- Research
- Open access
- Published:
Intercropping and environmental seasonality modulate the physiology and growth of Hancornia speciosa (Gomes)
CABI Agriculture and Bioscience volume 5, Article number: 31 (2024)
Abstract
Background
The recovery process of degraded areas with the implantation of orchards of native species is still little known. Thus, we intend to evaluate the physiological performance of Hancornia speciosa during different seasons of the year, cultivated in full sun and in intercropping for recovery of degraded areas.
Methods
Intercropping with Syagrus oleracea (double intercropping); with annual crops (double intercropping); and with S. oleracea and annual crops (triple intercropping) were completed over two years at the beginning of each season. Crops (experimental plots) were planted using a Nelder wheel design.
Results
Over the two years, H. speciosa was observed to experience seasonal regulatory changes, some of which were mitigated by the intercropping. The cultivation arrangement influenced the physiology and consequently the growth of H. speciosa.
Conclusions
It is concluded that the double intercropping benefits the growth of H. speciosa during the formation of the orchard, and the triple intercropping does not affect growth in relation to full sun. It is recommended the implantation of orchards of H. speciosa in recovery areas through intercropping.
Introduction
Global food production has increased substantially due to the systematization of monocultures. The organization of cultivation practices, mechanization, phytosanitary protocols, and genetic breeding were molded for monocultures in the “Green Revolution” (Pingali 2012). However, systems intercropped with trees, known as agroforestry systems, can also contribute to improvements in productivity (LER) combined with significant ecological gains (José 2009), obtained by the increase in biodiversity and their respective positive interspecific interactions.
There are several more sustainable cropping modalities than monocultures, as intercropping, which can provide gains in production efficiency of up to 100% (Land Equivalent Ratio—LER) with the same natural resources used in full sun cultivation (Gao et al. 2009). The gains described with intercropping for the Cerrado landscape of Goiás state, Brazil, have varied according to the season, species, and planting layout used (Custódio et al. 2015; Santos et al. 2017a It is noteworthy that intercropping systems, with different groups of species used, provided results of socio-environmental and economic gains (Alves et al. 2015; Gao et al. 2009; Ronald and Charles 2012).
The physiological responses of intercropped crops are extremely important because they are sensitive to adverse conditions for plant growth and productivity and can therefore provide accurate and rapid information about plant vigor (Peng et al. 2009), with the purpose of filtering the desired ones and formatting promising systems.
Despite the thousands of species in the world, few plant species are currently used in food production (Zappi et al. 2015). Aligned with the need for biodiversification of this food source, Hancornia speciosa is a species with great potential for use in the food sector given its productive capacity and acceptance by the consumer market (Pereira et al. 2006). It is a widely occurring medium-sized tree species and rustic, native to the Brazilian Cerrado (Vieira Neto et al. 2002). Hancornia speciosa is a fruit tree of the family Apocynaceae, a latex producer whose fruit is known as ‘mangaba’, a Tupi-Guarani word meaning “good thing to eat” (Vieira Neto et al. 2002).
The ‘mangaba’ fruit has great production potential that is currently underexploited (Ferreira et al. 2018). It is consumed mainly by specific and regional markets either fresh or in the form of juices and ice creams. Several pharmacological uses for H. speciosa have also been demonstrated (Marinho et al. 2011; Moraes et al. 2008; Silva et al. 2016).
Hancornia speciosa is influenced by environmental conditions such as light, temperature, and water and nutrient availability (Nabout et al. 2016). These environmental factors may directly influence the growth and development of the species and its impact may vary according to the phenological stage of the plant and cropping system (Carvalho et al. 2007).
In this context, the hypothesis that Hancornia speciosa has its physiological behavior and growth positively influenced by the cropping system, attenuating the effects of the seasons of the year, enhancing growth increment is fundamental in the establishment of orchards of this species.
Physiological responses that contribute to the growth and development of H. speciosa and make it competitive and fit for cultivation have long been sought (Caldas et al. 2009), however, there are no works focused on the hypothesis described.
H. speciosa is listed as having either threatened or endangered status. It is an allogamous species that is self-incompatible, with no expression of heterosis or exogamic depression (Collevatti et al. 2016). The maximum sustainable rate of fruit harvest by extractivism for maintaining the native population is 87%. It is noteworthy that the stability of the in situ population is highly dependent on larger adult plants (Lima et al. 2013).
Both extractivism and cultivation of H. speciosa are indicated as strategies with the potential for conservation and improvement of the biodiversity and life quality of the communities involved (Bisseleua and Vidal 2008; Caldas et al. 2009; Lima et al. 2013).
Thus, the objective of this study was to characterize the physiological and growth responses of H. speciosa Gomes during different seasons of the year when grown in full sun and by intercropping. The experiment aimed to evaluate innovative ways for establishing orchards of H. speciosa.
Materials and methods
Study site
The experimental site was located in the Cerrado domain (Brazilian savanna) (Batalha 2011), whose climatic conditions are classified as Aw with rainy summer and dry winter (Alvares et al. 2013). The experiment was conducted at the Teaching Farming of Goiano Federal Institute, Iporá Campus (51°09′12″ W and 16°25′38″ S), at 588 m altitude. The climatic conditions recorded during the test are shown in Fig. 1.
Soil characteristics
The experiment was conducted in a degraded area, whose soil was classified as Cambisol (Embrapa 2013). The upper soil layer (0.6 m) of the experimental site was removed for use in landscaping, therefore, the experiment was implemented on a subsoil layer, intended for restoration. The physicochemical characteristics of the soil profile at the site before the intervention at the 0.00–0.20 m, 0.21–0.40 m, and 0.61–0.80 m used for implantation of the experiment (Tables 1 and 2).
Site preparation and planting
The soil was prepared between June 1st and 6th, 2016 with two harrowing operations (28" disks). The first occurred before lime (1.8 Mg ha−1) and gypsum (200 kg·ha−1) application and the second afterwards, according to the soil correction adapted from Ribeiro et al. (1999).
