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Response of four woody species to salinity and water deficit in initial growth phase/ Resposta de quatro especies lenhosas a salinidade e deficit hidrico em fase inicial de crescimento.

Introduction

Forest resources involving the areas with tree species have undergone extensive exploitation and still suffer other types of damages, arising not only from anthropogenic causes, but also from biotic and abiotic factors, such as soil salinity and water deficit, common in semi-arid regions.

In semi-arid regions, high evapotranspiration rates and low rainfall levels contribute to the accumulation of soluble salts in the soil, and this process is intensified in areas with drainage problems. Under salinity conditions, plants exhibit symptoms such as necrosis and burns at leaf edges, usually caused by sodium and chlorine salts; however, the main response to the toxic and osmotic effects caused by salts is the reduction in plant growth (Taiz & Zeiger, 2013).

The use of species with higher tolerance to salinity has been a strategy recommended in the recovery of soils degraded by the excess of salts and sodium (Qadir et al., 2007; Miranda et al., 2018). However, few studies with this focus have been conducted with tree species under Brazilian semi-arid conditions, and particularly with native plants of the Caatinga. Many of the species in this ecosystem have potential for multiple uses, but studies on their tolerance to salinity are still scarce (Silva et al., 2008; Bessa et al., 2017), notably under field conditions.

Another relevant issue is that salinity does not act in isolation under natural conditions, and the imposition of multiple stresses on plants is more rule than exception (Larcher, 2000; Mittler, 2006). Thus, plants growing in salt-affected soils may also suffer action of other abiotic stress factors, such as water deficit or excess. These factors acting together can intensify the negative effects on plants (Silva et al., 2017), hindering the process of revegetation of these areas, being particularly decisive in the establishment of seedlings under these conditions (Silva et al., 2016; Medeiros et al., 2018).

In this context, with the increasing need for recovery of areas degraded by salinization and solonization, there has been an increased interest in forest species adapted to the semi-arid region and with capacity for establishment under such soil conditions, associated with the water restriction that characterizes a significant part of the Northeast region of Brazil. Therefore, this study aimed to evaluate the initial growth of four forest species, three native to the Caatinga and one exotic, under conditions of salinity and water deficit.

Material and Methods

The experiment was conducted at the Center of Education and Research in Urban Agriculture (NEPAU) of the Plant Science Department of the Federal University of Ceara--UFC, located in Fortaleza, CE, Brazil (3[degrees]44' S; 38[degrees]33'W; ~20 m), from April 11 to September 5, 2014.

To compose the treatments with levels of salts, a soil classified as Fluvic Neosol (EMBRAPA, 2006) was collected at different points in the Irrigated Perimeter of Morada Nova. The points were selected based on in-situ analysis of soil electrical conductivity in the 0-20 cm layer, using a Wet Jet sensor (Delta T--Devices, Cambridge, England). After collection, this soil was pounded to break up clods and sieved through a 5-mm mesh, and electrical conductivity of the saturated soil (EC) was measured, resulting in two salinity treatments (1.2 and 8.6 dS [m.sup.-1]).

Four forest species were used in the experiment: three native to the Caatinga, 'Aroeira' (Myracrodruon urundeuva Fr Allemao), 'Sabia' (Mimosa caesalpiniifolia Benth) and 'Ipe roxo' (Tabebuia impetiginosa (Mart. ex. DC.) Standl) and one exotic species, Neem (Azadirachta indica A. Juss). Species from the Caatinga were selected based on the previous knowledge on their responses to saline stress alone in the seedling stage (Bessa et al., 2017). It is necessary to evaluate their responses to multiple stress conditions and compare them with an exotic species, in this case Neem, which has aroused the interest of various producers due to its rusticity.

Seedlings were produced in greenhouse under 50% shading by sowing on polystyrene trays with 128 cells and substrate of sand + earthworm humus at 2:1 proportion, where they remained for 20 days and were daily irrigated by micro sprinklers using well water with electrical conductivity of 0.7 dS [m.sup.-1].

At 20 days after sowing, the seedlings were selected according to uniformity and transplanted to 8-L pots containing a 5-cm-layer of crushed stone at the bottom and filled with soils with different levels of salinity. To reduce the impact of the direct contact between seedling root system and saline soil, the holes in each pot received an adequate volume of washed river sand (Bessa et al., 2017). The treatment with water restriction was only applied 20 days after transplanting (DAT). Plants remained in the pots until 120 DAT and were manually irrigated every day.

The experimental design was completely randomized, in a triple factorial scheme, 4 x 2 x 2, relative to four forest species ('Aroeira', 'Ipe', 'Sabia' and Neem), two salinity levels (1.2 and 8.6 dS [m.sup.-1]) and two water regimes (with and without water restriction, WR and WoR, respectively). Four replicates were used, totaling 64 experimental units.

