INTRODUCTION
Having little knowledge on the potential use of native tree species and associated technologies, whether for productive or environmental purposes, has been one of the factors preventing the development of propagation techniques, especially regarding the cloning of superior individuals (i.e. selected plants in the field). This includes not only the propagation process but also the appropriate selection of genetic material with sufficient quality and genetic variability levels to fulfil silvicultural needs (Stuepp et al. 2018).
Among the native species with great potential for afforestation is Cordia trichotoma (Vell.) Arrab. ex Steud., in the family Boraginaceae, which is popularly known in Brazil as ‘louro-pardo’ or ‘freijó’. This species occurs naturally from Ceará to Rio Grande do Sul in the semi-deciduous Atlantic rainforest and the Cerrado, and it is considered important for environmental restoration and noble timber production (Berghetti et al. 2015).
Cordia trichotoma reproduces naturally by seed; however, this form of propagation results in specific restrictions in seedling production due to the high unevenness at the seed germination stage and the fact that sexual propagation confers high genetic variability to new generations, hampering commercial plantations, in which homogeneity is highly important (Tambarussi et al. 2017, Bisognin et al. 2020).
The rescue of selected adult trees in the field may be an alternative for vegetative propagation, in which the selection of trees is based on phenotypic traits of interest towards increasing forest productivity and improving the quality of timber as raw material (Tambarussi et al. 2017, Bisognin et al. 2020, Abiri et al. 2020). Among the various existing techniques, the vegetative rescue method based on epicormic shoots is an alternative for the cloning of adult trees and is considered an excellent tool for vegetative propagation without the need to cut the selected tree (Baccarin et al. 2015, Trueman et al. 2018, Avelar et al. 2020).
Studies that seek to improve large-scale vegetative propagation techniques of native species for use in homogeneous plantations, degraded area recovery, genetic improvement and germplasm conservation have become fundamental from a strategic point of view, considering the increased exploitation of natural resources (Avelar et al. 2020).
Micropropagation technique is considered an in vitro vegetative propagation (e.g. microcutting technique), and compared to other techniques, such as cutting and mini-cutting, it has advantages in terms of tissue rejuvenation and propagule rooting (Hartmann et al. 2011). Micropropagation consists of different stages, and in vitro establishment is the most critical for most woody plants (Souza et al. 2020, Molinari et al. 2020) considering the high losses of materials due to microorganism contamination (e.g. fungal and/or bacterial contamination) or tissue oxidation. These losses justify the need for studies seeking to minimize these obstacles during native species propagation.
Considering the above context, the aims of the work were to evaluate the epicormic shoot emission, and to define a protocol for the in vitro establishment of nodal segments from C. trichotoma selected adult trees.
METHODS
Study site and experimental material
The experiments were conducted at the Forest Nursery and the Laboratory of In Vitro Culture of Forest Species, both located in the Department of Forestry Sciences of the Federal University of Lavras (Universidade Federal de Lavras - UFLA) in the municipality of Lavras, Minas Gerais, Brazil (21° 14’ 43” S and 44° 59’ 59” W).
The experimental material used to conduct the tests was derived from the selection of four C. trichotoma adult trees, which were selected according to their trunk shape (straight), diameter at breast height (21.4 to 23.9 cm) and health (absence of diseases and pest attacks), that originated from a commercial stand belonging to the company “Symbiosis Investimentos e Participações S.A.” in Trancoso, Distrito de Porto Seguro, Bahia, Brazil. The trees were identified as tree A, B, C and D. Branch collection was realized considering two seasons, autumn (06/08/2017) and spring (10/10/2017).
Pruned branches were transported to the city of Lavras, Minas Gerais, and standardized to a length of 45 cm without the presence of shoots (i.e. axillary or apical shoot) and leaves. The branches were placed in a greenhouse with controlled temperature (T < 35 °C) and relative humidity (RH > 80 %), maintained by an intermittent mist system with high-pressure, low flow rate nozzles and automatically controlled by a humidistat and thermostat. The branches were placed vertically in polyethylene pots (5 L) containing washed medium sand according to Baccarin et al. (2015) (figure 1 A - D).
The branches remained in the greenhouse for 50 days during the experimental period. The mean temperature was 16.4 °C in the autumn, and 21.9 °C in the spring. Mean cumulative rainfall levels were 29 mm and 227.4 mm in the autumn and spring, respectively. Climatological data were obtained from the website of the National Institute of Meteorology (Instituto Nacional de Meteorologia - INMET) according to the meteorological station OMM: 83687 located in Lavras, Minas Gerais, Brazil.
