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Growth and chlorophyll in noni seedlings irrigated with saline water in substrate with vermicompost/ Crescimento e clorofila em mudas de noni irrigadas com agua salina em substrato com vermicomposto.

INTRODUCTION

Noni (Morinda citrifolia L.) is a fruit crop belonging to the family Rubiaceae, originally from Micronesia, according to Razafimandimbison et al. (2010). It was recently introduced in Brazil, where its planting is focused on commercial cultivation (Silva et al., 2014). This species has aroused the interest of consumers due to its medicinal properties.

This plant is highly adaptable to tropical countries, standing out for its ability to develop in soil, climate and extreme environment conditions (Basar et al., 2010; Souto et al., 2015a). It is considered a salinity-tolerant crop for surviving in areas flooded by tsunamis and saline environments, without presenting symptoms of foliar toxicity (Silva & Cavalcante, 2014). Souto et al. (2016) observed that noni plants in soil without salt leaching did not survive when irrigated with water salinity of 5.28 dS [m.sup.-1].

Irrigation is a fundamental factor for the development of crops, especially in semi-arid and arid regions, since water sources in these regions contain salts, which can accumulate in the soil and in the plant. The accumulation of salts can cause alterations of the physical and chemical attributes of the soil and, by the action of the specific ions, on the germination, growth, production and plant nutrition (Amorim et al., 2010; Cavalcante et al., 2010; Nazario et al., 2010).

There are several alternatives to mitigate the effects of irrigation water salts on plants, e.g., the application of organic inputs in the soil, such as the humus from vermicomposting, which is a low-cost technological system (Bassaco et al., 2015). This compound, in addition to generating a nutrient-rich material, easily assimilated by plants, contains organic material of high molecular weight such as fulvic acids, humic acids and humin (Fernandes et al., 2009; Yadav & Garg, 2011).

Based on these considerations, this study aimed to evaluate the growth and chlorophyll index of noni in response to the salinity of irrigation water in substrates with and without vermicompost.

MATERIAL AND METHODS

The experiment was conducted from April 2015 to January 2016, in a greenhouse located at the Centro de Humanas, Sociais e Ciencias Agrarias (CCHSA) of the Universidade Federal da Paraiba (UFPB) in the municipality of Bananeiras, PB, Brazil.

Bananeiras is located in the Agreste' Mesoregion and 'Brejo' Microregion of Paraiba State, at the geographic coordinates 6[degrees]46' S and 35[degrees]38' W, at 552 m of altitude. The climate in the region is classified as As', which means hot and humid (Brasil, 1972). The rainy season occurs from April to August and the dry season from September to December. The accumulated rainfall during the experiment was 1,242 mm (AESA, 2017).

For the substrate preparation, the soil was collected at 20 cm depth in an Oxisol in the Agricultural Sector of the CCHSA/ UFPB. The earthworm humus was obtained from the seedbed vermicomposting, carried out in the seedling nursery of the institution. The organic residues used to feed the red californian earthworms (Eisenia foetida) were plant remains collected in the agricultural area of the abovementioned institution. The humus was obtained with 90 days. After being removed from the seedbed, the humus was dried in the shade.

The chemical characterization of soil and humus was performed according to EMBRAPA (2014) and the results obtained are shown in Table 1.

The treatments were distributed in a completely randomized design, with four repetitions using the 4 x 3 factorial design, corresponding to four levels of electrical conductivity of the irrigation water (0.5, 1.5, 3.0 and 4.5 dS [m.sup.-1]), and three substrates (soil without humus, soil with 33.33 and with 66.66% of humus). One noni plant in a 5 L plastic pot represented each experimental unit, totalizing 48 pots distributed in rows of 1.0 m in line and 1.0 m between the plants.

The seeds were obtained from mature fruits in adult noni plants one year old in the experimental area of CCHSA/UFPB. The ripe fruits were collected and, their pulp was removed and then the seeds were washed in running water to remove the remaining pulp.

For breaking the dormancy of noni seeds (integument dormancy), the most effective method (Leite et al., 2012) was used, by immersion of noni seeds in water for 48 h. After the immersion, the sowing was carried out in plastic pots. Three seeds were sown in each experimental unit (pot). The thinning was performed 90 days after germination, leaving one plant in each pot.

