Ionic homeostasis, biochemical components and yield of Italian zucchini under nitrogen forms and salt stress

Homeostase iônica, componentes bioquímicos e produção da abobrinha italiana sob formas de nitrogênio e estresse salino

Abstract

This research was carried out aiming at evaluating the effects of nitrate and ammonium ions on nutrient accumulation, biochemical components and yield of Italian zucchini (cv. Caserta) grown in a hydroponic system under salt stress conditions. The experiment was carried out in a greenhouse utilizing an experimental design in randomized blocks, arranged in a 2 x 5 factorial scheme, with 4 replications. The treatments consisted of two forms of nitrogen (nitrate - NO₃^- and ammonium - NH₄⁺) and 5 electrical conductivity levels of irrigation water (EC_w) (0.5, 2.0, 3.5, 5.0 and 6.5 dS m^-1). The analysis of the results indicated that supply of N exclusively in NH₄⁺ form promotes greater damage to the leaf membrane and reduction in accumulation of macronutrients and higher Na⁺/K⁺, Na⁺/Ca⁺⁺ and Na⁺/Mg⁺⁺ ratios in the shoots of zucchini plants. Electrical conductivity of irrigation water above 2.0 dS m^-1 reduces the accumulation of nutrients in shoot and yield of Italian zucchini plant. The toxicity of NH₄⁺ under Italian zucchini plants overlap the toxicity of the salinity, since its fertilization exclusively with this form of nitrogen inhibits its production, being the NO₃^- form the most suitable for the cultivation of the species.

Keywords:
Cucurbita pepo L.; electrolyte leakage; nitrogen fertilization; saline water

Resumo

Este trabalho foi desenvolvido com o objetivo de avaliar os efeitos dos íons nitrato e amônio sobre o acúmulo de nutrientes e produção da abobrinha italiana (cv. Caserta) cultivada em sistema hidropônico sob estrese salino. O experimento foi conduzido em casa de vegetação utilizando o delineamento experimental em blocos casualizados, arranjados em esquema fatorial 2 x 5, com 4 repetições. Os tratamentos foram constituídos de duas formas de nitrogênio (nitrato - NO₃^- e amônio - NH₄⁺) e cinco níveis de condutividade elétrica da água de irrigação (CE_a) (0,5; 2,0; 3,5; 5,0 e 6,5 dS m^-1). As análises dos resultados indicaram que suprimento de N exclusivamente em forma de NH₄⁺ promove maiores danos na membrana foliar e redução no acúmulo de macronutrientes e maiores relações Na⁺/K⁺, Na⁺/Ca⁺⁺ e Na⁺/Mg⁺⁺ na parte aérea das plantas de abobrinha. A irrigação com água a cima de 2,0 dS m^-1 reduz o acúmulo de nutrientes na parte aérea das plantas e a produção de abobrinha. A toxicidade do NH₄⁺ sob abobrinha italiana sobrepõe-se à toxicidade da salinidade, pois a fertilização exclusiva com esta forma de nitrogênio inibe sua produção, sendo a forma NO₃^- a mais adequada para o cultivo da espécie.

Palavras-chave:
Cucurbita pepo L.; extravasamento de eletrólitos; adubação nitrogenada; água salina

1. Introduction

Nitrogen is a limiting factor for crop growth and yield, since it is essential and required in large quantities by most plants (McAllister et al., 2012; Medeiros et al., 2016). Nitrogen nutrition in adequate quantities becomes essential for normal plant growth and satisfactory production. Under natural conditions, the two forms of nitrogen absorbed are the ions NH₄⁺ and NO₃^-, with a variation in the preferential form of absorption of this nutrient among the species (Helali et al., 2010). However, most species prefer to absorb it in the form of NO₃^-, although there is a greater energy expenditure for its assimilation in this case (McAllister et al., 2012).

The higher energy expenditure of the plant to assimilate NO₃^- occurs because, unlike NH₄⁺ which is directly incorporated into amino acids by the enzymes glutamine synthase (GS) and glutamate synthase (GOGAT) (Bittsánszky et al., 2015; Silva Júnior et al., 2019), NO₃^- initially needs to be reduced to NO₂^- by the nitrate reductase enzyme and then NH₄^- by nitrite reductase enzyme, to then be incorporated by the enzymes GS and GOGAT (Bredemeier and Mundstock, 2000).