Epicormic shoot emission: genotype vs climatic season
The experiment was set up in a completely randomized factorial design (2 × 4), with two climatic seasons (autumn and spring) and four selected trees (trees A, B, C and D). The experiment consisted of eight treatments with 12 replicates, in which each pot was considered an experimental unit. At 20 days after the start of the experiment, the percentage of emitted epicormic shoots and the number of shoots were evaluated.
Epicormic shoot emission: climatic season vs shoot collection time
The experiment was organized in a completely randomized factorial design (2 × 4), which addressed the climatic season (i.e. autumn and spring) and the shoot collection time (20, 30, 40 and 50 days). The experiment consisted of eight treatments with 36 replicates, in which each pot was considered one experimental unit. The percentage of epicormic shoot emission and the number of shoots were evaluated at 20, 30, 40 and 50 days after the start of the experiment.
In vitro establishment
The epicormic shoots of pruned branches from four C. trichotoma individuals were used to obtain explants. Prior to collection (72, 48 and 24 hours), a dimethyl 4.4' - (o-phenylene) bis (3-thioallophanate) fungicide was applied at a concentration of 0.5 g L-1. Shoots measuring 3 to 5 cm in length were collected after 30 days in the greenhouse, stored in plastic bags moistened with autoclaved water and transported to the laboratory.
Prior to in vitro inoculation, the explants (i.e. nodal segments) were standardized to contain two axillary buds and no leaves and washed in running water for 10 minutes. Next, the aseptic procedure was started, during which the explants were washed in a 70 % (v / v) hydroalcoholic solution in a horizontal laminar flow chamber. Subsequently, disinfection was initiated by immersion in a sodium hypochlorite (NaClO) solution for five minutes at three different concentrations; namely C1 = 0.58 % active chlorine, C2 = 1.12 % active chlorine and C3 = 2.12 % active chlorine, followed by triple washing with deionized and autoclaved water.
The explants were inoculated vertically, under aseptic conditions, in 2 × 10 cm test tubes containing 10 mL of MS culture medium (Murashige and Skoog 1962). The tubes were sealed with polyvinyl chloride (PVC) - based plastic film and placed in a growth room at 24 °C (± 1 °C) for a 16 - hour photoperiod and 40 μmol m-2 s-1 irradiance. During the entire process, the equipment was disinfected with 70 % hydroalcoholic solution. The culture medium was supplemented with 30 g L-1 of sucrose and 6 g L-1 of agar and prepared in deionized water, and the pH value of solution was adjusted to 5.8 (± 0.05) with NaOH (0.1 M) and HCl (0.1 M). The culture medium was autoclaved at 127 °C and 1.5 kgf cm-2 pressure for 20 minutes.
Twenty-eight days after the in vitro inoculation of the explants, the percentage of fungal and bacterial contamination, tissue oxidation and establishment were evaluated. The experiment was conducted in a completely randomized design, with three treatments (i.e. active chlorine concentration: C1, C2 and C3), 50 replicates and one explant per replicate.
Data analyses
Data collected during the experiments were analyzed for the homoscedasticity and normality of the residual distribution using the Hartley (P > 0.05) and Shapiro-Wilk (P > 0.05) tests, respectively. When non-parametric, the data were Box-Cox transformed and subjected to an analysis of variance (ANOVA, P < 0.05). The quantitative data were subjected to a polynomial regression analysis (P < 0.05), and the qualitative data were compared using Tukey’s test (P < 0.05). The analyses were performed in R (R Core Team, 2018) using the ExpDes package, version 1.1.2 (Ferreira et al. 2013).
RESULTS
Epicormic shoot emission: genotype vs climatic season
There was effect of the selected plant and climatic seasons on the shoot emission and the number of shoots on the pruned branches. The highest mean shoot emission values in the autumn were observed in tree A (100.0 %) and D (91.7 %). In the spring, the highest means were observed for tree C (66.7 %) and D (83.3 %); in contrast, tree B did not produce shoots during the evaluated seasons (figure 2A). This result demonstrates that the shoot emission is also genotype-dependent and related to the season.