Water regime treatments were obtained by applying water depths equivalent to 100 and 50% in the treatments without restriction (WoR) and with restriction (WR), respectively, based on reference evapotranspiration determined by the Class A pan method. Plants were subjected to different treatments at 21 DAT and remained under different water regimes until 120 DAT.

At the end of the experiment, plant height (PH), stem diameter (SD), number of leaves (NL), shoot dry matter (SDM), root dry matter (RDM) and total dry matter (TDM) were measured.

The results were subjected to analysis of variance by F test and means were compared by Tukey test at 0.05 probability level, using the program Assistat, beta version 7.6 (Silva & Azevedo, 2016).

Results and Discussion

The factors A (species) and B (salinity), individually, had significant effect on all variables studied (p < 0.01 or p < 0.05). On the other hand, the factor water deficit (C) and the interaction between factors (A x B x C) did not cause any statistical difference (p > 0.05). The interactions A x B and B x C had significant effect only on SDM (p < 0.05), whereas the interaction A x C had significant effect on SD (p < 0.05), SDM (p < 0.05) and TDM (p < 0.01).

In Figure 1A, it is possible to note the difference in plant height between Neem and the other species. On average, Neem was 54% superior, which caused it to be statistically different from the others. The species 'Aroeira, 'Ipe' and 'Sabia' had heights of 33.75, 33.25 and 41.5 cm, respectively. According to the statistical difference found between the soils without salinity (WoS) and with salinity (WS) regarding the mean height of the evaluated species (Figure 1B), PH was higher when plants were grown in soil without salinity.

The reduction of growth observed in the saline treatment act as an adaptive mechanism of the plant to salt stress, providing conditions for it to maintain its vital activities, even in limited manner. In addition, the development stage in which the stress occurs is also critical (Pimentel, 2004), because it can affect the vegetative and reproductive development of the plant.

Figure 2A shows the difference between treatments without water restriction (WoR) and with water restriction (WR) for stem diameter (SD) in the species Neem and 'Aroeira'. Such difference was not observed for the species 'Ipe' and 'Sabia'. For the mean SD of the analyzed species as a function of salinity (Figure 2B), the WoS condition led to SD of 5.94 mm, higher than the value found for the WS condition, 4.69 mm.

Part of the results in the present study can be explained by the comments of Sun et al. (2009) and Yao et al. (2010), who mentioned the possibility of difference in effect of salinity between plant species and between development stages of a same genotype. According to Nery et al. (2009), the reduction in stem diameter growth is more expressive than the growth in plant height.

Figure 3A shows the graphical representation of the test of means for number of leaves (NL) as a function of the forest species. As occurred with plant height and stem diameter, Neem was also superior with respect to this variable. For NL, as a function of salinity in the analyzed species (Figure 3B), there was a 30% reduction in the treatment WS, compared with the WoS treatment, and this response was independent of the other factors studied.

For SDM as a function of the forest species (Figure 4A), the values were higher in Neem (8.79 g), which differed from the other species. 'Aroeira, 'Ipe' and 'Sabia' had values of 2.78, 2.11 and 3.18 g, respectively, with no statistical difference from one another. For SDM as a function of the interaction between salinity and water regime (Figure 4B), the WoS condition caused higher values compared with the WS condition. The percentage reduction in SDM for the WoR and WR conditions between both salinity levels (WoS and WS) were respectively on the order of 53 and 56%. Thus, it can be noted that the factor which most contributed to the reduction in SDM was soil salinity. Somehow, these reductions can be adaptive responses for plants to survive under stress, allowing them to have multiple resources to resist under adverse conditions.

Results similar to those observed in this study were found by Freire & Rodrigues (2009), who studied the development of Leucaena leucocephala in saline and non-saline soils and observed that there was greater shoot and total dry matter accumulation in non-saline soil. However, the effect of soil salinity was more pronounced on the shoots, causing a 60% reduction in the dry matter in comparison to plants grown in non-saline soils. Similarly, Gomes et al. (2011), in studies with Tabebuia aurea seedlings, observed that salinity significantly reduced shoot dry matter accumulation.

In the graphical representation of RDM as a function of the species (Figure 5A), the species Neem, 'Ipe' and 'Sabia' were statistically different from one another, with absolute values of 6.10, 4.44 and 2.04 g, respectively. For RDM as a function of salinity (Figure 5B), the trend was the same as that for SDM, since plants had lower values of SDM in the treatment with greater imposition of salt stress.

These responses can be justified possibly by the inhibition caused by the salt stress in vital processes, such as photosynthesis and synthesis of proteins (Parida & Das, 2005). As a consequence, there may have been a reduction in leaf surface expansion, with considerable decrease in leaf area, fresh and dry biomass of leaves and roots (Chartzoulakis & Klapaki, 2000), consequently leading to a significant decrease in plant growth rate (Rhoades et al., 1992). Silva et al. (2005) studying 'Favela' (Cnidosculus Phyllacanthus Pax & K. Hoffm), observed that salt stress significantly inhibited the production of root dry matter (RDM) and shoot dry matter (SDM), particularly at the highest level of irrigation water salinity.