Besides playing an important role in improving growth and yield, nitrogen fertilization can mitigate the deleterious effects of salt stress on plants, including some studies point out that the availability of certain forms of nitrogen can interact with the physiological mechanisms of sensitivity and tolerance of plants to salt stress (Fernández-Crespo et al., 2012; Miranda et al., 2015). This interaction occurs because this macronutrient performs important functions in plant metabolism, such as structural functions and participation as a component of proteins, enzymes, RNA, DNA, ATP, chlorophyll, among other molecules (Chaves et al., 2011). In addition, it can promote the accumulation of organic compounds such as amino acids and soluble carbohydrates, which increase the osmotic adjustment capacity of plants, promoting acclimation to salinity and increasing their resistance to salt stress (Oliveira et al., 2010). However, this effect is strongly dependent on plant species and stress duration and intensity (Hessini et al., 2013).

Despite the possible benefits of an adequate nitrogen nutrition for the acclimation of plants to salt stress, the literature is divergent with respect to the action of forms of nitrogen as attenuator of the effects of salinity. Some authors argue that this occurs due to a favorable accumulation of nitrogen and/or a positive effect on ionic homeostasis (Miranda et al., 2015), while others advocate that this fact occurs due to the minimization of the effects of reactive oxygen species (Ashraf and Harris, 2004). However, it should be noted that, in general, NH₄⁺ tends to be toxic to plants (Britto and Kronzucker, 2002; Cruz et al., 2011; Bittsánszky, et al., 2015; Esteban et al., 2016).Thus, there is a need for investigations aimed at elucidating the possible benefits of nitrogen fertilization in the acclimation of plants to salt stress and how they occur.

Regarding the salinity tolerance of the vegetable species cultivated in Brazil, the Italian zucchini (Cucurbita pepo L.) is moderately sensitive to salt stress with threshold salinity (soil saturation extract) of 3.2 dS m^-1 and yield losses of up to 9.4% per dS m^-1 (Dias et al., 2016). In relation to its national importance, Italian zucchini stands out among the vegetables for the great potential for commercialization and acceptance in the consumer market due to its food value and culinary versatility of its fruits (Azambuja et al., 2015).

Thus, based on the hypothesis that the form of nitrogen supply can constitute a management strategy for the acclimation of plants to salinity, this study aimed to evaluate the effects of NH₄⁺ and NO₃^- ions on the accumulation of nutrients, biochemical components and yield of Italian zucchini (cv. Caserta) cultivated in hydroponic system under salt conditions.

2. Materials and Methods

2.1. Study location, treatments and statistical design

The experiment was conducted from May to July 2018 in a greenhouse, located on the East Campus of the Federal Rural University of the Semi-Arid Region (UFERSA), in the municipality of Mossoró/RN, Brazil (5° 11' S and 37° 20' W, and 18 m altitude). The climate of the area where the experiment was conducted is classified as Equatorial Zone Tropical, with three subtypes (mild semiarid, medium semiarid and strong semiarid) (Diniz and Pereira, 2015). During the experimental period, the maximum and minimum temperatures were of 32.8 and 19.4 ºC and maximum and minimum relative air humidity of 86 and 33%, while the daily mean values of temperature and relative air humidity throughout the experiment were 27.1 ºC and 65%, respectively.

The experimental design adopted was randomized blocks, arranged in a 2 × 5 factorial scheme, with four replicates, totaling 40 experimental units, each of which contained 3 plants. The treatments consisted of two forms of nitrogen (nitrate - NO₃^- and ammonium - NH₄⁺) and five levels of irrigation water electrical conductivity (EC_w) (0.5; 2.0; 3.5; 5.0 and 6.5 dS m^-1).

The nutrient solution was prepared based on the recommendation of Furlani et al. (1999), modified to contain nitrogen only in the form of NO₃^- and only in the form of NH₄⁺. Nitrogen fertilizers KNO₃ and Ca(NO₃)₂ were used to prepare the nitric nutrient solution, while for the ammoniacal nutrient solution, fertilizers (NH₄)₂SO_4, NH₄HPO₄, and NH₄Cl were used.

2.2. Experimental setup and analyses

Italian zucchini (cv. Caserta) plants were cultivated in 8-dm³ plastic pots, filled with coconut fiber substrate. At the bottom, the pots received a 2-cm-thick layer of crushed stone + geotextile to avoid substrate loss. The substrate was irrigated with public-supply water so as to substrate attain moisture content close to its maximum water retention capacity, and sowing was performed at 3 cm depth, by planting four seeds per pot. The pots were placed on bricks to avoid direct contact with the greenhouse floor, facilitating the drainage of the leachate.