Seeds of H. speciosa were sown in 120 mL tubes in November 2014. The seedlings were later transplanted in February 2015 to 15 × 15 × 35 cm (3.78 L) citrus pots filled with Latosol (Embrapa 2013). Seedlings of S. oleracea were sown and produced in 3.00 L plastic bags filled with Latosol (Embrapa 2013).
Twenty months after sowing of H. speciosa and 8 months after sowing of S. oleracea, the seedlings were transplanted to the field.The transplanting beds (pits) measuring 0.15 × 0.15 × 0.25 m and 0.40 × 0.40 × 0.40 m were dug, and 100 and 500 g of thermophosphate (16% of P2O5; 12% of P2O5 soluble in citric acid 2%; 16% Ca; 6.5% Mg; 6%S; 0.1%B; 0.05% Cu; 0.3% Mn; 9% Si; 0.55% Zn) was applied to each pit for S. oleracea and H. speciosa, respectively. After transplanting, localized supplementary drip irrigation was employed from July until the beginning of the rainy season in 2016, being equally applied for all the evaluated systems.
Pre-seeding fertilization and topdressing were performed for corn and squash at all cropping. For pre-seeding fertilization, 400 kg ha−1 of NPK fertilizer (4-30-10) was uniformly applied to the rows (corn) and holes (squash). For topdressing, 200 kg ha−1 of agricultural urea (45% N) was applied at each crop cycle, divided into two applications (Ribeiro et al. 1999).
Experimental design
The distribution of plots and treatments was adapted from the method proposed by Nelder (1962) because each plant would have its effects blocked, allowing the size of the experimental plots to be reduced to one plant. In this layout, the blocks were placed along the lines formed by the radius in the circumferences, excluding only the inner and outer circumferences (borders) (Fig. 2). Four densities were: 403, 469, 603 e 803 plants ha−1 de H. speciosa, used to block the plots in the direction of the radius.
The experimental design was a complete randomized block design (RBD) with four treatments (H. speciosa cropping systems) and 20 replicates. The 20 repetitions were obtained by blocking observations in the five radius and in the four arrangement densities of the four treatments.
One evaluation was performed per season over two consecutive years. A total of 8 ages were evaluated, i.e., the 21st, 24th, 27th, 30th, 33rd, 36th, 39th, and 42nd months after transplanting, performed at the beginning of the seasons (March—Fall, June—Winter, September—Spring, and December—Summer). Therefore, 160 measurements were obtained per treatment for each variable evaluated.
Experimental treatments
The treatments consisted of four systems of H. speciosa (‘Mangaba’) orchard establishment. The systems were as follows: 1. Hancornia speciosa monoculture grown in full sun (H.s); 2. Hancornia speciosa intercropped with Syagrus oleracea (‘Gueroba’) cultivated between the plants’ rows (H.s + S.o); 3. Hancornia speciosa intercropped with annual crops (corn and pumpkin, in succession to each harvest sown between rows) (H.s + Crop); 4. Hancornia speciosa intercropped with annual crops (corn and pumpkin, in succession to each harvest sown between rows) and S. oleracea (‘Gueroba’) grown between the plants in the row (H.s + S.o + Crop).
The intercropping systems of H. speciosa with annual crops was cultivated by squash (Cucurbita moschata) cultivation in all years between September and December evaluations, and corn (Zea mays) crop from January to April. Corn was sown in three rows spaced 0.60 m apart, centered in the inter rows of H. speciosa. Squash was sown in four holes, located 0.75 m from the H. speciosa plants. After emergence, thinning was performed, keeping one C. moschata plant per hole, therefore four plants per plot. In the intercropping systems of H. speciosa with S. oleracea, the two species were simultaneously transplanted to the field at the start of the experiment. S. oleracea was arranged in the line (circumference) obeying the spacing of 0.90 m between the plants of S. oleracea and also of H. speciosa (Fig. 3).
Cultivation practices
The H. speciosa plants did not receive any topdressing. The intercropping systems that included annual crops were cultivated during the dry and rainy seasons with squash (C. moschata) and corn (Z. mays), respectively. During the dry seasons, squash (C. moschata) was cultivated with the aid of local irrigation (drip irrigation). Corn (Z. mays) was grown in the rainy seasons, with open pollinated varieties, without irrigation, under a rainfed regime. The pre-planting fertilizers were mixed with the soil removed to open the pits for S. oleracea transplanting. Topdressing was applied 0.15 m from the plant stem.
During 90 days of drought in 2016, 2017, 2018 and 2019, all H. speciosa plants were equally irrigated, regardless of cropping system. Irrigation in the years of evaluation was carried out between the evaluations of June and September of 2018 and 2019. Period corresponding to the cultivation of pumpkin in the corn inter-harvest, with irrigation depths according to Klosowski et al. (1999).
Evaluations
Biometrics of H. speciosa plants
For Hancornia speciosa growth was evaluated at 21, 24, 27, 30, 33, 36, 39, and 42 months after transplanting, at the same time as the other evaluations. The stem diameter (mm) was determined at 3 cm from the ground using a caliper, and the height (m) was measured using a centimeter ruler.
Photosynthetically active radiation (PAR)
Photosynthetically active radiation (PAR) was determined using a bar with six PAR sensors model APG-SQ-316 (Apogee, North Logan, UT, USA). The radiation characterization evaluations were performed above and below the H. speciosa canopy at 8 am, 12 pm, and 4 pm.
This bar was leveled and positioned 2 cm from the main trunk of H. speciosa plants, facing the center of the Nelder wheel, and suspended 10 cm from the ground for the below-canopy readings. For the above-canopy readings, the bar was leveled and positioned 2 cm from the main trunk of H. speciosa plants, facing the center of the Nelder wheel, and suspended 10 cm from the top of the plants.
Gas exchange in H. speciosa leaves
The net carbon assimilation rate (A) (μmol CO2 m−2 s−1), transpiration rate (E) (mmol H2O m−2 s−1) and stomatal conductance (gsw) (mol m−2 s−1) of H. speciosa were measured. These measurements were performed with an infrared gas analyzer (Li-Cor—Li6800 XT, Lincoln, NE, USA). A total of 1000 μmol m−2 s−1 of irradiance was standardized and used at a temperature of 25 °C and CO2 pressure of 40 Pa during all evaluations. All measurements were taken from 8:00 to 11:30 am in the third pair of fully expanded leaves located in one of the apex branches.
