principles and Procedures of Statistics: A Biometrical Approach, 3rd ed.; McGraw Hill Book Co. Inc.: New York, NY, USA, 1997; pp. 400–428. [Google Scholar]
  36. Neupane, J.; Guo, W. Agronomic basis and strategies for precision water management: A review. Agronomy 2019, 9, 87. [Google Scholar] [CrossRef] [Green Version]
  37. Gustav, O.A.; Pereyra, I.; Luciano, V.; Leandra, L.; Aguirrezabal, L.A.N. Genetic variability for leaf growth rate and duration under water deficit in sunflower: Analysis of responses at cell, organ, and plant level. J. Exp. Bot. 2008, 59, 2221–2232. [Google Scholar] [CrossRef] [Green Version]
  38. Farooq, M.; Wahid, A.; Kobayashi, N.; Fujita, D.; Basra, S.M.A. Plant drought stress: Effects, mechanisms and management. Agron. Sustain. Dev. 2009, 29, 185–212. [Google Scholar] [CrossRef] [Green Version]
  39. Taiz, L.; Zeiger, E. Plant Physiology, 4th ed.; Sinauer Associates Inc. Publishers: Sunderland, MA, USA, 2006. [Google Scholar] [CrossRef] [Green Version]
  40. Randhawa, M.S.; Maqsood, M.; Shehzad, M.A.; Chattha, M.U.; Chattha, M.B.; Nawaz, F.; Yasin, S.; Abbas, T.; Nawaz, M.M.; Khan, R.D.; et al. Light interception, radiation use efficiency and biomass accumulation response of maize to integrated nutrient management under drought stress conditions. Turk. J. Field Crops 2017, 22, 134–142. [Google Scholar] [CrossRef]
  41. Wu, B.; Lin, X.; Ali, M.F.; Wang, D. Development of an irrigation regime for winter wheat to save water resources by avoiding irrigation at anthesis stage. J. Agron. Crop Sci. 2023, 209, 188–203. [Google Scholar] [CrossRef]
  42. Ali, K.; Arif, M.; Shah, S.; Hussain, Z.; Ali, A.; Munir, S.; Sher, H. Effect of organic and inorganic nutrients sources on phenology and growth of wheat. Pak. J. Bot. 2015, 47, 2215–2222. [Google Scholar]
  43. Hayatu, M.; Muhammad, S.; Habibu, U.A. Effect of water stress on the leaf relative water content and yield of some cowpea (Vigna Unguiculata (L) Walp.) genotype. Int. J. Sci. Technol. 2014, 3, 148–152. [Google Scholar]
  44. Khan, A.; Jan, M.; Marwat, K.; Arif, M. Organic and inorganic nitrogen treatments effects on plant and yield attributes of maize in different tillage systems. Pak. J. Bot. 2009, 41, 99–108. [Google Scholar]
  45. Darjee, S.; Shrivastava, M.; Langyan, S.; Singh, G.; Pandey, R.; Sharma, A.; Khandelwal, A.; Singh, R. Integrated nutrient management reduced the nutrient losses and increased crop yield in irrigated wheat. Arch. Agron. Soil Sci. 2022, 1–12. [Google Scholar] [CrossRef]
  46. Kumar, S.; Sharma, S.K.; Dhaka, A.K.; Bedwal, S.; Sheoran, S.; Meena, R.S.; Jangir, C.K.; Kumar, D.; Kumar, R.; Jat, R.D.; et al. Efficient nutrient management for enhancing crop productivity, quality and nutrient dynamics in lentil (Lens culinaris Medik.) in the semi-arid region of northern India. PLoS ONE 2023, 18, e0280636. [Google Scholar] [CrossRef]
  47. Ejigu, W.; Selassie, Y.G.; Elias, E.; Damte, M. Integrated fertilizer application improves soil properties and maize (Zea mays L.) yield on Nitisols in Northwestern Ethiopia. Heliyon 2021, 7, e06074. [Google Scholar] [CrossRef]
  48. Rahman, M.M.; Uddin, S.; Jahangir, M.M.R.; Solaiman, Z.M.; Alamri, S.; Siddiqui, M.H.; Islam, M.R. Integrated nutrient management enhances productivity and nitrogen use efficiency of crops in acidic and charland soils. Plants 2021, 10, 2547. [Google Scholar] [CrossRef]