At 10 days after sowing (DAS), when the seedlings were established, fertigation began to be applied with nutrient solution (Table 1). To avoid NH₄⁺ nitrification, a nitrification inhibitor (Dicyandiamide) was mixed in this solution at 10% of the NH₄⁺-N dose, thus guaranteeing the absorption of nitrogen exclusively in the ammoniacal form. The solutions were prepared using water from the supply system of the East Campus of UFERSA (Table 1), plus sodium chloride, calcium chloride and magnesium chloride salts in an equivalent proportion of 7:2:1 to achieve desired level of electrical conductivity.

Table 1
Physico-chemical characterization of the supply water used to prepare the nutrient solutions and contents of nutrients used in its formulation.

Physico-chemical characterization of the supply water1
pH	EC	K+		Na+	Mg++	Ca++		Cl-	CO3--		HCO3-	SAR
H2O	dS m-1	-------------------------------------mmolc L-1----------------------------------------										(mmol L-1)0.5
7.57	0.54	0.31		3.79	1.20	0.83		2.40	0.60		3.20	3.73
Nutrients used in its formulation 2
Stock Solution			Concentration (g L-1)				NO3-			NH4+
KNO3 - 1 M			101.10				6 mL L-1			-
Ca(NO3)2 - 1M			164.09				5 mL L-1			-
MgSO4 - 1M			120.37				2.5 mL L-1			2.5 mL L-1
KH2PO4 - 1M			136.09				1.5 mL L-1			-
Fe-EDTA3			-				1 mL L-1			1 mL L-1
Micronutrients4			-				1 mL L-1			1 mL L-1
(NH4)2SO4 - 1M			132.14				-			6 mL L-1
NH4HPO4 - 1M			115.06				-			1.5 mL L-1
NH4Cl - 1M			53.49				-			2.5 mL L-1
KCl - 1M			74.55				-			1.5 mL L-1
K2SO4 - 0.5 M			87.13				-			6 mL L-1
CaCl2 - 1 M			110.98				-			5 mL L-1

• ¹
  pH - Hydrogen potential; EC - Electrical conductivity; K⁺ - Potassium; Na⁺ - Sodium; Mg²⁺ - Magnesium; Ca⁺⁺ - Calcium; Cl^- - Chloride; CO₃^-- - Carbonate; HCO₃^- - Bicarbonate; SAR - Sodium adsorption ratio; ²Adapted from Furlani et al. (1999); ³(Disodium EDTA + FeSO₄.7H₂O); ⁴(H₃BO₃ + MnSO₄ + ZnSO₄ + CuSO₄ + H₂MO₄).

From sowing to the 10^th day, plants were irrigated with supply water and then fertigated with the standard nutrient solution. Both irrigation and fertigation were performed twice a day (early morning and late afternoon), applying a water volume sufficient to replace the losses occurred by evapotranspiration. The water depth used was estimated by subtracting the leached water volume from the applied water volume (lysimetry). A drip irrigation system with pressure-compensating drippers with flow rate of 1.4 L h^-1 was used.

2.3. Mineral composition, biomass e fruiting production

At the beginning of the flowering stage (30 DAS), plant samples were collected from each experimental plot to determine the mineral composition of the shoots, leaf pigments and leaf membrane damage. One plant of each experimental unit was cut close to the substrate surface to determine shoot dry biomass (SDB) and subsequently placed in paper bags and dried in a forced air circulation oven at 65 °C until constant weight, to determine the dry weight on an electronic digital scale. Mineral composition analyses were performed by wet digestion, using the methodology described by EMBRAPA (2009) to determine the contents of phosphorus (P), potassium (K), calcium (Ca), magnesium (Mg) and sodium (Na) and the methodology cited by Tedesco et al. (1995), with some adaptations of EMBRAPA (2009), to determine the nitrogen content. These data were used to estimate the accumulated amount per plant and the relationship between the concentration of Na and the cationic elements K, Ca and Mg (Na⁺/K⁺, Na⁺/Ca⁺⁺ and Na⁺/Mg⁺⁺).

The degree of membrane integrity was determied by electrolyte leakage (EE) according to the methodology described by Singh et al. (2007).