Corroborating the results found in this study, Silva et al. (2009) worked with the species 'Sabia' in a greenhouse and found that saline stress significantly inhibited the production of RDM and SDM, particularly at the highest level of irrigation water salinity (T6 = 6 dS [m.sup.-1]), and that these plants exhibited symptoms of early senescence and ionic toxicity (leaf burns), at 60 days of application of the treatments.

Figure 6 shows a graphical representation of the test of means for total dry matter (TDM) as a function of the interaction between species and water regime (A) and salinity (B). In Figure 6A, it is possible to see the superiority of the WoR treatment for Neem, and there were no effects of water restriction on the other species with respect to this variable. In general, the species 'Aroeira', 'Ipe' and 'Sabia' did not show any statistical difference, either between species or water regimes. Conversely, in the graphical analysis of TDM as a function of salinity (Figure 6B), there was statistical difference between the two treatments, with values of 10.98 and 5.39 g for WoS and WS, respectively, which represents a reduction of 50% between treatments.

The large reduction caused by salt stress is partially due to the high concentrations of sodium salts, which negatively affect plant physiology by causing ionic, osmotic and nutritional interactions deleterious to plant cells (Hasegawa et al., 2000; Taiz & Zeiger, 2013; Bessa et al., 2017). These responses, however, occur at different intensities according to the tolerance of plant species, with effects on biomass production (Chaves et al., 2009; Bessa et al., 2017).

The effects of salinity and water deficit on the total dry matter of the species studied in this work also reflect the effects observed on shoot dry matter and root dry matter. It can also be noted that, for all variables analyzed, the water regime with application of 50% water requirement was not sufficient to affect biomass production.

Conclusions

1. The 50% reduction in water replacement for seedlings of the four species studied was not enough to cause significant damages to their growth.

2. Based on shoot dry matter production, Neem behaved as moderately tolerant, whereas the other species were moderately sensitive to salinity.

3. The applied water deficit was not enough to intensify the effects of salt stress under the studied conditions.

DOI: http://dx.doi.org/10.1590/1807-1929/agriambi.v22n11p753-757

Ref. 186825--Received 19 Oct, 2017 * Accepted 11 Jun, 2018 * Published 14 Sept, 2018

Acknowledgments

The authors thank the National Institute of Science and Technology in Salinity--INCTSal and National Council for Scientific and Technological Development--CNPq, for the financial support, and to the Coordination for the Improvement of Higher Education Personnel--CAPES for granting the scholarship to the first author.

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Alan D. Lima (1), Francisco M. S. Bezerra (1), Antonia L. R. Neves (1), Carlos H. C. de Sousa (1), Claudivan F. de Lacerda (1) & Antonio M. E. Bezerra (2)

(1) Universidade Federal do Ceara/Departamento de Engenharia Agricola/Programa de Pos-Graduacao em Engenharia Agricola. Fortaleza, CE. E-mail: alandinizlima@yahoo.com.br (Corresponding author)--ORCID: 0000-0001-6939-4210; mardonesagronomia@gmail.com--ORCID: 0000-0002-82788182; leilaneves7@hotmail.com--ORCID: 0000-0002-2555-5390; sousaibiapina@yahoo.com.br--ORCID: 0000-0001-9462-4647; cfeitosa@ufc.br--ORCID: 0000-0002-5324-8195

(2) Universidade Federal do Ceara/Departamento de Fitotecnia/Programa de Pos-Graduacao em Fitotecnia. Fortaleza, CE. E- mail: esmeraldo@ufc.br ORCID: 0000-0003-0060-5803

Caption: Figure 1. Graphical representation of the test of means for plant height (PH) for the evaluated species (A) and salinity (B)

Caption: Figure 2. Graphical representation of the test of means for stem diameter (SD) as a function of the interaction between species and water regime (A) and salinity (B)

Caption: Figure 3. Graphical representation of the test of means for number of leaves (NL) for the evaluated species (A) and salinity (B)

Caption: Figure 4. Graphical representation of the test of means for shoot dry matter for the evaluated species (A) and interaction between salinity and water regime (B)

Caption: Figure 5. Graphical representation of the test of means for root dry matter (RDM) for the evaluated species (A) and salinity (B)

Caption: Figure 6. Graphical representation of the test of means for total dry matter (TDM) as a function of the interaction between species and water regime (A) and salinity (B)
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Author:Lima, Alan D.; Bezerra, Francisco M.S.; Neves, Antonia L.R.; de Sousa, Carlos H.C.; de Lacerda, Clau
Publication:Revista Brasileira de Engenharia Agricola e Ambiental
Date:Nov 1, 2018
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