The water use efficiency (WUE) of H. speciosa was calculated by the A/E ratio (μmol of CO2/mmol of H2O). The instantaneous carboxylation efficiency was calculated by the A/Ci ratio (μmol m−2 s−1/μmol mol−1) and the Ci/Ca index (μmol mol−1/μmol mol−1) was also calculated.
Fluorescence of chlorophyll a in H. speciosa leaves
The test OJIP chlorophyll a fluorescence transient was determined with a FluorPen FP 100 portable fluorometer (Photon Systems Instruments; Drasov, Czech Republic). It was evaluated in the third or fourth fully expanded leaf from the apex that was nondetached and had been adapted to the dark for 30 min for complete oxidation of the photosynthetic electron transport system.
The leaves were exposed to a light-saturating pulse (3000 μmol m−2 s−1) with a wavelength of 450 nm for one second after adaptation to obtain the responses related to the chlorophyll a fluorescence transient, according to the JIP test equations.
Analysis of pigments in H. speciosa leaves
Total chlorophyll, flavonoids, anthocyanins, and the nitrogen balance index (NBI) were determined. NBI was calculated as the chlorophyll/flavonoid ratio (Chl/Flav) in the adaxial epidermis of the leaves. A Dualex DX-4 Plus (Force-A, Orsay, France) instantaneous and nondestructive chlorophyll and polyphenol meter was used to record the excitation spectra of chlorophyll fluorescence (Cerovic et al. 2012). For all physiological evaluations, the readings were performed between 8:00 and 11:00 am on the third or fourth fully expanded leaf.
Statistical analysis
All data were evaluated for the presence of outliers using the outlierTest function of the car package (Fox and Weisberg 2019) of the R software v.3.4.0 (R CORE TEAM 2020). The identified outliers were removed, and the test was applied again until no outlier was identified. The identified outliers were probably related to extreme results obtained from the measurement equipment, therefore is not related to the experiment sources of variation, then we decide to remove to not compromise the statistical analyses. The normal distribution of the residuals was evaluated using the shapiro.test function of R v. 3.4.0. The homogeneity of variances between treatments was determined by the Bartlett test using the bartlett.test function in R v. 3.4.0.
All variables were evaluated by mixed models considering the fixed effects of year, season, and system, as well as the interaction between them. Density of plants, as they present known characteristics equally, formed blocks by density and the blocks were considered fixed effects in the model. Each plant (individual) was considered a random effect. Mixed model analyses were performed with lmer function of the lme4 package (Bates et al. 2015), testing one variable at a time. The p value (P < 0.05) for the fixed effects was determined by analysis of variance on the mixed model using the sum-of-squares type III method with the function Anova (type = 'III') from car package in R.
The least squares mean were obtained with the emmeans function of the emmeans package (Russell and Lenth 2020) and, when one of the fixed effects was significant (P < 0.05), the means were compared by Tukey’s test adjustment (P < 0.05). The graphs of the means and the difference between them were plotted using the plot function with the comparisons = TRUE command within the ggplot2 (Wickham 2016) and emmeans (Russell and Lenth 2020) packages in R.
We performed Principal Component Analyses (PCA) to identify the relationship between the evaluated variables and how these variables were related to the production systems and seasons evaluated. Principal component analysis (PCA) allowed to summarize the information in our data set, which contained multiple inter-correlated quantitative variables. Multivariate principal component analysis (PCA) was performed using the PCA function of the FactoMineR package (Le et al. 2008). The graphs of the different PCA dimensions were plotted using the fviz_pca_ind and fviz_pca_biplot functions of factoextra package (Kassambara and Mundt 2020). The PCA analyses were conducted in groups of variables according to their biological function: Gas Exchange and Biometrics, Pigments and Biometrics, Fluorescence and Biometrics, and Photosynthetically Active Radiation and Biometrics. PCA results were used to perform a hierarchical clustering on the factor map using the HCPC function in software R. Table frequencies between the clustering in four groups and cultivation system and season of the year were constructed to evaluated the relation between clusters and each factor.
Results
The significance levels of the variables evaluated in the experiment for system, season, the system × season interaction, and overall mean obtained throughout the observations (n ≤ 620) are shown in Table 3. Tree density did not affect (P < 0.05) any of the variables evaluated, which is probably related to the slow growth of this native species up to 42 months.
The results demonstrate predominantly seasonal effects. Although there are effects of systems and interactions (systems × seasons) on physiological and environmental attributes. Pigments and flavonoids seems to be the variables mainly affected by seasons. Means, standard error and significative difference of the means for production systems * season interaction are shown in Additional file 1: Figs. S1–S4.
Percentiles of the variables studied over the 2 years for each treatment, according to the evaluated system, are described in box plots (a visual analysis of the position, dispersion, symmetry, tails, and outliers of the data set). The results bring to light the phytotechnical performance index of H. speciosa not described in the scientific literature (Additional file 1: Figs. S5–S10).
Double intercropping (H. speciosa + Annual Crops—H.s + Crop) and (H. speciosa + S. oleracea—H.s + So) varying above, sometimes below full sun treatment (H. speciosa—H.s) and triple intercropping (H. speciosa + S. oleracea + Annual Crops—H.s + S.o + Crop) in terms of gas exchange (A, Ci/Ca, and gsw) (Fig. 4).
The highest net carbon assimilation rate (A) occurred in the H.s + S.o intercropping system compared to full sun system both in the winter and in fall. Great values were observed regardless of the cropping system in the spring (mean of 11.48 μmol CO2 m−2 s−1) which again declined in the summer (8.12 μmol CO2 m−2 s−1) (Fig. 4).
Greater water use efficiency (WUE) (P < 0.10) occurred in the H.s + Crop intercropping system in relation to H.s + S.o + Crop in summer (Fig. 4). It is also noteworthy that the H.s + S.o intercropping system presents greater stability throughout the seasons regarding the instantaneous carboxylation efficiency (A/Ci). Therefore, there were no significant changes for this variable in this intercropping system during the fall, winter or spring (Fig. 4).