Leaf disks of 0.625 cm in diameter were removed from the same leaf used to determine the EE for the determination of the following chloroplastidic pigments: chlorophyll a (CLO a), chlorophyll b (CLO b) and carotenoids (CAROT). The pigments were extracted in a dimethyl sulfoxide solution saturated with CaCO₃, following the methodology described by Wellburn (1994).

At 55 DAS, at the end of the experiment, the production per plant (PP) was quantified by weighing all fruits produced by the plants on a digital scale.

2.4. Statistical analysis

The data were analyzed using the statistical program SISVAR, version 5.6, obtaining the variances (ANOVA) and checking the significances at 0.05 and 0.01 probability levels using the F test. When there was significance, regression analysis was performed for EC_w and means comparison test (Tukey test at 0.05 probability level) was carried out for the forms of nitrogen. When the interaction between factors was significant, the EC_w factor was further analyzed at each form of nitrogen, by means of regression analysis.

3. Results

The interaction between the forms of nitrogen and water electrical conductivity was significant (p<0.01) for zucchini production. The forms of nitrogen significantly influenced (p<0.01) all the studied variables of nutrient accumulation (N, P, K, Ca and Mg), Na⁺/K⁺, Na⁺/Ca⁺⁺ and Na⁺/Mg⁺⁺ ratios, chlorophyll b, electrolyte leakage and SDB accumulation. In addition, there was significant effect of EC_w on the accumulation of N, P, K, Mg, Na⁺/K⁺, Na⁺/Mg⁺⁺ and shoot biomass accumulation (p<0.01) and on Ca⁺⁺ and Na⁺/Ca⁺⁺ (p<0.05). There was no effect (p>0.05) of forms of nitrogen and water electrical conductivity on chlorophyll a and carotenoids.

The plants fertilized with NO₃^- had higher accumulation of macronutrients than those fertigated with nutrient solution containing NH₄⁺, with increments of 25.5%, 54.0%, 61.4%, 165.3% and 215.9% for N, P, K, Ca and Mg, respectively (Figures 1A-E).

Figure 1
Accumulation of nitrogen - N (A), phosphorus - P (B), potassium - K (C), calcium - Ca (D) and magnesium - Mg (E) in Italian zucchini plants fertilized with different forms of nitrogen and irrigated with saline water. Means followed by different letters indicate significant difference by Tukey test at 0.05 probability level.

In relation to the effects of irrigation water salinity, there were linear reductions in the accumulation of macronutrients in the tissue of zucchini plants with the increase of EC_w, which were equal to 32.8%, 40.8%; 39.2%, 36.8% and 37.6% for N, P, K, Ca and Mg, respectively, between the high and low salinity levels (Figures 2A-E).

Figure 2
Accumulation of nitrogen (N) (A), phosphorus (P) (B), potassium (K) (C), calcium (Ca) (D) and magnesium (Mg) (E) in Italian zucchini plants irrigated with saline waters. * - Significant at 0.05 probability level (p<0.05).

Na accumulation in the shoots of Italian zucchini was 124.3% higher in plants fertilized with NO₃^- compared to plants nourished with NH₄⁺ (Figure 3A). In addition, there were also higher values of Na⁺/Ca⁺⁺ and Na⁺/Mg⁺⁺ ratios in plants fertilized with ammonium, with a 25.8% difference for Na⁺/Ca⁺⁺ and 54.6% difference for Na⁺/Mg⁺⁺ (Figures 3C and E). In relation to Na⁺/K⁺, Na⁺/Ca⁺⁺ and Na⁺/Mg⁺⁺ as a function of the increment in irrigation water salinity, there were similar responses for these variables and their data fitted to the quadratic regression model, reaching the highest values (0.30, 0.39 and 1.91 for Na⁺/K⁺, Na⁺/Ca⁺⁺ and Na⁺/Mg⁺⁺, respectively) at the EC_w from 4.1 dS m^-1 (Figures 3B, D and F).

Figure 3
Accumulation of sodium (Na⁺) (A), sodium/potassium ratio (Na⁺/K⁺) (B), sodium/calcium ratio (Na⁺/Ca⁺⁺) (C and D) and sodium/magnesium ratio (Na⁺/Mg⁺⁺) (E and F) in Italian zucchini plants nourished with different forms of nitrogen and irrigated with saline waters. Means followed by different letters indicate significant difference by Tukey test at 0.05 probability level. * and ^ns - Significant at 0.05 probability level (p<0.05) and not significant (p>0.05), respectively.

