Nitrate and potassium movement in a sandy loam soil cultivated with fertigated grapevine (Vitis vinifera /L.) in the Brazilian semiarid

Movimento de nitrato e potássio em solo arenoso cultivado com videira (Vitis vinifera L.) fertirrigada no Semiárido

Abstract

Fertigation can increase the efficiency of fertilizer application and facilitate the nutritional management of a crop. Thus, nitrate and potassium movements in a sandy loam soil were evaluated as function of fertilizer doses during three growing seasons of the grapevine cv. Syrah grafted on Paulsen 1103 rootstock (June to October 2013, February to June 2014, and August to November 2014) in Petrolina, state of Pernambuco, Brazil. Five doses of N (0, 15, 30, 60 and 120 kg ha-1) and five doses of K2O (0, 15, 30, 60 and 120 kg ha-1) were combined in a fractional 52 factorial design, totaling 13 combinations, in a randomized blocks experiment with four replications. The concentrations of nitrate and potassium in the soil solution were determined. Samples were collected by porous cup extractors installed at 0.4 and 0.6 m depths. The movement of these ions was obtained by the product between their concentration in the soil solution and the soil water flux density. The increase in nitrogen fertilization promoted a greater movement of NO3- (62.2 kg ha-1) in the soil. The movement of K+ was also observed in two growing seasons .

Index terms Irrigation management; porous cup extractor; Soil solution

Resumo

A prática da fertirrigação pode aumentar a eficiência de aplicação de fertilizantes e facilitar o manejo nutricional de uma cultura agrícola. Assim, os movimentos de nitrato e de potássio em solo de textura franco arenosa foram avaliados em função da dose de fertilizantes, durante três ciclos de produção da videira de vinho cv. Syrah sobre o porta-enxerto Paulsen 1103 (junho a outubro de 2013, fevereiro a junho de 2014 e agosto a novembro 2014), em Petrolina, Pernambuco. Cinco doses de N (0; 15; 30; 60 e 120 kg ha-1) e cinco doses de K2O (0; 15; 30; 60 e 120 kg ha-1) foram combinadas em um esquema fatorial 52 fracionado, em um total de 13 combinações, e com disposição dos tratamentos em blocos casualizados, com quatro repetições. A concentração de nitrato e de potássio foi determinada na solução do solo, que foi coletada por meio de extratores de cápsulas porosas instalados a 0,4 e 0,6 m de profundidade. O movimento desses íons foi obtido pelo produto entre a concentração dos mesmos na solução do solo e a densidade de fluxo de água no solo. O aumento da adubação nitrogenada promoveu maior movimento de NO3- (62,2 kg ha-1) no solo. O movimento de K+ também foi observado em dois ciclos de produção.

Termos para indexação Manejo da irrigação; Extrator de cápsulas porosas; Solução do solo

Introduction

The adoption of localized irrigation systems makes fertigation feasible. It contributes to a greater efficiency in the application of fertilizers and a greater ease in the nutritional management of crops (SILVA et al., 2016; SHARMA et al., 2014). Currently, the use of fertigation is a common practice in grapevine cultivation (Vitis vinifera L.) in the Lower Middle São Francisco river valley, where fertilizers containing nitrogen (N) and potassium (K) are frequently used due to a need for these nutrients by crops (ROCHA et al., 2015; SILVA et al., 2014) mainly during phenological phases such as flowering and grape ripening.

The production of vine is related to different managements, such as an efficient use of irrigation (BASSOI et al., 2015) and fertilizers (ALBUQUERQUE et al., 2013). Therefore, a correct management of water and fertilizers is necessary to avoid increases in production costs and minimize damages to the environment. Among the problems that arise from an excessive application of fertilizers, we can mention contamination of water tables, by which elements are leached to depths below the root system, and may reach water sources and pollute the environment (BORTOLOTTO et al. 2013). Among the fertilizers that may cause pollution as a consequence of an inadequate management, we can highlight N fertilizers, with an emphasis on the nitrate ion (NO3-) and its action in the contamination of groundwater (ANDRADE et al., 2016), and potassium fertilizers, which may raise the levels of K+ in the soil to levels above those required for crops when applied excessively (SILVA et al., 2014).

In semi-arid regions, the contamination of groundwater may happen even faster, since the soil of such regions are shallow and groundwater is close to the surface (BADR et al., 2016). This problem may further aggravate the hydric situation in such regions, as there are few good water sources.