The electrical conductivities of irrigation water were obtained based on the empirical relation proposed by Richards (1980). The salt used was sodium chloride; it was dissolved in water and the electrical conductivity was subsequently measured using a portable conductivity meter.

The entire irrigation period was carried out with salinity, from germination to plant removal. During the first 60 days after sowing (DAS), irrigation was performed manually, based on the weighing process, providing every 24 h the volume of evapotranspired water in each treatment in order to raise soil moisture (Souto et al., 2013). After this period, irrigation was performed three times a week.

Plant evaluations were carried out 95 days after sowing. Plant height, corresponding to the distance between the collar and the insertion of the last pair of leaves in the plant, was measured using a millimeter ruler. Stem diameter was measured using a Digimess@ 300 digital Caliper, at 10 cm from the plant collar, where it was marked with a dot made with ink to avoid experimental error. The number of leaves was counted in each plant.

A portable chlorophyll meter (CFL1030 ClorofiLOG') was used to measure chlorophyll index in the central leaflet of the third expanded leaf of the plants, with two readings per leaf. From the readings, the device provided values proportional to the absorbance of chlorophylls a, b and total (a + b) in dimensionless units called FCI values--Falker Chlorophyll Index (Falker Automacao Agricola Ltda, 2008).

After the end of the experiment, the fresh matter of shoots and roots was determined. Then, the plants were placed in an oven with air circulation at 65[degrees]C for 72 h. After total drying, the dry matter of shoots and roots was evaluated.

The data were submitted to analysis of variance, and for the variables for which the interaction was not significant, the Tukey test was applied at p < 0.05 for the substrates and the regression for the electrical conductivity of irrigation water. The Statistical Analysis System (SAS Institute, 2012) was used to process the data.

RESULTS AND DISCUSSION

From the summary of the analysis of variance, it was observed that plant height, fresh root biomass, dry root biomass and chlorophyll a were significantly influenced by the interaction between salinity and soil substrate. It is also verified that the stem diameter, number of leaves, fresh shoot biomass and total chlorophyll were influenced by electrical conductivity of the irrigation water and substrate (Table 2).

There was a quadratic effect on plant height with the increase of the electrical conductivity in the irrigation water in the substrate without humus. In the substrates with 33.33 and 66.66% of humus, there was a decreasing linear effect (p [less than or equal to] 0.05) with increased salinity (Figure 1).

In the substrate without humus the plant growth was limited by the nutritional deficiency, as verified in the soil chemical analysis (Table 1), therefore the effect of salt stress was not the main limiting factor in plant height.

The addition of humus increased the absortion of nutrients by the plants in conditions of salinity; therefore, the growth in height was superior to that of plants not treated with humus.

In this way the humus solved the nutritional problem, due to the action of the humic matter in the improvement of the water storage capacity of the soil, besides providing nutrients (Fernandes et al., 2009).

The increase of salinity in irrigation water from 0.5 to 4.5 dS [m.sup.-1] caused a decrease of 44.2 and 43.5% in the height of the plants of the treatments with 33.33 and 66.66% of humus, respectively, in comparison to the control.

Salinity affects the ion activity in solution and in the processes of absorption, transport, assimilation and distribution of nutrients (Neves et al., 2009).

It was verified that with increasing electrical conductivity of the irrigation water there was a decreasing linear effect (p [less than or equal to] 0.05) in the treatment with 66.66% of humus and quadratic effect with addition of 33.33% of humus, for dry root biomass (Figure 2).

In the absence of humus, the root system of the plants was poorly developed compared to the substrate with the highest vermicompost addition, supposedly due to nutritional restriction. By comparing the results between the plants irrigated with water of highest and lowest electrical conductivity, losses of 26.88 and 80.24 g were observed for those maintained in the soil with 33.33 and 66.66% of humus, respectively.

Based on the results, the salt stress compromised the biomass production of the root system in response to the depressive effects of salinity. According to the level of salts, salinity can cause nutritional imbalance, loss of chlorophyll and photosynthetic activity, reduction in the production of leaves, roots and leaf area (Souto et al., 2013, 2015b).