The transpiration rate (E) and the instantaneous carboxylation efficiency change according to the season and do not change according to the cropping system (Fig. 4), as also observed by the multivariate analyses (Fig. 7). The results show no effects of the intercropping systems.
The various parameters related to chlorophyll a fluorescence quantum efficiency, quantum yield, and electron transport of PSII were not affected by the H. speciosa cropping system (Additional file 1: Figs. S1–S3). Although, season did exert significant effects on these parameters (Additional file 1: Figs. S1–S3).
In the spring, there was a reduction in flavonoids (Flav) and an increase in nitrogen balance (NBI) in the H.s + Crop intercropping system differing from H.s + S.o in NBI and from H.s + S.o + Crop in flavonoids (Fig. 5). It is also noteworthy that the H.s + Crop intercropping system is the only system in which the NBI did not differ between seasons, suggesting greater stability in the face of the environmental variations imposed throughout the year. The other systems did fluctuate according to the season.
Different seasons had different effects on each evaluated variable, for example the reduction in chlorophyll a in the spring, the increase in flavonoids in fall, the reduction in anthocyanins in fall, and the reduction in nitrogen balance in the spring (Fig. 5).
The cropping system showed effects on stem diameter and height starting on 36th and 39th months after transplanting H. speciosa plants, respectively (Fig. 6). It is worth noting the need for long periods of evaluation to detect effects on Cerrado trees.
The fitted linear regression models for the different systems confirmed the H.s + Crop and H.s + S.o (double intercropping systems) as suitable for the height growth of H. speciosa. In full sun (H.s) and triple intercropping (H.s + S.o + Crop) performed similarly throughout the evaluated period. It is worth noting that triple intercropping did not affect H. speciosa growth when compared to the reference (Full sun).
The angular coefficients of the models show that triple intercropping (H.s + S.o + Crop) tended to increase the height at the expense of a smaller stem diameter. In the case of in full sun (H.s), there was an inverse behavior.
These results were reinforced by the photosynthetically active radiation (PAR) (Additional file 1: Fig. S4), which reached from the top to the bottom of H. speciosa plants. The effects obtained corroborate expected trends. The PAR values were higher in the Hs system and lower in the H.s + S.o + Crop system. In full sun and triple intercropping are exposed to higher and lower light incidence, respectively (Additional file 1: Fig. S4).
Although different physiological responses occurred throughout the seasons, thanks largely to the meteorological conditions imposed on the plants during growth, the double intercropping systems mitigated the effects of seasons, leading to greater stability. On the other hand, the triple intercropping promotes higher competition between plants and species opposing with benefits of intercropping.
The PCA performed with Gas exchange + Biometrics (Fig. 7), Pigments + Biometrics (Fig. 8), Fluorescence + Biometrics (Fig. 9) and Photosynthetic active radiation + Biometrics (Fig. 10) data were robust and clearly identified which variables were positively or negatively correlated with the evaluated seasons and systems.
The PCA with physiological and environmental parameters showed some separation of the seasons and no separation between the systems (Figs. 7, 8, 9, 10). The PCA with photosynthetically active radiation showed a clear separation of winter in one of the clusters and no separation for systems. PCA clusters for gas exchange did not show any clear separation between systems and seasons. Clusters with PCA of fluorescence variables showed that none Spring observations in cluster 4 and the other seasons were equally represented, what showed some different behavior of spring in relation to other seasons. Same behavior was seen for summer observations of the clustering with pigments variables, showing a different pattern in pigments measured at summer in relation to other seasons. According to the PCA, the lowest net carbon assimilation rates corresponded to full sun (Hs) and the highest to double intercropping (H.s + S.o). WUE was highest for H.s + Crop and lowest for triple intercropping (H.s + S.o + Crop).
Spring is the season in which PAR was most different from the other seasons, followed by winter. The summer and fall have similar PAR and had intermediate effects compared to the other seasons according to the univariate analyses. Spring had higher anthocyanin and lower Flavonoids content than Fall and Summer seems to be related to higher NBI and Chlorophyll a than Spring (Fig. 9).
Results of fluorescence variables did not differ between systems, but were able to significantly separate Spring from Fall (Fig. 9). Spring mainly had higher TRoRC, Fo and ABSRC compared to Fall and Winter. Figure 10 shows clear separation of Winter in relation to other seasons. BASE12, BASE 16, TOP 16 and TOP 12 were lower in Winter and higher in the other seasons.
Discussion
In intercropping systems, all components of the system must be as complementary as possible to ensure favorable environmental conditions for the expression of productive potential (Barbosa et al. 2019). However, the slow growth of the species investigated explains the absence of the population density effect. According to Lima et al. (2013) and Pereira et al. (2006), effects are expected only in the productive phase, when H. speciosa is fully developed.
The results show that double intercropping (annual crops or S. oleracea) provided cumulative increases in growth. In the triple intercropping system, there was no reduction in growth rate when compared to full sun. These findings show that designs that consider species, densities, and adequate times for establishment of intercropping systems provide more efficient, promoted by positive interaction between species (Custódio et al. 2015; Gao et al. 2013; Santos et al. 2017a; Schwartz et al. 2015).
The triple intercropping has a spatial/temporal arrangement with plants arranged in line and between lines, surrounding the plants of H. speciosa on all sides (Fig. 3). In double intercropping, the arrangement is only on the line or between the lines, depending on the system tested. Competition for space, light, water and nutrients in the triple intercropping is naturally higher (Custódio et al. 2015; Gao et al. 2013; Santos et al. 2017a, b). The results presented demonstrate a tendency of etiolation in the triple intercropping, with inversely proportional height and diameter (Additional file 1: Figs. S9 and S10).
In the triple intercropping (H.s + S.o + Crop) the height of H.s was more favored than the stem diameter. In this aspect, it shows poor performance, since photosynthesis apparently has a more direct relationship with the growth in diameter than with the height of the plant (Lima et al. 2008). Now, in full sun (H.s) there was an investment opposite characteristics, with reduction of vegetative structures (Righi et al. 2016).