The main losses of N are caused by denitrification, volatilization and leaching. The latter is responsible for 72% of total N losses in the conventional fertilizer (QUAGGIO et al., 2014). The movement of N in the soil occurs by convection processes of the soil solution, also called mass flows, and by molecular or ionic diffusion due to concentration gradients. Nitrogen movement occurs commonly in the NO3- form, and may be intensified by the excess of water resulting from irrigation systems (MENDES et al., 2015) and by successive N fertilizations (BORTOLOTTO et al., 2013).

The movement of K in the soil depends on the soil type. In most cases, it moves with limitations (SHARMA et al., 2014). In soils with a low cation exchange capacity, this nutrient can be leached. However, when adequate fertilizer doses are applied, leaching losses are extremely low for most conditions. According to Sharma et al. (2014), K can move in the soil profile when there is a concentration of this element near the emitters of the irrigation system, thus increasing concentrations of this nutrient near the root system located within the wet bulb.

This study aims to evaluate the movement of NO3-and K+ in a soil cultivated with fertigated wine vine in Petrolina, in the Brazilian semiarid region.

Materials and methods

Experimental characterization

The experiment was conducted at the Experimental Field of Bebedouro, which belongs to Embrapa Semiárido, in Petrolina, state of Pernambuco, Brazil, located at 09°08’08.09” S, 40°18’33.6” W and altitude of 373 m.

The climatic classification according to Köppen is BSWh, semiarid tropical. Grapevine (Vitis vinifera L.), cultivar Syrah, was grafted into Paulsen 1103 rootstocks. The planting was carried out on April 30, 2009, using a spacing of 1 m between plants and 3 m between rows in a Argissolo Vermelho-Amarelo Eutrófico plintossólico (Santos et al., 2013) which corresponds a Typic Plinthustalf (Soil Survey Staff, 2014). The period of formation of trellised vines occurred until April 2010, when the first pruning was performed. Three prunings were performed on June 17, 2013, February 7, 2014, and August 6, 2014, with the respective harvests performed on October 8, 2013, June 9, 2014, and November 25, 2014, resulting in growing seasons with durations of 113,122 and 111 days, respectively.

Previously to the beginning of the experiment, 36 soil samples were collected from the layers 0-0.20, 0.20- 0.40 and 0.40-0.60 m in plant rows. The samples were analyzed by the Laboratory of Soils and Leaf Analysis of Embrapa Semiárido to determine the physical (Table 1) and chemical (Table 2) attributes of the soil according to the methodologies described by Donagema et al. (2011).

The treatments comprised five nitrogen doses (0, 15, 30, 60 and 120 kg ha-1) and five K2O doses (0.15, 30, 60 and 120 kg ha-1). These treatments were combined in a fractionated 52 factorial design (LITTEL and MOTT, 1975), totaling 13 combinations. The experiment used randomized blocks with four replications. The experimental unit consisted of 17 plants.

The drip irrigation system was used. Each experimental plot had 17 m long side rows (polyethylene hoses) controlled by a shut off valve to open at each fertigation event. The suction system consisted of a 6 m long pipe connected to a water reservoir, a water pump with a flow rate of 15 m3 h-1, a disc filter, an injection pump and a 60 L reservoir for fertilizer solution. Fertigation was performed once a week by an injection pump with a capacity of 300 L h-1. The fertilizers were potassium sulphate (50% of K2O), potassium chloride (60% of K2O), potassium nitrate (12% of N and 45% of K2O) and urea (46% of N). The accompanying ions were balanced by complementary fertilization.

Irrigation management was performed based on the estimation of crop evapotranspiration (ETc). For this, the reference evapotranspiration (ETo, mm day-1) was estimated by the Penmam-Monteith FAO method (ALVES et al., 2017) using data collected by an automatic weather station located 60 m from the experimental area. The crop coefficients (kc) for wine vine cv. Syrah were obtained by Bassoi et al. (2007) in the same location of the experiment.

To monitoring soil moisture (θ, m3 m-3), six sets of tensiometers were installed at the experimental area.

Each contained one instrument at the depths 0.20 m, 0.40 m and 0.60 m. The soil water matric potential (fm, kPa) was determined by a digital punction tensiometer and tension reader. Using a soil water retention curve, the corresponding soil moisture value was determined.