In addition, the negative effect of salinity on the dry matter of noni plants is attributed to the decrease in the osmotic potential of the soil solution which reduces the capacity of the plant to absorb water and nutrients, mainly due to the increase of the concentrations of soluble salts in the soil. Under these conditions, the plants diminish their vegetative growth and develop the root system to supply the need for nutrients and water (Asik et al., 2009; Alves et al., 2011).

It is observed in Figure 3 that there was a decreasing linear effect (p [less than or equal to] 0.05) with the increase of the electrical conductivity in the irrigation water in the substrate without humus. With the addition of humus, the index of chlorophyll a increased, reaching the highest value (44.31 FCI) in the substrate with 66.66% humus and irrigated with 0.5 dS [m.sup.-1].

The addition of vermicompost increased the presence of N (61.8%) and Mg (81.63%) in the substrate (Table 1). The higher availability of these elements has possibly increased the photosynthetic efficiency of the plants, and consequently the chlorophyll a index, as can be observed in the substrates with humus addition.

With an increase in the electrical conductivity, without humus, lower values of chlorophyll a index were observed. High levels of salts absorbed by plants contribute to an increase in the activity of chlorophyllase, an enzyme that degrades chlorophyll (Lima et al., 2004) and inhibits the photosynthetic action of plants (Taiz & Zeiger, 2013). The results of Souto et al. (2015b) show that salt stress reduces chlorophyll index.

There was no statistical difference for stem diameter and number of leaves with the use of 33.33 and 66.66% of humus in the substrate. For all others variables a positive effect was observed for the vermicompost in the proportion of 66.66% (Table 3).

The plants showed better vegetative performance in the presence of humus in comparison to the control, proving a nutritional deficiency in the soil. Humus is a source of essential nutrients for the development of plants, containing phosphorus, sulfur, nitrogen and also some micronutrients (Goes et al., 2011).

The humus contributes to the increase of the cation exchange capacity of the soil, improving its physical and chemical properties (Goes et al., 2011). In addition, it decreases the depressive effects of salinity of irrigation water, not severely compromising the growth and biomass production of noni plants, as observed in this study.

CONCLUSIONS

1. The increase of salinity in irrigation water decreases growth and chlorophyll a and total chlorophyll indexes, but with lower intensity in substrates with humus.

2. Humus improves the fertility of the substrate and favors the growth of noni plants, regardless of the salinity of the irrigation water. However, the beneficial effect decreases with the intensification of salt stress.

Ref. 200253--Received 21 May, 2018 * Accepted 16 Jun, 2019 * Published 01 Jul, 2019

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DOI: http://dx.doi.org/10.1590/1807-1929/agriambi.v23n8p586-590

Daiane G. dos Santos (1), Belisia L. M. T. Diniz (2), Manoel A. Diniz Neto (2), Joao H. C. S. Silva (3), William N. de Oliveira Filho (4) & Roberto M. Ferreira Filho (4)

(1) Universidade Federal da Paraiba/Centro de Ciencias Agrarias/Programa de Pos-Graduacao em Zootecnia. Areia, PB, Brasil. E-mail: daianeagro@outlook.com (Corresponding author)--ORCID: 0000-0001-9629-0441

(2) Universidade Federal da Paralba/Departamento de Agricultura. Bananeiras, PB, Brasil. E-mail: belisia.diniz@gmail.com--ORCID: 0000-0002-7580-2433; diniznetto@gmail.com--ORCID: 0000-0002-3190-8682

(3) Universidade Federal da Paraiba/Centro de Ciencias Humanas, Sociais e Agrarias/Programa de Pos-Graduacao em Ciencias Agrarias (Agroecologia). Bananeiras, PB, Brasil. E-mail: joaohenriqueconst@gmail.com--ORCID: 0000-0001-6218-5096

(4) Universidade Federal da Paraiba/Centro de Ciencias Agrarias/Programa de Pos-Graduacao em Ciencia do Solo. Areia, PB, Brasil. E-mail: wnovaes39@gmail.com --ORCID: 0000-0003-4035-8245; robertomonteiroff@yahoo.com--ORCID: 0000-0002-2905-258X