  49. Sohu, I.; Gandahi, A.; Bhutto, G.; Sarki, M.; Gandahi, R. Growth and yield maximization of chickpea (Cicer arietinum) through integrated nutrient management applied to rice-chickpea cropping system. Sarhad J. Agric. 2015, 31, 131–138. [Google Scholar] [CrossRef]
  50. Driesen, E.; Van den Ende, W.; De Proft, M.; Saeys, W. Influence of environmental factors light, CO2, temperature, and relative humidity on stomatal opening and development: A review. Agronomy 2020, 10, 1975. [Google Scholar] [CrossRef]
  51. Uikey, V.; Verma, H.; Nawange, D. Influence of organic, chemical and biofertilizer on growth and yield of pea. Agric. Sci. Dig. 2015, 35, 237–240. [Google Scholar] [CrossRef]
  52. Shehzad, M.A.; Maqsood, M.; Iqbal, S.; Saleem, M.; Hassan, M.; Ahmad, W. Impact of nitrogen nutrition and moisture deficits on growth, yield and radiation use efficiency of wheat (Triticum aestivum L.). Afr. J. Biotechnol. 2012, 11, 13980–13987. [Google Scholar] [CrossRef]
  53. Imam, Y.; Segha-Al-Islami, M.J. Crop Yield (Physiology and Processes); Shiraz University Press: Fars, Iran, 2005; p. 521. [Google Scholar] [CrossRef]
  54. Baroutzadeh, M.; Ayeneband, A.; Alavifazel, M. The Study Water Deficit Stress and Plant Density Levels on Yield and Morphological Traits of Maize. In Proceedings of the National Conference of Water Crisis in Agriculture, Islamic Azad University, Sharerey Branch, Iran, 5 November 2009. [Google Scholar]
  55. Kumar, R.; Kumar, R.; Prakash, O. The Impact of Chemical Fertilizers on Our Environment and Ecosystem. In Research Trends in Environmental Sciences; AkiNik Publications: Delhi, India, 2019; Chapter-5; pp. 69–86. [Google Scholar]
  56. Khan, M.J.; Sarwar, T.; Shahzadi, A.; Malik, A. Effect of different irrigation schedules on water use and yield of wheat. Sarhad J. Agric. 2007, 23, 1061–1066. [Google Scholar]
  57. Chand, S.; Anwar, M.; Patra, D.D. Influence of long-term application of organic and inorganic fertilizer to build up soil fertility and nutrient uptake in mint mustard cropping sequence. Commun. Soil Sci. Plant Anal. 2006, 37, 63–76. [Google Scholar] [CrossRef]
  58. Ali, M.F.; Ali, U.; Bilal, S.; Zulfiqar, U.; Sohail, S.; Hussain, T. Response of sorghum and millet to poultry and farmyard manure–based biochar treatments. Arab. J. Geosci. 2022, 15, 1592. [Google Scholar] [CrossRef]
  59. Srinivasarao, C.; Venkateswarlu, B.; Hegde, D.M.; Venkateswara Rao, K.; Kundu, S. Use of Organic Fertilizers Alone or in Combination with Inorganic Ones: Effects on Water-and Nutrient-Use Efficiency in Indian Farming Systems. In Improving Water and Nutrient-Use Efficiency in Food Production Systems; Wiley: Hoboken, NJ, USA, 2013; pp. 235–261. [Google Scholar]
  60. Caravaca, F.; Garcia, C.; Hernandez, M.; Roldan, A. Aggregate stability changes after organic amendment and mycorrhizal inoculation in the afforestation of a semiarid site with Pinus halepensis. Appl. Soil Ecol. 2002, 19, 199–208. [Google Scholar] [CrossRef]
  61. Bat-Oyun, T.; Shinoda, M.; Tsubo, M. Effects of water and temperature stresses on radiation use efficiency in semiarid grassland. J. Plant Interact. 2011, 7, 214–224. [Google Scholar] [CrossRef] [Green Version]
  62. Hamzei, J.; Soltani, J. Deficit irrigation of rapeseed for water-saving: Effects on biomass accumulation, light interception and radiation use efficiency under different N rates. Agric. Ecosyst. Environ. 2012, 155, 153–160. [Google Scholar] [CrossRef]