The soil water retention curve was determined at the Laboratory of Soil and Leaf Analysis at Embrapa Semiárido using the centrifuge method (ASSIS et al., 2015) in deformed soil samples collected by an auger at the depths 0-0.20 m, 0.20-0.40 m and 0.40-0.60 m.

Afterwards, the parameters of the soil water retention curve equation (Table 3) were obtained using the software SWRC - Soil Water Retention Curve (DOURADO NETO et al., 2000).

Soil water balance

During the three growing seasons of grapevine cv. Syrah, the soil water balance was estimated from the pruning until harvesting according to equation 1:

$$Rn+I\pm D/A\pm ∆h\pm Ro-ETc=0$$

Where ETc is crop evapotranspiration (mm), Rn is rainfall (mm), I is the irrigation (mm), Δh is the variation in soil water storage (mm), D/A is the deep drainage - descending flow or capillary rise – ascending flow (mm), and Ro is the soil surface flow - runoff (mm).

Soil water storage (h, mm) was determined by integration of soil moisture for each soil layer of interest using equation 2.

$$∆h={\int }_0^L\theta \left(z\right)dz\cong \left[\mathrm{1,5}\theta \left(z_1\right)+\sum \theta \left(z_i\right)+\mathrm{0,5}\left(z_n\right)\right]∆Z$$

Where θ (z1) is the moisture of the first layer (m3 m-3), θ (zi) is the moisture of intermediate layers (m3 m-3), θ (zn) is the moisture of the last layer (m³ m-³), dz is the variation of moisture in the soil layer of interest (m3 m-3), and Δz is the thickness of the soil layer (mm).

The variation of soil water storage was calculated during the periods studied by the following equation 3:

$$∆h=h_f-h_i$$

Where Δh is the variation of soil water storage (mm), Hf is the mean storage at final time (mm), and hi is the mean storage at initial time (mm).

For the determination of the unsaturated soil hydraulic conductivity (CONCEIÇÃO, 2014) by the instantaneous field profile method, a 10 m2 plot inside the experimental area was used where tensiometers were installed at the depths 0.20, 0.40 and 0.60 m. The soil profile was saturated with water using a hose to moisten the upper soil layer (0.60 m). The readings of tensiometers, which were close to zero, indicated saturation of the soil layer of interest. Subsequently, the plot was covered with a plastic cover to prevent any water flow through the soil surface or water evaporation from the soil. The time of the cover installation was considered the time zero (t = 0) of soil water redistribution. Therefore, tensiometer readings began and were taken until the drainage became practically null (20 days), which was verified by the stability of readings of soil water tension.

The hydraulic conductivity as function of matric potential (fm) was determined by the equation (4) using water content data in the profile obtained from tensiometer readings and retention curves determined at the same depths:

$${\left.K\left(\theta \right)\right|}_z=\frac{{\int }_0^z\frac{\partial }{\partial }dz}{{\left.\frac{\partial {\varphi }_t}{\partial z}\right|}_z}=\frac{\frac{\partial h_z}{\partial t}}{{\left.\frac{\partial {\varphi }_t}{\partial z}\right|}_z}$$

Where hz (m3 m-2) is soil water storage between the surface (z = 0) and the depth z, t is redistribution time, and ft is the total soil water potential.

As the values of the function K(θ) present an exponential relation with moisture, the equation (5) was expressed by:

$$K\left(\theta \right)=K_o{e}^{\gamma (\theta -{\theta }_o)}$$

Where K(θ) is the unsaturated soil hydraulic conductivity (mm day-1), Ko is the saturated soil hydraulic conductivity (mm day-1), γ is the soil-dependent constant, θ is soil moisture (m3 m-3), and θo is saturated soil moisture (m3 m-3).

Table 4 shows the values of the parameters of the equation (5) for the different soil depths.

Soil water flux density

To determine deep drainage or capillary rise (descending or ascending flow) at the lower limit of the soil volume (Z = 0.60 m), the Darcy-Buckingham equation was used according to equation 6:

$$D/A=-K\left(\theta \right)\frac{{\mathrm{\Delta }\varphi }_t}{z}D/A=-K\left(\theta \right)\frac{{\mathrm{\Delta }\varphi }_t}{z}$$

Where D/A is the soil water flux density (mm day-1), K (θ) is the unsaturated soil hydraulic conductivity (mm day-1), Δφt/z is the total potential gradient, Φt is total soil water potential (m), and z is the vertical position coordinate (m).