Considering tree A, the highest mean shoot emission occurred in the autumn (100.0 %), and for B, there was no shoot emission (0.0 %). Tree C had the highest mean during the spring (66.7 %), and D showed no effect from the interaction at the different evaluated seasons. The observed means were 91.7 % in autumn, and 83.3 % in spring. The highest mean number of shoots emitted in the autumn were found in tree A (11.3 shoots per branch) and D (8.3 shoots per branch). In the spring, the highest mean was observed in tree D (12.8 shoots per branch) (figure 2B). For the interaction between seasons and selected adult plants, in tree A, the highest mean number of emitted epicormic shoots was observed in the autumn (11.3 shoots per branch). For trees C and D, the highest means were observed in the spring, with mean values of 6.5 and 12.8 shoots per branch, respectively (figure 2B). The epicormic shoots emitted in autumn and spring in trees A, C and D were considered viable at 20 days after the start of the experiment (figures 3A - F).
Epicormic shoot emission: climatic season vs shoot collection time
The percentage of shoot emission (53.3 %) and the number of shoots (9.6 shoots) throughout the evaluation time were highest at 20 days of evaluation (figures 4A - B).
The best time interval for collecting the shoots was 20 days after setting up the experiment in a greenhouse, considering that the highest shoot emission and number of shoots were recorded during this period. There was a reduction in the percent shoot emission and number of shoots over time and no viable shoots, and at the 50-day evaluation, there was no emission of viable shoots for the in vitro introduction.
In vitro establishment
Active chlorine treatments significantly influenced the in vitro establishment of Cordia trichotoma nodal segments at 28 days after inoculation (C1 = 0.58 % active chlorine, C2 = 1.12 % and C3 = 2.12 %) (figure 5A - D).
The highest fungal contamination was 55.1 %, as observed in treatment C1 with 0.58 % active chlorine. In contrast, the lowest mean values were observed in treatments C2 and C3 at active chlorine concentrations of 1.12 % and 2.12 %, respectively, which did not differ significantly (figure 5A). Regarding bacterial contamination, as shown in figure 5B, the lowest means were found in treatments of 1.12 % to 2.12 % active chlorine (C2 and C3); the lowest mean for this variable was observed in treatment C1 (0.58 % active chlorine). The pattern of tissue oxidation for the explants (figure 5C), a direct relationship between active chlorine concentration and percent oxidation is observed. The highest value for this variable was 96.8 %, with a concentration of 2.12 % active chlorine. The highest percentage of in vitro establishment (61.3 %) occurred in the treatment in which 1.12 % active chlorine was used (figure 5D), resulting in the emission of viable shoots to be used for the other micropropagation stages (figures 6A - 6D).
DISCUSSION
Epicormic shoot emission
The results of the present study suggest that epicormic shoots from the pruned branch propagation technique was efficient regarding the shoot emission and number of shoots for C. trichotoma. By definition, epicormic shoots are branches that sprout from dormant buds, which elongated over a previous growth period (Andrew et al. 2012). These shoots can be used for the vegetative propagation of forest species, to rescue the adult individuals selected in the field. This mechanism was important for the study species C. trichotoma, which is considered a species with high commercial potential, given that during the seedling production stage, the use of seeds results in certain restrictions, primarily because sexual propagation confers high genetic variability to new generations (Kielse et al. 2015).
Several similar studies have indicated the efficiency of this vegetative rescue method using epicormic shoots, such as in Ilex paraguariensis (Wendling et al. 2013), Eucalyptus benthamii (Baccarin et al. 2015), E. cloeziana (Oliveira et al. 2015) and E. pilularis (Avelar et al. 2020). According to Kuppusamy et al. (2019) and Esposito-Polesi et al. (2020), the use of this technique is especially important for germplasm conservation and the selection of superior individuals, in which a vegetative rescue is typically performed at the adult stage and propagation may be limited due to the ontogenetic age. Kratz et al. (2016) reported that in situations in which vegetative rescues are performed in plants with high genetic value, the application of this method is indicated, considering the low interference of branch collection from the selected plant and ensuring the highest possible survival of the selected individuals.
However, the physiological principle for bud induction in epicormic shoots is related to changes in the balance of the plant growth regulation (auxin / cytokinin), favoring shoot emergence (Trueman et al. 2018, Abiri et al. 2020). The vegetative propagation of adult trees may be facilitated by epicormic shoot induction to obtain shoots with a higher degree of juvenility, usually with good propagation potential (Oliveira et al. 2015, Souza et al. 2020). These changes may vary with the genotype, resulting in considerable shoot emergence by favoring rejuvenation opposite to the base of the shoot from the shoot collected from the tree branches. In the present study on C. trichotoma, the selected tree directly influenced the emission of epicormic shoots, and it is important to account for the genotype factor of the selected plants, which may influence the success of this technique.