It should be noted that intense shading, as well as exposure to full sun, can cause stress due to lack or excess of light on plant leaves and consequently high leaf temperature (Taiz and Zeiger 2009). However, partial shading can contribute to the improvement of these microclimatic parameters. Plants have ideal ranges of leaf temperature and light intensity, which allow an increase in the CO2 assimilation rate resulting from effects on carboxylation efficiency and stomatal conduction (Machado et al. 2005).
These results are directly related to the improvement and/or maintenance that the intercropping systems provided to the physiological vigor of H. speciosa plants throughout the seasons. In general, intercropped crops, especially double intercropping systems, provided higher photosynthetic rates and instantaneous carboxylation efficiency (A/Ci), as shown in the PCA (Fig. 7A). Integrated systems promote a more favorable microclimate for crop development. Agroforestry systems act by changing the luminosity of the environment, decreasing the air temperature, especially under high temperature conditions. Additionally, humidity can be increased (Guo et al. 2017; Yang et al 2021). This reduces the vapor pressure deficit (VPD), favoring stomatal opening and increasing gsw, optimizing carbon fixation, but without increasing the loss of water vapor in the leaves (Santos et al. 2017b). Since, adequate temperatures result in gains in the indecencies of gas exchange (Machado et al. 2005).
These responses were more evident in fall and winter, which are characterized by milder temperatures and low rainfall. Notably, these events were more pronounced in the winter, where there was an effective reduction in the photosynthetic rate in all cropping systems. However, over time the small physiological gains were linearly reflected in the accumulation of benefits from intercropping systems suitable for the establishment of H. speciosa orchards (Fig. 6).
The maintenance of the photosynthetic rate of these plants may be linked to the water relationships of the system. The plants grown in intercropping showed an overall increase in stomatal conductance. Especially in the fall when comparing H.s versus H.s + S.o and H.s + S.o + Crop. Therefore, they had a higher capacity to conduct higher carbon concentrations to the mesophyll, as indicated by Ci/Ca. This process improves the instantaneous carboxylation efficiency of ribulose-1,5-bisphosphate carboxylase/oxygenase (Rubisco), since it concentrates more carbon near its carboxylic sites, increasing the probability of carboxylation occurring in relation to the oxygenation reactions that would lead the system to photorespiratory metabolism (Avila et al. 2019). The lower PAR values found in triple intercropping associated with interspecies competition may have suppressed more expressive photosynthetic rates, as well as efficient water use (WUE) of H. speciosa plants.
The reduction in gas exchange rates observed between seasons was closely linked to the phenological stage and to stomatal limitations than photochemical limitation. In the spring, for example, there were reductions in the indicators of good functioning of the photochemical apparatus as evaluated based on the chlorophyll a fluorescence parameters, such as the potential quantum yield (Fv/Fm) and the photosynthetic performance index (PIABS) (Gonçalves et al. 2010). In addition, there was an increase in Fo and energy dissipation in the form of heat, i.e., nonphotochemical quenching (PhiDO and DIo/RC). However, the photosynthetic rate (A) and instantaneous carboxylation efficiency of Rubisco (A/Ci) had the highest mean values in spring comparing to other seasons.
Despite the correlation between PSII efficiency and net CO2 assimilation rate (Baker and Rosenqvist 2004), this study found that there may have been a discrepancy between the recovery of photochemical machinery damage still occurring in winter and improvement in the efficiency of gas exchange due to the reestablishment of the rainfall regime in mid-spring.
In contrast, in the summer, the resumption of PIABS and of chlorophyll concentration was observed, while there was a decline in gas exchange, which may be attributed to greater leaf expansion and high temperatures inherent to this season. A larger leaf area may have reduced chloroplast density in summer, and high temperatures suppress stomatal conductance, reducing the internal CO2 concentration and the transpiration rate, in contrast with high values of water use efficiency.
Furthermore, there is not always a positive correlation between photosynthetic rate measured by area and leaf area, and in some cases even negative, so it is important to consider characteristics such as specific leaf area and leaf age (Bhagsari and Brown 1986; Weraduwage et al. 2015). Thus, the supply of photochemical products was sufficient to sustain the Calvin cycle, and the production of trioses that provided energy and carbon skeletons during plant growth was maintained (Guidi et al. 2019). Additionally, the possible explanation is that photochemical damage did not limit carboxylation.
In contrast, plants that are under any type of stress tend to reduce the transfer of photochemical energy and increase the rate of energy loss in the form of heat and fluorescence (Guidi et al. 2019).
Therefore, our findings suggest that the senescence process initiated in the winter culminated in a reduction in the chlorophyll content in the spring, triggering a sequence of negative events on the photochemical stage. This result corroborates to the mechanisms described by Sakaigaichi et al. (2019), as they discovered that the chlorophyll content and the Fv/Fm ratio are common to decrease in winters in sugarcane crops.
It is important to highlight the literature lack of parameters related to chlorophyll a fluorescence in H. speciosa. Nevertheless, this native species, presented values known as “adequated” differing from the values found in crop species. For example, Fv/Fm values lower than 0.7 in sugarcane means photoinibition (Sakaigaichi et al. 2019), however, in the present study we verified that Fv/Fm values up to 0.65 did not compromise the photosynthesis of H. speciosa. Further studies about chlorophyll a fluorescence in H. speciosa are essentials to improve knowledge about the physiology of this specie and expand their use.
The possibility of classifying and/or describing a tree species through physiological attributes is already known (Bussotti and Pollastrini 2015; Pollastrini et al. 2016) and reinforced mainly when associated with multivariate analysis techniques (Ganopoulos et al. 2015; Pollastrini et al. 2016), with the possibility of combined and automated use (Virlet et al. 2017) being a trend in production systems. Therefore, finding new production systems depends on the grouping of results, as it allows us to identify and group the different physiological patterns of H. speciosa under favorable and unfavorable conditions.
The gains in growth rate of H. speciosa obtained with the intercropping cultivation systems highlights the potential contribution of intercropping systems to food security and, at same time, to genetic resources and biodiversity conservation (Bhagwat et al. 2008; Bisseleua and Vidal 2008). It is noteworthy that the species used here are alternative to the portfolio of the main food species used in the world.