  63. Maqsood, M.; Shehzad, M.; Ramzan, Y.; Sattar, A. Effect of nitrogen nutrition on growth, yield and radiation use efficiency of different wheat (Triticum aestivum L.) cultivars. Pak. J. Agric. Sci. 2014, 51, 441–448. [Google Scholar]
  64. Azam, M.; Hussain, A.; Wajid, S.; Maqsood, M. Effect of sowing date, irrigation and plant densities on radiation interception and its utilization efficiency in lentils. Int. J. Agric. Biol. 2002, 4, 217–219. [Google Scholar]
  65. Tewolde, H.; Fernandez, C.J. Vegetative and reproductive dry weight inhibition in nitrogen and phosphorus-deficient Pima cotton. J. Plant Nutr. 1997, 20, 219–232. [Google Scholar] [CrossRef]
  66. Crecchio, C.; Curci, M.; Mininni, R.; Ricciuti, P.; Ruggiero, P. Short term effects of municipal solid waste compost amendments on soil carbon and nitrogen content, some enzyme activities and genetic diversity. Biol. Fertil. Soils 2001, 34, 311–318. [Google Scholar] [CrossRef]
  67. Arif, M.; Ali, S.; Khan, A.; Jan, T.; Akbar, M. Influence of farm yard manure application on various wheat cultivars. Sarhad J. Agric. 2006, 22, 27–29. [Google Scholar]
  68. Ali, N.; Khan, M.N.; Ashraf, M.S.; Ijaz, S.; Saeed-ur-Rehman, H.; Abdullah, M.; Ahmad, N.; Akram, H.M.; Farooq, M. Influence of different organic manures and their combinations on productivity and quality of bread wheat. J. Soil Sci. Plant Nutr. 2020, 20, 1949–1960. [Google Scholar] [CrossRef]
  69. Zaheer, M.S.; Ali, H.H.; Soufan, W.; Iqbal, R.; Habib-ur-Rahman, M.; Iqbal, J.; Israr, M.; El Sabagh, A. Potential effects of biochar application for improving wheat (Triticum aestivum L.) growth and soil biochemical properties under drought stress conditions. Land 2021, 10, 1125. [Google Scholar] [CrossRef]
  70. Motevali, A.; Hooshmandzadeh, N.; Fayyazi, E.; Valipour, M.; Yue, J. Environmental Impacts of Biodiesel Production Cycle from Farm to Manufactory: An Application of Sustainable Systems Engineering. Atmosphere 2023, 14, 399. [Google Scholar] [CrossRef]
  71. Ahsan, M.; Valipour, M.; Nawaz, F.; Raheel, M.; Abbas, H.T.; Sajid, M.; Manan, A.; Kanwal, S.; Mahmoud, E.A.; Casini, R.; et al. Evaluation of Silicon Supplementation for Drought Stress under Water-Deficit Conditions: An Application of Sustainable Agriculture. Agronomy 2023, 13, 599. [Google Scholar] [CrossRef]
  72. Valipour, M.; Khoshkam, H.; Bateni, S.M.; Heggy, E. Annual Trends of Soil Moisture and Rainfall Flux in an Arid Climate Using Remote Sensing Data. Highlights Sustain. 2022, 1, 171–187. [Google Scholar] [CrossRef]
Figure 1. Summary of daily weather conditions at the experimental site.
Figure 1. Summary of daily weather conditions at the experimental site.
Hydrology 10 00056 g001
Figure 2. (A) Time course changes of leaf area index for irrigation regimes (B) for integrated nutrient levels.
Figure 2. (A) Time course changes of leaf area index for irrigation regimes (B) for integrated nutrient levels.
Hydrology 10 00056 g002
Figure 3. (A) Time course changes of leaf area duration for irrigation regimes (B) integrated nutrient levels.
Figure 3. (A) Time course changes of leaf area duration for irrigation regimes (B) integrated nutrient levels.
Hydrology 10 00056 g003
Figure 4. (A) Time course changes in crop growth rate for irrigation levels (B) integrated nutrient levels.