The total potential at each depth was calculated by the equation (7):

$${\varphi }_t={\varphi }_m+{\varphi }_g$$

Where fg is the gravitational potential (m).

The matric potential (fm), in m of water, was calculated according to the equation (8):

$$-{\varphi }_m=Rtx\mathrm{0,1}-\left(ht+hc\right)$$

Where Rt is the tensiometer reading (kPa), Ht is the height of the tensiometric tube above the soil (m), and hc is the installation depth of the tensiometer (m).

Movement of nitrate and potassium in the soil solution

In the plant rows of each plot, porous cup extractors were installed near the tensiometers at the depths 0.40 and 0.60 m. The soil solution was removed by vacuum (-80 kPa) using a hand pump one day after each fertigation event until the end of crop growing seasons. The samples were composed by treatment and by depth. The analyses of nitrate concentration in the soil solution were performed using a specific Horiba® cardiometer, while potassium analyses were performed using flame photometry.

Assuming the movement only by mass flow, the flux density of each nutrient at a given depth was determined by the product between water flux density and nutrient concentration at a given time interval equation 9:

$$qNUT=q{H}_{2}OxcNUT$$

Where qNUT is the nutrient flux density (kg ha-1 day-1), qH2O is the soil water flux density (m³ m-2 day-1), and cNUT is the mean nutrient concentration in the soil solution (kg L-1) per treatment, all at the depth z (m).

Soil water flux density was estimated by the equation 10:

$$q{H}_{2}O=K\left(\theta \right)\times grad\left(H\right)$$

Where K(f) is the unsaturated soil hydraulic conductivity (m3.m2.day-1), and grad(H) is the hydraulic gradient of soil water.

The results were submitted to analysis of variance and then regression analysis at a 5% probability (p <0.05).

Results and discussion

Soil moisture

Due to the daily frequency of drip irrigation, the values of soil moisture (θ) in all grapevine growing seasons studied (Figure 1) were close to field capacity moisture. The 0.20 m depth presented values of θ with small variations for all growing seasons. The mean values were 0.16 m3 m-3, 0.17 m3 m-3 and 0.17 m3 m-3 for the first, second and third growing seasons (Figure 1A, 1B and 1C, respectively). At 0.4 m and 0.60 m depths, the values of θ were similar in all the growing seasons studied, showing increases in moisture values in measurements performed a few hours after irrigation, as can be observed in the first 30 days after pruning (dap) of the third grapevine growing season.

According to Castellanos et al. (2013), the application of water may directly influence fertilizer losses since the excess of irrigation water depths causes leaching, while an efficient use of water, related to a correct irrigation management, reduces the risks of contamination of rivers and water sources by fertilizers.

In this aspect, the drip irrigation system becomes a good option since its application efficiency is high, concentrating the application of nutrients in the crop root system (BARAKAT et al., 2016).

Water balance

For water balance during the first growing season (Table 5), rainfall (Rn) results were only 13.0 mm, with a maximum Rn of 5.5 mm on the 28th dap. Thus, irrigation was responsible for making available all the water consumed by the plants during this season by applying a total irrigation (I) of 600.7 mm. During the second season, the total value of Rn was 99.2 mm. At 61 dap, there was a 35.5 mm rainfall, raising soil water storage (Δh) to field capacity (SWC) up to 0.60 m depth in the period between 14 and 88 dap. Due to the high rainfall in this period, there was a reduction in the total I, and 431.3 mm season-1 were applied.

During the third growing season, the total Rn value was 71.6 mm and 64.4 mm occurred at 103 dap, which caused the irrigation interruption until the harvesting day.

The total I during this season was 644 mm, which was higher than the previous two seasons. The proper water management in grapevines is of great importance for a better quality of grapes. According to Bassoi et al. (2015) grape quality is influenced directly by water management, such as volume of must and concentration of tartaric acid.

However, number and weight of bunches per plant did not change. Therefore, a correct quantification of irrigation management, in addition to avoiding the leaching of fertilizers, may result in significant results in the grape yield due to an efficient water use.

Movement of nitrate

During the first grapevine season, at 0.4 m depth (Figure 2A), a maximum movement was 13 kg NO3- ha-1.