Further studies with this species is fundamental to determine the influence of the use of fertilizers between the rows of trees, as fertilizers were used for the nutrition of annual crops in the intercropping systems with annual crops (H.s + Crop and H.s + S.o + Crop). Indeed, long-term differentiation is expected, especially at the beginning of the reproductive phase with fruit production. This is because the intercropping system with S.o received fertilizers only in the palms located between H. speciosa plants.
Conclusions
Overall performance of H. speciosa was favored by double intercropping; therefore, the best way to implement H. speciosa orchards is intercropped with annual crops or with S. oleracea. The physiological changes were subtle but detectable through the growth rate at 42 months after field establishment, demonstrating the need for long-term studies of this species.
Triple intercropping (H.s + Crop + So) did not negatively impair growth when compared to H. speciosa in full sun. Further studies should seek systems that decrease the effects of full sun, without promoting severe shading in the establishment of H. speciosa. It is noteworthy that the seasons of the year had a strong influence on the physiological and environmental parameters of H. speciosa.
Availability of data and materials
Additional file 1 follows in the metadata.
References
Alvares CA, Stape JL, Sentelhas PC, Gonçalves JLM, Sparovek G. Köppen’s climate classification map for Brazil. Meteorol Z. 2013;22(6):711–28. https://doi.org/10.1127/0941-2948/2013/0507.
Alves EP, Silva MLD, Neto SNDO, Barrella TP, Santos RHS. Economic analisys of a coffee-banana system of a family-based agriculture at the Atlantic Forest Zone, Braxil. Ciênc Agrotecnol. 2015;39:232–9. https://doi.org/10.1590/s1413-70542015000300004.
Avila RG, Magalhães PC, Da Silva EM, Gomes Júnior CC, De Paula Lana UG, De Alvarenga AA, De Souza TC. Silicon supplementation improves tolerance to water deficiency in Sorghum plants by increasing root system growth and improving photosynthesis. SILICON. 2019. https://doi.org/10.1007/s12633-019-00349-5.
Baker NR, Rosenqvist E. Applications of chlorophyll fluorescence can improve crop production strategies: an examination of future possibilities. J Exp Bot. 2004;55:1607–21. https://doi.org/10.1093/jxb/erh196.
Barbosa RA, Reis GGD, Reis MDGF, Leite HG, Oliveira CHRD, Silva MLD, Cacau FV, Caliman JP. Growth, yield and economic analysis of an eucalypt-soybean consortium: effect of the distance between trees within the row. Rev Árvore. 2019;43:e430202. https://doi.org/10.1590/1806-90882019000200002.
Batalha MA. O cerrado não é um bioma. Biota Neotrop. 2011;11:21–4. https://doi.org/10.1590/s1676-06032011000100001.
Bates D, Maechler M, Bolker B, Walker S. Fitting linear mixed-effects models using lme4. J Stat Softw. 2015;67(1):1–48. https://doi.org/10.18637/jss.v067.i01.
Bhagsari AS, Brown RH. Leaf photosynthesis and its correlation with leaf area. Crop Sci. 1986;26:127–32.
Bhagwat SA, Willis KJ, Birks HJB, Whittaker RJ. Agroforestry: a refuge for tropical biodiversity? Trends Ecol Evol. 2008;23:261–7. https://doi.org/10.1016/j.tree.2008.01.005.
Bisseleua DHB, Vidal S. Plant biodiversity and vegetation structure in traditional cocoa forest gardens in southern Cameroon under different management. Biodivers Conserv. 2008;17:1821–35. https://doi.org/10.1007/s10531-007-9276-1.
Bussotti F, Pollastrini M. Evaluation of leaf features in forest trees: methods, techniques, obtainable information and limits. Ecol Indic. 2015;52:219–30. https://doi.org/10.1016/j.ecolind.2014.12.010.
Caldas LS, De Lima Machado L, Caldas SC, Campos ML, Caldas JA, Pharis RP, Pereira-Netto AB. Growth-active gibberellins overcome the very slow shoot growth of Hancornia speciosa, an important fruit tree from the Brazilian “Cerrado.” Trees. 2009;23:1229–35. https://doi.org/10.1007/s00468-009-0361-9.
Carvalho APF, Bustamante MMC, Kozovits AR, Asner GP. Variações sazonais nas concentrações de pigmentos e nutrientes em folhas de espécies de cerrado com diferentes estratégias fenológicas. Rev Bras Bot. 2007;30:19–27. https://doi.org/10.1590/s0100-84042007000100003.
Cerovic ZG, Masdoumier G, Ghozlen NB, Latouche G. A new optical leaf-clip meter for simultaneous non-destructive assessment of leaf chlorophyll and epidermal flavonoids. Physiol Plant. 2012;146:251–60. https://doi.org/10.1111/j.1399-3054.2012.01639.x.
Collevatti RG, Olivatti AM, Telles MPC, Chaves LJ. Gene flow among Hancornia speciosa (Apocynaceae) varieties and hybrid fitness. Tree Genet Genomes. 2016;12:74. https://doi.org/10.1007/s11295-016-1031-x.
Custódio AM, Alves EM, Paim TP, Carneiro HA, Lima Junior AF. Desempenho agronômico de consórcios entre rabanete e alface no Oeste goiano. Rev Verde Agroecol Desenvolv Sustent. 2015;10:56–60. https://doi.org/10.18378/rvads.v10i5.3828.
EMBRAPA. Sistema Brasileiro de Classificação do Solo, 3rd ed. EMBRAPA, Brasília. 2013. p 353
Ferreira EG, Menino IB, De Sousa MF, Régis TKO, Vasconcelos GC. Caracterização biométrica de plantas e físico-química de frutos de mangabeiras do litoral da paraíba. Rev Campo Saber. 2018;4:36–57.
Fox J, Weisberg S. An {R} companion to applied regression, 3rd ed. Thousand Oaks CA: Sage. 2019. https://socialsciences.mcmaster.ca/jfox/Books/Companion/
Ganopoulos I, Moysiadis T, Xanthopoulou A, Ganopoulou M, Avramidou E, Aravanopoulos FA, Tani E, Madesis P, Tsaftaris A, Kazantzis K. Diversity of morpho-physiological traits in worldwide sweet cherry cultivars of GeneBank collection using multivariate analysis. Sci Hortic. 2015;197:381–91. https://doi.org/10.1016/j.scienta.2015.09.061.