The use of branches to obtain epicormic shoots has also been employed as a source of explants for the micropropagation of E. benthamii (Baccarin et al. 2015), Ilex paraguariensis (Wendling et al. 2013), E. cloeziana (Olveira et al. 2015) and E. pilularis (Avelar et al. 2020). According to Abiri et al. (2020), there are many gaps in our knowledge of epicormic shoots; therefore, developing a larger understanding of the physiological, ontogenetic and environmental factors that support the development of these shoots is still necessary. However, for C. trichotoma, regardless of the climatic season (autumn or spring) in which the pruned branches were collected, it is possible to obtain epicormic shoots, which can be used in propagation techniques such as grafting, cutting and micropropagation. In addition, it is possible to use this method to rescue other native species without the need to fell the selected tree, although the genotype factor must be considered because it can also influence the technique success.
In vitro establishment
The use of branches to obtain epicormic shoots has been employed as a source of explants for the micropropagation of several forest species, such as, E. benthamii (Baccarin et al. 2015), E. cloeziana (Olveira et al. 2015) and E. pilularis (Avelar et al. 2020). For C. trichotoma, this technique has also been shown to be efficient for the preparation and establishment of explants and is recommended as an alternative for the in vitro production of C. trichotoma propagules.
As previously reported, C. trichotoma showed appropriate behavior in terms of in vitro establishment; however, it is necessary to develop adequate measures for the use of chemicals during disinfection, defining the factors, time and ideal concentration for better success in obtaining established explants (Salles et al. 2017, Zorz et al. 2020), especially when the sources of explants originate from adult selected plants, selected in the field due to the high percentage of contamination under these conditions (Postemsky and Curvetto 2016).
The use of active chlorine in micropropagation is an inexpensive and effective method for the disinfection of explants and its use is widespread in several species, such as E. cloeziana (Oliveira et al. 2015), Cochlospermum regium (Gavilan et al. 2018) and E. grandis × E. urophylla (Miranda et al. 2020). In the present study, the lowest percentages of fungal and bacterial contamination occurred with the use of active chlorine at concentrations of 1.12 % and 2.12 %, showing the effectiveness of using this disinfection agent for the successful initial in vitro establishment of C. trichotoma from epicormic shoots.
For micropropagation to be successful, it is necessary for only a few explants to emit shoots free of contamination, because the start of in vitro propagation is the primary limiting stage (Trueman et al. 2018). In addition, the metabolic pathway of microorganisms may be subject to regulation by the genotype through differential genetic expression, in carotenoid biosynthesis and hyphal aggregation (Abiri et al. 2020).
Phenolic oxidation has been a problem that is associated with the micropropagation of woody species. In the present study on C. trichotoma, the oxidation percentage increased directly in relation to the use of sodium hypochlorite; the higher the concentration of the disinfecting agent, the higher the percentage of oxidation, thus indicating that the tissues of this species exhibited high sensitivity to chemical treatment. Similar results have been reported in studies on E. cloeziana (Oliveira et al. 2015), E. benthamii (Baccarin et al. 2015), Corymbia citriodora × C. torelliana and C. torelliana × C. citriodora (Souza et al. 2018), and E. grandis × E. urophylla (Molinari et al. 2020).
The highest in vitro establishment percentage (61.3 %) at 28 days was observed when 1.12 % active chlorine was used, which was considered an adequate value denoting the importance of high rates of shoot induction. Different results are found in literature, in which the response varied according to plant material (genotype) and culture conditions. In E. cloeziana, Oliveira et al. (2015) obtained, on average, 51.2 % of established explants in vitro with the use of sodium hypochlorite. Souza (2020) studied the in vitro establishment of Eucalyptus grandis × E. urophylla and achieved 95.0 % establishment by this method. The results obtained here provide a source of information for future research on C. trichotoma for continuing on to the other micropropagation stages, including bud multiplication, shoot elongation and adventitious rooting.
CONCLUSIONS
The vegetative propagation technique of using epicormic shoots in pruned branches was considered viable for C. trichotoma, regarding the percent emission and number of shoots, regardless of the collection season (autumn or spring); however, the genotype factor should be considered because it may influence the success of this technique. The use of active chlorine at a concentration of 1.12 % for five minutes was effective for in vitro establishment of nodal segments derived from epicormic shoots of C. trichotoma, resulting in 61.3 % establishment at 28 days.