The use of ammoniacal nitrogen increased the concentration of chlorophyll b in the leaves of zucchini by 10.5% (Figure 4A). Regarding the state of membrane integrity, zucchini plants fertilized with NH₄⁺ showed EE values more than two times higher than plants fertilized with NO₃^- (Figure 4B). The mean values obtained in the presence of the two forms of nitrogen were 49.3 and 24.2% for NH₄⁺ and NO₃^- (Figure 4B).

Figure 4
Chlorophyll b content (A) and electrolyte leakage (B) in Italian zucchini plants nourished with different forms of nitrogen and irrigated with saline waters. Means followed by different letters indicate significant difference by Tukey test at 0.05 probability level.

Ammonium toxicity can be seen in Figure 5. Visually, in both forms of N, the growth of plants is reduced by the increase in the electrical conductivity of irrigation water, with the greatest reductions in plants fertilized with NH₄⁺. Plants fertilized with NO₃^- reduced growth due to the increase in saline levels of irrigation water, however, these plants managed to emit a good number of flowers at the highest level of salinity (6.5 dS m^-1). On the other hand, plants fertilized with NH₄⁺ showed reduced growth and marginal burns on the leaves in relation to plants fertilized with NO₃^- in all saline levels, with more evident reductions in salinity levels from 5.0 dS m^-1, in which plants did not even managed to emit flowers.

Figure 5
Italian zucchini plants fertilized with different forms of nitrogen and irrigated with saline waters.

Dry biomass accumulation was 62.8% higher in plants fertilized with NO₃^- in comparison to those nourished with NH₄⁺ (Figure 6A). In relation to salinity, shoot dry biomass was reduced by 31.4% as the salinity level increased from 0.5 to 6.5 dS m^-1 (Figure 6B), corroborating with the results of nutrient accumulation. As for production, it was observed that only plant fertilized with NO₃^- reached the fruiting stage, while plants nourished with ammonium (NH₄⁺) did not produce and died within a few days after flowering, regardless of the salinity level (Figure 6C). Regarding the effects of salinity, there was a linear reduction in the production of plants nourished with NO₃^-, with a 91.8% reduction in the production per plant between the EC_w levels of 0.5 and 6.5 dS m^-1 (Figure 6C).

Figure 6
Shoot dry biomass (SDB) (A and B) and production (PP) (C) of Italian zucchini plants fertilized with different forms of nitrogen (♦ Nitrate and ■ Ammonium) and irrigated with saline waters (B). Means followed by different letters indicate difference by Tukey test at 0.05 probability level. * = Significant at 0.05 probability level (p<0.05).

4. Discussion

Salt stress is caused by excess ions in the rhizosphere, limiting water extraction by the roots and reducing plant growth, while the secondary effects are caused by ionic imbalance, resulting in inactivation of enzymes, lack of nutrients, ionic toxicity in tissues and oxidative stress (Nazar et al., 2011). Thus, as observed in the Italian zucchini, salinity affects the establishment, growth, development and production of plants, leading to a significant loss of yield or even death (Acosta-Motos et al., 2017).

The reductions in the accumulation of elements such as N, K, Ca and Mg in plant tissues as a consequence of the effects of salinity occur due to the competition between the ions Cl^- and NO₃^- and between the ion Na⁺ and the ions K⁺, Ca⁺⁺ and Mg⁺⁺. Ionic competition causes changes in the availability, absorption, transportation, assimilation and distribution of these elements in the plant, resulting in lower accumulation in its aerial parts, as reported by Carmo et al. (2011); these authors demonstrated that plants of pumpkin irrigated with water of electrical conductivity of 4.38 dS m^-1 reduce the accumulation of N, P, K, Ca and Mg in their tissues by 30.4%, 16.4%, 22.5%, 50.5% and 14.4%, respectively.

Excessive accumulation of elements in plants, especially sodium, inhibits their growth and production due to ionic toxicity, nutritional imbalances or both, simultaneously (Sá et al., 2015). Toxicity causes changes in the ionic ratios Na⁺/K⁺, Na⁺/Ca⁺⁺, Na⁺/Mg⁺⁺ and Cl^-/NO₃^-, affecting photophosphorylation, respiratory chain, nutrient assimilation and the metabolism of proteins and other organic compounds, which causes changes in the entire plant metabolism (Viudes and Santos, 2014).