Gao Y, Duan A, Sun J, Li F, Liu Z, Liu H, Liu Z. Crop coefficient and water-use efficiency of winter wheat/spring maize strip intercropping. Field Crops Res. 2009;111:65–73. https://doi.org/10.1016/j.fcr.2008.10.007.
Gao L, Xu H, Bi H, Xi W, Bao B, Wang X, Bi C, Chang Y. Intercropping competition between apple trees and crops in agroforestry systems on the Loess Plateau of China. PLoS ONE. 2013;8:e70739. https://doi.org/10.1371/journal.pone.0070739.
Gonçalves JFDC, Silva CE, Guimarães DG, Bernardes RS. Análise dos transientes da fluorescência da clorofila a de plantas jovens de Carapa guianensis e de Dipteryx odorata submetidas a dois ambientes de luz. Acta Amaz. 2010;40:89–98. https://doi.org/10.1590/s0044-59672010000100012.
Guidi L, Lo Piccolo E, Landi M. Chlorophyll fluorescence, photoinhibition and abiotic stress: does it make any difference the fact to be a C3 or C4 species? Front Plant Sci. 2019;10:174. https://doi.org/10.3389/fpls.2019.00174.
Guo F, van Ittersum MK, Simon E, Leffelaar PA, van der Putten PEL, Zhang LZ, van der Werf W. Intercropping wheat and maize increases total radiation interception and wheat RUE but lowers maize RUE. Eur J Agron. 2017;84:125–39. https://doi.org/10.1016/j.eja.2016.10.014.
Jose S. Agroforestry for ecosystem services and environmental benefits: an overview. Agrofor Syst. 2009;76:1–10. https://doi.org/10.1007/s10457-009-9229-7.
Kassambara A, Mundt F. Factoextra: extract and visualize the results of multivariate data analyses. R package version 1.0.7. 2020. https://CRAN.R-project.org/package=factoextra
Klosowski ES, Lunardi DMC, Sandanielo A. Determinação do consumo de água e do coeficiente de cultura da abóbora na região de Botucatu. SP Rev Bras Eng Agríc Ambient. 1999;3:409–12. https://doi.org/10.1590/1807-1929/agriambi.v3n3p409-412.
Le S, Josse J, Husson F. FactoMineR: an R package for multivariate analysis. J Stat Softw. 2008;25(1):1–18. https://doi.org/10.18637/jss.v025.i01.
Lenth RV. emmeans: estimated marginal means, aka least-squares means. R package version 1.5.3. 2020. https://CRAN.R-project.org/package=emmeans.
Lima JD, Silva BMS, Moraes WS, Dantas VAV, Almeida CC. Efeitos da luminosidade no crescimento de mudas de Caesalpinia ferrea Mart. ex Tul. (Leguminosae, Caesalpinoideae). Acta Amazon. 2008;38:5–10.
Lima ILP, Scariot A, Giroldo AB. Sustainable harvest of mangaba (Hancornia speciosa) fruits in Northern Minas Gerais, Brazil. Econ Bot. 2013;67:234–43. https://doi.org/10.1007/s12231-013-9244-5.
Machado EC, Schmidt PT, Medina CL, Ribeiro RV. Respostas da fotossíntese de três espécies de citros a fatores ambientais. Pesq Agrop Brasileira. 2005. https://doi.org/10.1590/S0100-204X2005001200002.
Marinho DG, Alviano DS, Matheus ME, Alviano CS, Fernandes PD. The latex obtained from Hancornia speciosa Gomes possesses anti-inflammatory activity. J Ethnopharmacol. 2011;135:530–7. https://doi.org/10.1016/j.jep.2011.03.059.
Moraes TDM, Rodrigues CM, Kushima H, Bauab TM, Villegas W, Pellizzon CH, Brito ARMS, Hiruma-Lima CA. Hancornia speciosa: indications of gastroprotective, healing and anti-Helicobacter pylori actions. J Ethnopharmacol. 2008;120:161–8. https://doi.org/10.1016/j.jep.2008.08.001.
Nabout JC, Magalhães MR, De Amorim Gomes MA, Da Cunha HF. The impact of global climate change on the geographic distribution and sustainable harvest of Hancornia speciosa Gomes (Apocynaceae) in Brazil. Environ Manag. 2016;57:814–21. https://doi.org/10.1007/s00267-016-0659-5.
Nelder JA. New kinds of systematic designs for spacing experiments. Biometrics. 1962;18:283–307. https://doi.org/10.2307/2527473.
Peng X, Zhang Y, Cai J, Jiang Z, Zhang S. Photosynthesis, growth and yield of soybean and maize in a tree-based agroforestry intercropping system on the Loess Plateau. Agrofor Syst. 2009;76:569–77. https://doi.org/10.1007/s10457-009-9227-9.
Pereira AV, Pereira EBC, Silva Junior JF, Silva DB. Mangaba. In: Vieira RF, Costa TSA, Silva DB, Erreira FR, Sano SM, editors. Frutas Nativas da Região Centro-Oeste do Brasil. Embrapa Recursos Genéticos e Biotecnologia, Brasília. 2006. p. 188–213.
Pingali PL. Green revolution: impacts, limits, and the path ahead. Proc Natl Acad Sci U S A. 2012;109:12302–8. https://doi.org/10.1073/pnas.0912953109.
Pollastrini M, Holland V, Brüggemann W, Bruelheide H, Dănilă I, Jaroszewicz B, Valladares F, Bussotti F. Taxonomic and ecological relevance of the chlorophyll a fluorescence signature of tree species in mixed European forests. New Phytol. 2016;212:51–65. https://doi.org/10.1111/nph.14026.
R CORE TEAM. F: a language and environment for statistical computing. R foundation for statistical computing, Vienna, Austria. 2020. https://www.r-project.org/.
Ribeiro A, Guimarães P, Alvarez V. Recomendações Para uso de Corretivos e Fertilizantes em Minas Gerais 5 a Aproximação. CFSEMG, Viçosa. 1999. p. 359.