At 0.6 m depth (Figure 2B), the movement was higher (62.2 kg NO3- ha-1) in relation to application of 120 kg N ha-1. These results are similar to those presented by Lorensini et al. (2012) in a vineyard in Southern Brazil, in which the highest concentration of mineral nitrogen in the leached solution at 0.20 m depth were found when higher dose (120 kg N ha-1 year-1) of mineral fertilizer (urea) was applied in a Sandy Typic Hapludalf soil (clay content of 70 g kg-1 in 0.20 m layer).

During the second grapevine season, there was an increase in the movement of NO3- at 0.4 m depth (Figure 2C) possibly due to an acceleration of the nitrification process caused by several factors such as availability of soil water (BARAKAT et al., 2016), chemical conditions related to pH (HAN et al., 2015) and even soil physical conditions such as texture (74% of sand). However, such losses may not influence crop production since, according to the literature (ROCHA et al., 2015; ARROBAS et al., 2014), the application of high doses of N (above 80 kg N ha-1) to the soil did not increase plant yield.

Compared to the previous season, the movement of NO3- at 0.6 m depth (Figure 2D) was lower, presenting maximum values of 48.6 kg NO3- ha-1.

During the third grapevine season, there was a high movement of NO3- at both studied depths.

At the end of the fertigation period, the 0.4 m depth (Figure 2E) showed a minimum movement of 14 kg NO3- ha-1 (15 kg N ha-1) and a maximum movement of 61 kg NO3- ha-1 (120 kg N ha-1), whereas at 0.6 m depth (Figure 2F) there was a high movement of NO3- at deeper layers, with a value above 50 kg NO3- ha-1 for the highest dose of N applied.

In the analysis of variance for the movement of NO3- at 0.40 and 0.60 m soil depths, significant differences were observed for the factor N doses for all studied seasons, except for 0.60 m (second season) and 0.40 m (third season) depths.

In the data regression analysis, the adjustment model adopted in the first growing season at 0.4 m depth was linear (Figure 3A) with a movement of 0.044 kg NO3- ha-1 for each unit increase in the N dose applied to the soil. At 0.60 m depth (Figure 3B) the adjustment adopted was quadratic and presented a greater movement in the N dose of 120 kg N ha-1 with values of NO3- estimated in 115,40 kg NO3- ha-1. During the second growing season, there was an increase of 0.099 kg NO3- ha-1 at 0.40 m depth (Figure 3C) for each unit increase in the N dose applied.

There was a considerable increase in the NO3- movement during the first and second grapevine growing seasons. Soil texture (74% sand) and low soil CEC (6.3 cmolc dm-3) may have had a significant influence on the NO3- movement due to low ion adsorption by soil matrix and despite the high efficiency of the drip irrigation system for fertilizer application (BORSSOI et al., 2012). There was a high movement as the N doses applied by fertigation increased, as occurred during the third growing season at 0.60 m depth (Figure 3D), in which there was a NO3- movement of 0.155 kg NO3- ha-1 for each increase unit in N dose applied to the soil by fertigation.

Min et al.(2016) and Silva et al. (2016) have demonstrated that high rate of water infiltration in sandy soil can contribute to N movement to deep layers affecting NO3- availability in the root zone to the plants. The leaching of NO3- to water table is maximized by sandy texture, low organic matter, high permeability, low water holding capacity and high water application (GHIBERTO et al., 2015).

Movement of potassium

Although the K+ mobility in the soil is low and occurs mainly by diffusion (SILVA et al., 2016; SILVA et al., 2014) there were high movements of this ion at 0.4 m and 0.6 m depths in relation to increases in K2O doses applied by fertigation. During the first growing season we observed a movement of 9 kg K+ ha-1 at 0.4 m depth (Figure 4A), and of 16 kg K+ ha-1 at 0.60 m depth (Figure 4B) for 120 kg K2O ha-1 doses.

During the second season, there was an increase in the K+ movement, with values of 20.9 kg K+ ha-1 (Figure 4C) at 0.4 m depth, and 30.56 kg K+ ha-1 at 0.6 m depth (Figure 4D) for the 120 kg K2O ha-1 dose. Possibly, the high movement of K+ can be attributed to the low CEC and the good soil drainage, since K is little adsorbed by the soil. During the third season, there was a decrease in movement in relation to previous seasons, with maximum values of 20.03 kg K+ ha-1 at 0.4 m depth (Figure 4E), and 13.14 kg K+ ha-1 at 0.6 m depth (Figure 4F) for the 120 kg K2O ha-1 dose.