According to Azevedo Neto and Tabosa (2000), determining the ratios of sodium with the macronutrients potassium, calcium and magnesium (Na⁺/K⁺, Na⁺/Ca⁺⁺ and Na⁺/Mg⁺⁺) is fundamentally important when the aim is to analyze the nutritional status of plants subjected to salt stress, because they indicate their state of nutritional stress. Some authors recommend that ionic ratios should be lower than 0.60 in glycophytes so that there are no losses in their metabolism (Garcia et al., 2007). Based on these criteria, the Na⁺/Mg⁺⁺ ratios (Figure 3F) in the Italian zucchini were more than three times higher than that considered appropriate for development.

The reductions in the accumulation of the macronutrients N, P, K, Ca and Mg in the shoots of zucchini plants fertilized with NH₄⁺, compared to plants nourished with NO₃^-, are attributed to the greater reductions caused in the biomass accumulation in these plants when they received this type of fertilization (Figure 6A), since the total amount of macronutrients accumulated in their tissue is directly related to the dry biomass accumulation. These results corroborate those obtained by other authors, which have shown that plants nourished exclusively with nitrogen in the ammoniacal form may have lower contents of elements such as Ca⁺⁺ and Mg⁺⁺ in their tissues, as reported by Borgognone et al. (2013) in tomato plants and by Savvas et al. (2010) in eggplant plants.

In the Italian zucchini, some symptoms of NH₄⁺ toxicity were found, such as reduced growth, leaf chlorosis and marginal leaf burns (Figure 5). According to Esteban et al. (2016), these symptoms are due to changes in the ionic balance of plants, since the excess of NH₄⁺ inhibits the uptake of other cations, such as K⁺, Mg⁺⁺ and Ca⁺⁺. In addition, excess NH₄⁺ also causes, among other things, intracellular alkalinization, extracellular acidification, interference with photosynthetic activity, alteration in the assimilation of enzymes, interruption of hormonal homeostasis and increased oxidative stress (Britto and Kronzucker, 2002; Cruz et al ., 2011; Bittsánszky, et al., 2015; Esteban et al., 2016). This fact is confirmed by the high leakage of electrolytes in the leaves of zucchini.

The reduction in membrane stability occurs due to lipid peroxidation caused by reactive oxygen species (ROS), such as the superoxide radical (O₂^-), singlet oxygen (¹O₂), the hydroxyl radical (OH⁻) and hydrogen peroxide (H₂O₂) (Singh et al., 2007; Ashraf and Harris, 2004; Sá et al., 2017). As there was no significant effect of ECw on EE, it is deduced that this greater degradation in the membranes of plants fertilized with NH₄⁺ happened due to the cytotoxic effects provided by the exclusive absorption of NH₄⁺ by the zucchini plants; and the increase in the content of chlorophyll b in Italian zucchini fertilized with NH₄⁺ is indicative that the plant is trying to compensate for the loss caused to the photosynthetic apparatus, with increased synthesis of pigments accessory to light capture (Sá et al., 2017).

Although the ammoniacal fertilization improved ionic homeostasis (Na⁺/Ca⁺⁺ and Na⁺/Mg⁺⁺), Italian zucchini plants nourished with NH₄⁺ were not able to produce fruits. The pollinated flowers were not fertilized and ultimately fell. Possibly, fertilization did not occur because the pollen was non-viable, given that the NH₄⁺ ion can promote biochemical and physiological alterations in plants, such as changes in the intracellular pH and metabolism of hormones (Li et al., 2014). Thus, exclusive fertilization with NH₄⁺ is toxic to zucchini plants, with more harmful effects at the flowering stage, so only plants fertilized with NO₃^- reached the fruiting stage (Figure 6C).

In summary, Italian zucchini plants nourished only with ammoniacal nitrogen in the standard nutrient solution promotes greater damage to the leaf membrane and reduced their accumulation of macronutrients and increased their Na⁺/K⁺, Na⁺/Ca⁺⁺ and Na⁺/Mg⁺⁺ ratios in the shoots. Irrigation with water above 2.0 dS m^-1 reduces the accumulation of nutrients in the shoots and the production of Italian zucchini plants. The toxicity of NH₄⁺ under Italian zucchini plants overlap the toxicity of the salinity, since fertilization with this form of nitrogen inhibits its production, so the NO₃^- form is the most adequate for its cultivation.

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Publication Dates

• Publication in this collection
  04 June 2021
• Date of issue
  2022

History

• Received
  31 Jan 2020
• Accepted
  03 Nov 2020