Righi C, Couderc V, Pereira C, Couto H. Responses of Eucalyptus camaldulensis sprouts to shade: an evaluation of canopy plasticity. Exp Agric. 2016;52(3):346–58. https://doi.org/10.1017/S0014479715000137.
Ronald M, Charles K. Weed suppression and component crops response in maize/pumpkin intercropping systems in Zimbabwe. J Agric Sci. 2012;4:231–6. https://doi.org/10.5539/jas.v4n7p231.
Sakaigaichi T, Tsuchida H, Adachi K, Hattori T, Tarumoto Y, Tanaka M, Hayano M, Sakagami J-I, Irei S. Phenological changes in the chlorophyll content and its fluorescence in field-grown sugarcane clones under over-wintering conditions. Sugar Tech. 2019;21:843–6. https://doi.org/10.1007/s12355-018-0693-0.
Santos LJ, Gléria AA, Custodio AM, Paim TP, Santos LC, Alves EM. Produtividade de abóbora cabotiá cultivada em consórcio e monocultivo. Sci Agrar. 2017a;16:516–20. https://doi.org/10.18188/1983-1471/sap.v16n4p516-520.
Santos MV, Ferreira EA, Valadão D, Oliveira FLR, Machado VD, Silveira RR, Souza MF. Brachiaria physiological parameters in agroforestry systems. Cienc Rural. 2017b. https://doi.org/10.1590/0103-8478cr20160150.
Schwartz G, Ferreira MDS, Lopes JDC. Silvicultural intensification and agroforestry systems in secondary tropical forests: a review. Rev Ciênc Agrar. 2015;58:319–26. https://doi.org/10.4322/rca.1830.
Silva GC, Braga FC, Lemos ES, Cortes SF. Potent antihypertensive effect of Hancornia speciosa leaves extract. Phytomedicine. 2016;23:214–9. https://doi.org/10.1016/j.phymed.2015.12.010.
Taiz L, Zeiger E. Fisiologia vegetal. 4th ed. Porto Alegre: Artmed; 2009.
Vieira Neto RV, Cintra F, Silva A, Silva Júnior J, Costa J, Silva A, Cuenca M. Sistema de Produção de Mangaba para os Tabuleiros Costeiros e Baixada Litorânea. Embrapa Tabuleiros Costeiros, Aracaju. 2002. p. 22.
Virlet N, Sabermanesh K, Sadeghi-Tehran P, Hawkesford MJ. Field Scanalyzer: an automated robotic field phenotyping platform for detailed crop monitoring. Funct Plant Biol. 2017;44:143–53. https://doi.org/10.1071/fp16163.
Weraduwage SM, Chen J, Anozie FC, Morales A, Weise SE, Sharkey TD. The relationship between leaf area growth and biomass accumulation in Arabidopsis thaliana. Front Plant Sci. 2015;6:167. https://doi.org/10.3389/fpls.2015.00167.
Wickham H. ggplot2: elegant graphics for data analysis. New York: Springer; 2016.
Yang T, Ma C, Lu W, Wan S, Li L, Zhang W. Microclimate, crop quality, productivity, and revenue in two types of agroforestry systems in drylands of Xinjiang, northwest China. Eur J Agron. 2021;124:126245. https://doi.org/10.1016/j.eja.2021.126245.
Zappi DC, Filardi FLR, Leitman P, Souza VC, Walter BM, Pirani JR, Morim MP, Queiroz LP, Cavalcanti TB, Mansano VF. Growing knowledge: an overview of seed plant diversity in Brazil. Rodriguésia. 2015;66:1085–113. https://doi.org/10.1590/2175-7860201566417.
Acknowledgements
We thank the Federal Institute of Goiano and CNPq.
Funding
The team appreciates the financial support provided by CNPq (SETEC/MEC Nº 17/2014 - Process: 468549/2014-5 and MCTI/MAPA/CNPq Nº 40/2014 - Process: 473115/2014-0) and the Goiano Federal Institute, through Campi Rio Verde, Iporá and Innovation Center.
Author information
Authors and Affiliations
Contributions
EMA—Part of the author's doctoral thesis. Planning, conducting reviews and writing the article. FGS—Advisor of the author's doctoral thesis. Planning, conducting reviews and writing the article. RGA, LLL, TCdO, AMC, MR—Conducting, evaluating, and contributing to the writing of the article. JPP—Contributing to the writing of the article. TdoPP—Conducting, evaluating, statistical analysis and contributions in writing the article.
Corresponding author
Ethics declarations
Ethics approval and consent to participate
The activities carried out in the construction of the article do not require evaluation by an ethics council.
Consent for publication
The authors consent to CABI Agriculture and Bioscience to publish the full article.
Competing interests
We declare that there is no conflict of interest in the realization of this paper.
Additional information
Publisher's Note
Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
Supplementary Information
Additional file 1.
Effects of systems and seasons in pigments, fluorescence of chlorophyll, gas exchange, photosynthetically active radiation (PAR), and biometrics of H. speciosa plants.
Rights and permissions
Open Access This article is licensed under a Creative Commons Attribution 4.0 International License, which permits use, sharing, adaptation, distribution and reproduction in any medium or format, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons licence, and indicate if changes were made. The images or other third party material in this article are included in the article's Creative Commons licence, unless indicated otherwise in a credit line to the material. If material is not included in the article's Creative Commons licence and your intended use is not permitted by statutory regulation or exceeds the permitted use, you will need to obtain permission directly from the copyright holder. To view a copy of this licence, visit http://creativecommons.org/licenses/by/4.0/. The Creative Commons Public Domain Dedication waiver (http://creativecommons.org/publicdomain/zero/1.0/) applies to the data made available in this article, unless otherwise stated in a credit line to the data.
About this article
Cite this article
Alves, E.M., Silva, F.G., Avila, R.G. et al. Intercropping and environmental seasonality modulate the physiology and growth of Hancornia speciosa (Gomes). CABI Agric Biosci 5, 31 (2024). https://doi.org/10.1186/s43170-024-00235-0
Received:
Accepted:
Published:
DOI: https://doi.org/10.1186/s43170-024-00235-0