The analysis of variance (F test) for the movement of K+ in the different grapevine growing seasons and soil depths showed significant differences for 0.40 m depth during the first and second seasons. There was the interaction among N and K2O doses during the first season and only among doses of K2O during the second season cycle at 1 and 5% probability, respectively.

For the first growing season, the response surface in the movement at 0.40 m depth (Figure 5A) indicates a progressive increase of K + in 0.0458 kg K+ ha-1 for doses of N and 0.0205 kg K+ ha-1 for doses of K2O. The highest value (8.46 kg K+ ha-1) was observed when doses of 120 kg ha-1 of N and K2O were applied. If fertilizers containing these two ions are used together in fertigation, the interaction between them may occur (SILVA et al., 2016). During the second growing season, at 0.40 m depth (Figure 5B), there was a linear adjustment, with an increase of 0.049 kg K+ ha-1 for the K+ movement for each unit increase in K2O doses applied. Silva et al. (2014) observed an increase in the K+ concentration in the soil solution according to increase in K2O doses applied in an area close to this experiment.

Figure 1
Soil water content during the first (A), second (B) and third (C) growing seasons of grapevine cv. Syrah/Paulsen 1103 in Petrolina, PE, according to days after pruning (dap).

Figure 2
Accumulated movement of nitrate in the soil during fertigation events according to days after pruning (dap) at the 0.40 m (A) and 0.60 m (B) depths - first growing season, 0.40 m (C) and 0.60 m (D) - second growing season, and 0.40 m (E) and 0.60 m (F) - third growing season of grapevine cv. Syrah/Paulsen 1103.

Figure 3
Regression analysis for the movement of nitrate at 0.4 m (A, C and E) and 0.6 m soil depths (B, D and F) in three growing seasons of grapevine cv. Syrah/Paulsen 1103.

Figure 4
Accumulated movement of potassium in the soil during fertigation events according to days after pruning (dap) at 0.40 m (A) and 0.60 m (B) depths - first growing season, 0.40 m (C) and 0.60 m (D) depths - second growing season, and 0.40 m (E) and 0.60 m (F) depths - third growing season of grapevine cv. Syrah/Paulsen 1103, in Petrolina.

Figure 5
Regression analysis for the soil movement of potassium at 0.4 m (A) and 0.6 m (B) depth in the first growing season, 0.4 m (C) and 0.6 m (D) in second growing seasons and 0.4 (E) m and 0.6 m (F) in third growing season of grapevine cv. Syrah/Paulsen 1103.

Table 1
Physical attributes of a Red Yellow Argisol (experimental area).

Depth	Sd	Pd	P	Particle size			Texture
				Sand	Silt	Clay	Classification
M	kg cm-3	kg cm-3	(%)	------------g kg-1----------
0-0.20	1.23	2.54	51.41	764.3	171.18	64.50	Sandy loam
0.20-0.40	1.24	2.53	51.08	737.7	180.38	81.88	Sandy loam
0.40-0.60	1.30	2.55	49.13	721.4	139.61	139.00	Sandy loam

• ^Sd
  soil density
• ^Pd
  particle density
• ^TP
  total porosity

Table 2
Chemical attributes of a Red Yellow Argisol before the beginning of fertigation.

Depth	EC	pH			OM		NO3-		NH4+	P	K		K	Ca	Mg
(m)	ds m-1	H2O			g dm-3		---mg kg-1----			-----mg dm-3			----- cmolc dm-3 ----
0-0.20	0.7	7.5			20.8		4.28	4.86		156.9	351		0.9	3.5	1.3
0.20-0.40	0.5	7.2			15.2		3.50	4.67		123.9	234		0.6	3.1	1.1
0.40-0.60	0.32	6.81			8.92		3.11	4.08		93.79	156		0.4	2.8	1.1
Depth	Na	H+Al			BS		CEC		V	Cu			Fe	Mn	Zn
(m)	-------cmolc dm-3-------							(%)		-----------mg dm-3--------
0-0.20	0.1		1.1	5.8		7.0		83.3		1.75		18.08		61.6	21.5
0.20-0.40	0.1		1.3	4.9		6.2		78.8		2.49		19.63		46.4	19.8
0.40-0.60	0.08		1.4	4.4		5.8		75.7		4.71		23.02		26.9	12.2

• ^*
  CE - electric conductivity of the saturation extract; OM - organic matter; NO3- - nitrate; NH4+ ammonium; P - phosphorus; K - potassium; Ca - calcium; Mg - magnesium; Na - sodium; H+Al - potential acidity; BS - base sum; CEC - cation exchange capacity; V (%) - base saturation; Cu - copper; Fe - iron: Mn-manganese; Zn-zinc.