Figure 4. (A) Time course changes in crop growth rate for irrigation levels (B) integrated nutrient levels.
Hydrology 10 00056 g004
Figure 5. (A) Time course changes in dry matter for irrigation levels (B) integrated nutrient levels.
Figure 5. (A) Time course changes in dry matter for irrigation levels (B) integrated nutrient levels.
Hydrology 10 00056 g005
Table 1. Soil physical and chemical analysis of the experimental site and chemical analysis of farmyard manure and chemical fertilizers.
Table 1. Soil physical and chemical analysis of the experimental site and chemical analysis of farmyard manure and chemical fertilizers.
ParameterSand (%)Silt (%)Clay (%)pHEC dS m−1OM
(%)
N (%)P2O5 (ppm)K2O (ppm)
Value4521347.94.51.230.06916.4256
Status---AlkalineSalineMediumMediumHighHigh
Farmyard Manure
ParameterpHEC (ds m−1)N (%)P2O5 (%)K2O (%)Zn (ppm)Mn (ppm)
7.462.601.261.290.8474363
Chemical Fertilizers
FertilizerN (%)P2O5 (%)K2O (%)
Urea46--
Diammonium phosphate1846-
Murate of Potash--60
Table 2. Irrigation applied to different treatments and rainfall received.
Table 2. Irrigation applied to different treatments and rainfall received.
DateI1I2I3
mmMmmm
26 November606075
9 December25--
19 December---
2 January2550-
16 January--75
30 January25--
11 February2550-
26 February25-75
6 March---
14 March2550-
Rainfall292929
Total239239254
Table 3. The mean squares of irrigation and integrated nutrient treatments about yield and yield components of wheat.
Table 3. The mean squares of irrigation and integrated nutrient treatments about yield and yield components of wheat.
SOVDFPlant Height (cm)Productive Tillers (m−2)No. of Grains Spike−11000-Grain Weight (g)Biological Yield (t ha−1)Grain Yield (t ha−1)RUETDM (g MJ−1RUEGY
(g MJ−1)
Protein Contents (%)Starch (%)
Replication (r)25.25136.70.680.800.053100.066800.0070.0030.020.51694
Irrigation (I)264.66 **10968 **40.10 **187.79 **0.88148 **0.80300 *9.26 *2.042.68 **0.63361
Error a41.934261.81.960.360.016520.067120.030.0010.030.14194
Nutrients (N)3289.8 **6402.08 **53.13 **28.3 **10.4427 **3.32033 **12.05 *2.53 *20.53 **7.24630 **
I × N65.38 *1211.8 **5.77 **2.98 **0.0314 *0.11836 **0.310.060.010.14769
Error b181.67256.10.440.730.00890.024360.0010.0010.010.13583
Total35
* = Significant at p < 0.05; ** = Significant at p < 0.01.
Table 4. The response of moisture deficit levels and integrated nutrient levels on yield and yield components of wheat.
Table 4. The response of moisture deficit levels and integrated nutrient levels on yield and yield components of wheat.
Integrated Nutrient Levels (N)I1I2I3MeanI1I2I3Mean
Plant Height (cm)Productive Tillers
N197.9de100.1cd99.2cd99.11b301.3a301.3a233.0de284.4a
N290.9g96.2ef95.4f94.21c253.6cd268.6bc261.3c261.2b
N385.6h92.7g92.0 g90.13b231.0de246.6cd182.3f220.0c
N4101.5bc104.6a103.2ab103.1a263.3c294.6ab214.6e257.4b
Mean97.50a98.41a94.01b 262.2b282.2a222.8c
LSD (p ≤ 0.05)I = 1.57; N = 1.28; I × N = 2.22I = 18.34; N = 15.85; I × N = 27.45
Grains Per Spike1000-Grain Weight (g)
N142.16cde49.76a42.60cd44.81a43.79c49.56a40.09ef44.48a
N237.26g42.93bc40.36ef40.18c36.74g42.45cd35.10h38.10c
N339.13fg40.70def39.26f39.70c34.45h39.41f34.06h35.97d
N441.23cde44.53b40.73def42.16b41.20de46.30b37.62g41.71b
Mean40.74b44.48a39.95b 39.04b44.43a36.72c
LSD (p ≤ 0.05)I = 1.02; N = 1.07; I × N = 1.87I = 0.68; N = 0.84; I × N = 1.46
Biological Yield (t ha−1)Grain Yield (t ha−1)
N114.78b15.24a14.44c14.82a4.53ab4.78a4.32bc4.54a
N213.37fg13.53f13.23g13.37c3.66d4.37bc3.30de3.77c
N312.27i12.57h12.06j12.30d3.10ef3.23ef3.02f3.11d
N414.11d14.39c13.84e14.11b4.05c4.33bc4.04c4.14b
Mean13.63b13.93a13.39c 3.83b4.18a3.67b
LSD (p ≤ 0.05)I = 0.14; N = 0.09; I × N = 0.16I = 0.29; N = 0.15; I × N = 0.26
Means sharing same letters did not differ significantly at p = 0.05; I1 = 25 mm PSMD; I2 = 50 mm PSMD; I3 = 75 mm PSMD; N1 = 50% FYM + 50% inorganic (NPK); N2 = 75% FYM + 25% inorganic (NPK); N3 = 100% FYM; N4 = 100% inorganic (NPK).