Caption: Figure 1. Height of noni plants as function of irrigation water electrical conductivity in three substrates

Caption: Figure 2. Dry root biomass of noni plants as function of irrigation water electrical conductivity in three substrates

Caption: Figure 3. Leaf chlorophyll a in noni plants as function of irrigation water electrical conductivity in three substrates
Table 1. Chemical characterization of soil and humus

            pH            P         [K.sup.+]   [Na.sup.+]

        [H.sub.2]O       (mg [dm.sup.-3])      ([cmol.sub.c]
         (1:2.5)                                [dm.sup.3])

Soil       4.93         32.36        220.00        0.22
Humus      6.84         731.04       1900.00       3.04

        [H.sup.+] +   [Al.sup.+3]   [Ca.sup.+2]   [Mg.sup.+2]    SB
        [Al.sup.+3]
                      ([cmol.sub.c] [dm.sup.3])

Soil       9.41          0.65          2.20          1.10       4.08
Humus      0.50            0           13.00         6.00       26.89

         CEC             V       M          0M

        ([cmol.sub.c]        (%)          (g [kg.sup.-1])
        [dm.sup.3])

Soil    13.49           30.26   13.74       65.22
Humus   27.39           98.17     0        170.70

SB--Sum of bases, CEC--Cation exchange capacity, V--Exchangeable
base saturation, M--saturation by aluminum, OM--Organic matter
in the soil

Table 2. Summary of analysis of variance of the effect of
irrigation water salinity (S) and substrate (SU) on the
initial growth of the noni plant

SV         DF                 Mean square

                   PH          SD         LN          FSB

S          3    51.11 **    6.80 **    6.30 **     742.17 *
SU         2    196.77 **   41.47 **   12.07 **   26910.39 **
SxSU       6     5.80 **     0.67NS     0.64NS     306.98NS
Residual   36    1.15569     0.3427     0.3051     206.3396
CV (%)            9.34        8.19       5.69        20.07

SV         DF                     Mean square

                   DSB           FRB          DRB          CA

S          3     36.14NS     24662.08 **   2382.10 **   14.85 **
SU         2    1423.13 **   42297.92 **   5340.67 **   151.21 **
SxSU       6     25.13NS     7745.05 **    1228.67 **    9.90 **
Residual   36    12.0400      1995.0694     207.5679     2.6965
CV (%)            21.14         52.51        45.12        4.02

SV         DF       Mean square

                   CB          TC

S          3     45.03NS     73.90 *
SU         2    542.71 **   978.93 **
SxSU       6     11.19NS     33.71NS
Residual   36    23.2399     21.3804
CV (%)            21.36       7.76

PH--Plant height; SD--Stem diameter; LN--Leaf number; FSB--Fresh
shoot biomass; DSB--Dry shoot biomass; FRB--Fresh root biomass;
DRB--Dry root biomass; CA--Chlorophyll a; CB--Chlorophyll b;
TC--Total chlorophyll; **--Significant effect at p < 0.01;
*--Significant effect at p < 0.05; NS--Non-significant effect by
the F test (p > 0.05)

Table 3. Effect of substrates with different humus concentrations
on plant stem diameter (SD), leaf number (LN), fresh shoot
biomass (FSB), dry shoot biomass (DSB), chlorophyll b (CB)
and total chlorophyll (TC)

Variables             Humus (%)

               0      33.33      66.66

SD (cm)      4.84 b    8.30 a     7.90 a
LN           8.67 b    9.77 a    10.66 a
FSB (g)     14.57 c   84.92 b   110.40 a
DSB (g)      4.07 c   18.24 b    26.25 a
CB (FCI)    14.87 c   23.12 b    29.51 a
TC (FCI)    48.48 c   61.84 b    67.61 a

Means followed by the same letter do not differ by the Tukey
test at p < 0.05; FCI--Falker chlorophyll index
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Author:dos Santos, Daiane G.; Diniz, Belisia L.M.T.; Neto, Manoel A. Diniz; Silva, Joao H.C.S.; Filho, Will
Publication:Revista Brasileira de Engenharia Agricola e Ambiental
Date:Aug 1, 2019
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