Table 3
Parameters of the van Genutchen equation describing water retention curves in the three soil layers of a Argissolo Vermelho-Amarelo Eutrófico plintossólico.

Depth (m)	α	m	n	θr (m³ m-3)	θs (m³ m-3)
0-0.20	1.338	0.182	3.123	0.086	0.393
0.20-0.40	0.707	0.203	2.311	0.092	0.317
0.40-0.60	1.217	0.170	3.809	0.117	0.489

• ^*
  ?r- residual moisture, ?s - saturation moisture; a, m, n - empirical parameters of the equation

Table 4
Values of of saturated hydraulic conductivity (Ko, m² h-1 KPa-1), ? and soil water saturation (?o, m3 m-3) at 0.20, 0.40 and 0.60 m depths of a Argissolo Vermelho-Amarelo Eutrófico plintossólico.

Depth (m)	Ko	upsih;	theta;o
0.20	1.200	16.839	0.395
0.40	2.813	20.408	0.315
0.60	1.906	19.155	0.324

Table 5
Variation in soil water storage (?h), irrigation (I), rainfall (Rn), deep drainage / capillary rise (D/A) and crop evapotranspiration (ETc) in three growing seasons of grapevine cv. Syrah/Paulsen 1103.

Period (dap)	PF	Delta;h	I	RnRt	D/A	ETc
		------------------------------- 1st season --------------------------
		--------------------------- mm -----------------------------
8-28	UL - SF	-5.41	133.02	7.50	-7.32	122.41
30-39	FL	3.23	65.72	3.60	-12.48	59.15
42-52	PS	11.30	66.75	1.90	-13.40	59.91
56-67	PS-BC	-7.42	92.73	0.00	-8.04	83.46
70-81	CB-VE	5.13	85.89	0.00	-12.39	77.30
84-94	VE	-0.98	71.15	0.00	-11.85	64.04
98-105	R	10.03	49.73	0.00	-11.38	44.76
107-113	R	6.65	35.73	0.00	-16.19	32.15
Total		22.53	600.72	13.00	-93.05	543.18
		------------------------------- 2nd season -------------------------
5-14	UL	0.00	51.70	29.70	-6.05	72.47
23-33	SF - FL	4.91	99.74	2.60	-3.82	99.57
38-49	PS	0.38	98.51	0.00	-9.85	88.66
61-77	CB	0.48	69.16	45.70	-5.96	107.00
80-91	VE	-6.2	36.23	18.00	-20.74	39.31
94-103	VE	21.03	26.90	0.00	-13.80	24.21
105-112	R	12.03	21.48	3.20	-9.15	19.75
115-122	R	32.06	27.59	0.00	-12.92	24.83
Total		64.69	431.31	99.20	-82.29	475.80
		------------------------------- 3rd season --------------------------
2-12	UF - SF	6.3	47.5	3.9	-9.9	42.6
14-28	SF - FL	12.9	123.2	0.0	-12.6	110.9
30-42	FL - PS	0.1	117.0	0.0	-7.2	105.3
44-56	PS	4.7	99.5	0.0	-10.3	89.6
58-68	VE	7.0	69.6	0.3	-10.6	62.7
70-79	VE	-3.8	74.1	0.0	-18.4	66.6
82-89	R	0.3	67.3	0.0	-5.3	60.6
91-100	R	14.3	43.2	1.1	-16.3	38.9
103-111	R	0.0	3.1	66.3	-23.9	2.8
Total		41.8	644.5	71.6	-114.5	580.0

• ^*
  dap - days after pruning, PP - phenological phase, UL – unfolded leaf SF - separate flowers, FL - flowering, PS - pea size berries, CB – closure bunch, VE – veraison and R - ripening

Conclusions

The increase in doses of N and K2O applied through drip fertigation during three grapevine growing seasons enhanced the movement of NO3- and K+ in a sandy soil of Brazilian semiarid. Despite the efficiency of drip fertigation, a greater split of fertilizer application is recommended to minimize downward movement of nutrients in the soil.

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Publication Dates

• Publication in this collection
  2018

History

• Received
  09 Nov 2017
• Accepted
  17 May 2018