Table 5. The response of moisture deficit levels and integrated nutrients on radiation use efficiency, protein, and starch contents.
Table 5. The response of moisture deficit levels and integrated nutrients on radiation use efficiency, protein, and starch contents.
Integrated Nutrient Levels (N)I1I2I3MeanI1I2I3Mean
RUETDM (gMJ−1)RUEGY (gMJ−1)
N15.70d6.55a4.89e5.71a2.09c2.70a1.66e2.15a
N23.83h5.76c3.50j4.36c1.26h1.88d1.07j1.40c
N32.83k3.62i2.63l3.03d0.83k1.13i0.79l1.79d
N44.52f6.16b4.34g5.01b1.57f2.37b1.42g2.15b
Mean4.22b5.52a3.84c 1.43b2.01a1.22c
LSD (p ≤ 0.05)I = 0.05; N = 0.03; I × N = 0.05I = 0.03; N = 0.03; I × N = 0.05
Protein Contents (%)Starch (%)
N110.1010.469.6010.06c57.8057.8057.6657.75b
N211.0611.6310.7011.13b57.9658.0657.8057.94b
N312.1012.7311.8012.21a59.1059.9359.1059.37a
N48.609.238.208.67d57.4357.5356.9357.30c
Mean10.47b11.02a10.07c 58.0758.33a57.87
LSD (p ≤ 0.05)I = 0.22; N = 0.03N = 0.36
Means sharing same letters did not differ significantly at p = 0.05; I1 = 25 mm PSMD; I2 = 50 mm PSMD; I3 = 75 mm PSMD; N1 = 50% FYM + 50% inorganic (NPK); N2 = 75% FYM + 25% inorganic (NPK); N3 = 100% FYM; N4 = 100% inorganic (NPK).
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Zulfiqar, U.; Ahmad, M.; Valipour, M.; Ishfaq, M.; Maqsood, M.F.; Iqbal, R.; Ali, M.F.; Roy, R.; El Sabagh, A. Evaluating Optimum Limited Irrigation and Integrated Nutrient Management Strategies for Wheat Growth, Yield and Quality. Hydrology 2023, 10, 56. https://doi.org/10.3390/hydrology10030056

AMA Style

Zulfiqar U, Ahmad M, Valipour M, Ishfaq M, Maqsood MF, Iqbal R, Ali MF, Roy R, El Sabagh A. Evaluating Optimum Limited Irrigation and Integrated Nutrient Management Strategies for Wheat Growth, Yield and Quality. Hydrology. 2023; 10(3):56. https://doi.org/10.3390/hydrology10030056

Chicago/Turabian Style

Zulfiqar, Usman, Muhammad Ahmad, Mohammad Valipour, Muhammad Ishfaq, Muhammad Faisal Maqsood, Rashid Iqbal, Muhammad Fraz Ali, Rana Roy, and Ayman El Sabagh. 2023. "Evaluating Optimum Limited Irrigation and Integrated Nutrient Management Strategies for Wheat Growth, Yield and Quality" Hydrology 10, no. 3: 56. https://doi.org/10.3390/hydrology10030056

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop