SciELO - Scientific Electronic Library Online

 
vol.95 número1Aspectos socioeconómicos y anomalías de temperatura: responsables del incremento del número de especies introducidas en las Islas Canarias (1940-2010)El efecto del cadmio en los nucleolos de las puntas de las raíces de Hordeum vulgare índice de autoresíndice de materiabúsqueda de artículos
Home Pagelista alfabética de revistas  

Servicios Personalizados

Revista

Articulo

Indicadores

Links relacionados

  • No hay artículos similaresSimilares en SciELO

Compartir


Botanical Sciences

versión On-line ISSN 2007-4476versión impresa ISSN 2007-4298

Bot. sci vol.95 no.1 México ene./mar. 2017

https://doi.org/10.17129/botsci.636 

Ecology

Morphological variation in fruits and seeds of Ceiba aesculifolia and its relationship with germination and seedling biomass

Variación morfológica en frutos y semillas de Ceiba aesculifolia y su relación con la germinación y la biomasa de las plántulas

Noé Velázquez-Rosas1  * 

Betsabé Ruiz-Guerra2 

María Esther Sánchez-Coronado3 

Alicia Gamboa de Buen3 

Alma Orozco-Segovia3 

1 Centro de Investigaciones Tropicales, Universidad Veracruzana, Veracruz, México.

2Instituto de Ecología A.C., Red de Biología Evolutiva, Xalapa, Veracruz, México.

3Departamento de Ecología Funcional, Instituto de Ecología, Universidad Nacional Autónoma de México, México, D. F., México.


Abstract:

Background:

Morphologic variation in fruits and seeds affects the performance and adaptation of plants. Only a few studies have integrally analyzed these variables and their effects in plant germination and early growth in tropical dry forest (TDF).

Questions:

Do the size and shape of fruits influence the number and mass of seeds? Is there a positive relation between seed traits, germination and seedling growth?

Species studied:

Ceiba aesculifolia.

Study site:

A TDF growing in a lava field in Actopan, Veracruz:

Methods:

The fruits of 35 individuals of one population were classified into three size categories (small, medium and large), from which fresh fruit mass and length, number and mass of seeds, and seed lipid and water content were determined. In addition, lag time, germination rate (velocity) and percentage, and seedling biomass were assessed.

Results:

Fruit mass was positively related to seed mass, but fruit weight was negatively related to number of seeds. Larger seeds had higher lipid and water content. No differences were registered in lag time or final germination percentage. Heavier seeds produced seedlings with higher biomass.

Conclusions:

The number and size of seeds in fruits may determine differential capabilities for seedling establishment.

Key words: tropical dry forest; Ceiba aesculifolia; germination; fruit size; seedling size

Resumen:

Antecedentes:

La variación morfológica de frutos y semillas afecta el desempeño y adaptación de las plantas. En pocos estudios se han analizado estas variables, sus efectos en la germinación y crecimiento en plántulas de bosques tropicales secos.

Preguntas:

¿El tamaño y forma de los frutos determina el número y peso de las semillas? ¿Existe una relación positiva entre las características de las semillas, la germinación y el crecimiento de las plántulas?

Especie en estudio:

Ceiba aesculifolia.

Sitio de estudio:

Bosque tropical seco desallorrandose sobre mal país en Actopan, Veracruz.

Métodos:

En una población de 35 individuos se clasificaron los frutos en tres categorías de tamaño (pequeño, medio, grande). En cada categoría se determinó el peso fresco, largo, número de semillas por fruto, así como el peso, contenido de lípidos y agua de las semillas. Además se determinó el tiempo de reposo, la velocidad y porcentaje de germinación y la biomasa de las plántulas.

Resultados:

El peso de los frutos estuvo relacionado positivamente con el peso de las semillas, y negativamente con el número de semillas. Las semillas más grandes tuvieron mayor contenido de lípidos y agua. No se registraron diferencias en el tiempo de reposo, ni en los porcentajes de germinación. Las semillas con mayor peso producen las plántulas con mayor biomasa.

Conclusiones:

El número y tamaño de las semillas en los frutos puede determinar capacidades diferenciales de establecimiento de las plántulas.

Palabras clave: bosque tropical seco; Ceiba aesculifolia; germinación; tamaño de fruto; tamaño de plántula

Fruit and seed sizes have an impact on plant dispersion patterns and reproductive success (Primack 1987, Bolmgren & Eriksson 2005, Bolmgren & Eriksson 2010). Nevertheless, few studies have integrally analyzed the relationships between these attributes and their ecologic implications (Bolmgren & Eriksson 2010), although they can provide relevant information for establishing ecological restoration strategies in tropical ecosystems (Orozco-Segovia & Sánchez-Coronado 2009).

In general, it has been demonstrated that fruit type influences the size of seeds; species with fleshy fruits have larger seeds than species with dry fruits (Bolmgren & Eriksson 2010). In addition, there is a positive relationship between seed size and fruit size in species with fleshy fruits, which is explained in terms of a cost-benefit approach between the increment of seed dispersal capability and the reward for endozoochory dispersal (Coomes & Grubb 2003, Moles & Westoby 2006, Bolmgren & Eriksson 2010). Another factor affecting size and number of seeds in fleshy fruits is the size of the mother plants (Moles & Westoby 2006).

Seed biomass is one of the most important functional traits for plant performance and fitness (Coomes & Grubb 2003, Orozco-Segovia & Sánchez-Coronado 2009). This characteristic is associated with the amount of energy reserves in the embryos (Cipollini & Stiles 1991, Moegenburg 1996, Aparicio et al. 2002), the probability for successful germination (Baloch et al. 2001) and the ability to avoid pathogens and herbivores (Coomes & Grubb 2003). In general, it has been reported among different ecosystems that the seed size of a plant is negatively related to the number of seeds it can produce, and plant species that produce smaller-seeds are considered competitively superior in colonizing different environments (Silvertown 1989, Coomes & Grubb 2003). Conversely, biomass is positively associated with seedling survival because larger seeds develop more vigorous seedlings (with greater biomass in their roots and cotyledons) and with greater soil emerging potential (Pieta & Ellis 1991, Aparicio et al. 2002), which confers them competitive advantages when facing the lack of resources (light and nutrients) or the negative influence of random events, such as dry periods or partial damage caused by herbivores (Coomes & Grubb 2003). Another aspect influenced by the size and shape of seeds is the amount of time they can persist in the soil seed bank (Cerabolini et al. 2003). Smaller, more compacted seeds, tend to remain in the soil longer than larger, more elongated seeds (Funes et al. 1999).

Although the importance of fruit size, seed size and seed shape on the performance and fitness of plants has been widely analyzed at the community level, little attention has been paid to the intra-specific variation of these variables and their ecological implications (Khurana & Singh 2001, Bolmgren & Eriksson 2010). The limited information available shows that variation in seed-size is very frequent within populations and even among individuals, which suggests that different selective forces regulate size variation within a population (Moegenburg 1996, Bu et al. 2007, Lázaro & Traveset 2009). At the intra-specific level, it has been recognized that seed size and shape influence germination rates, seed dormancy, vigor and survival of seedlings (Anderson & Milberg 1998, Moles et al. 2000, Baloch et al. 2001). This variation can be relevant for the survival of many species in heterogeneous environmental conditions (Khurana & Singh 2001, Coomes & Grubb 2003). For example in Albizia procera, a tropical dry forest (TDF) tree, it has been reported that larger seeds produce more vigorous seedlings with a greater ability to withstand water stress compared to smaller seeds. This could favor the survival of this species under variable dry periods (Khurana & Singh 2000).

Currently, TDF are seriously endangered due to human activities that threaten the biodiversity of these ecosystems. In México, TDF occupy only 21 % of their original extension, and annual deforestation rates are estimated to be nearly 2 % (Trejo & Dirzo 2000). Given the critical status of the TDF, strategies need to be developed to reverse the current trend of deforestation processes; thus, it is crucial to study the functional traits of seeds, their relationship with germination and the establishment of plants (Khurana & Singh 2001, Orozco-Segovia & Sanchéz 2009).

Ceiba aesculifolia (Kunth) Britten & Baker f. is a native tree from the Mexican TDF and shows great variation in size and shape of its fruits and seeds (Niembro et al. 2010). These characteristics make it an ideal candidate for studying the effects of morphological variation in fruits and seeds, seedling performance, and their possible use in restoration programs. In this study we analyzed morphological variation of fruits and seeds of this species to answer the following questions: Do size and fruit shape influence the number and size of seeds? Is there a positive relationship between seed size, germination and seedling growth? This study also discusses the usefulness of these data for the implementation of management and reproduction programs for this species in ecological restoration in the TDF of Mexico.

Materials and methods

Study species. Ceiba aesculifolia (Malvaceae) is a tree 15 to 20 m tall with a diameter at breast height of up to 60 cm. It is a monopodial tree; its trunk is covered with conical thorns, and its canopy is rounded and dense. The flowers are actinomorphic with funnel-shaped calyx and 5 brown petals up to 14 cm long. Its fruit is a dehiscent capsule with a woody pericarp, purple to bright red or reddish brown. The seeds are ovoid-globose 8 to 10 mm in diameter. Each seed has a tiny embryo with folded foliar cotyledons and a fleshy endosperm wrapping around the embryo and the cotyledons. The seeds are orthodox and can be stored at -20 °C with 15 % relative humidity (Avedaño 1998, Niembro et al. 2010). This tree species grows in preserved and secondary TDF in Mexico; therefore, it has been considered an important species for the restoration of these ecosystems (Valle-Díaz et al. 2009, Niembro et al. 2010).

Study area. This study was conducted in a lava field in the locations of “Trapiche del Rosario and Chicuasen”, in Actopan, Veracruz. In these locations, TDF fragments, secondary vegetation, riparian vegetation and agricultural lands integrate the landscape in the high river basin of the Actopan River (Castillo-Campos et al. 2007). These ecosystems develop on a lava field with upwelling rocks. The soil is heterogeneous in depth, but is mainly shallow. The TDF of this region has a very rich flora in which over 660 species of vascular plants have been recorded. The most common tree species are: Bursera cinerea, Cephalocereus palmeri var. sartorianus, Lysiloma microphylla, L. acapulcense and Pseudobombax ellipticum var. tenuiflorum (Castillo-Campos et al. 2007).

The climate is Aw1(w), warm-humid with rains in the summer (winter rainfall is lower than 5 %), with an average annual temperature of 22.3 °C (a minimum temperature of 11 °C and a maximum of 30 °C) (García 1988). The annual average rainfall is 1053.5 mm, with a dry season between October and May (average rainfall is 22 mm) and a rainy season from June to September (monthly average rainfall is 209 mm) (García 1988). Soils are shallow lithosols (Rossignol & Geissert 1987).

Data collection. Taking into account that the proximity of these collecting locations was less than 1 km, it was considered that the individuals of Ceiba aesculifolia used in this study were part of the same population. Thirty five individuals with fruits of different shapes and sizes were selected. Each tree produces a single category of form and size fruit. Between 5 and 10 fruits were collected from each individual. Two fruits per individual were randomly selected (N = 70) and fresh fruit mass, length and width were estimated for each one. From the mass distribution of the fruits, three size categories were established: small (150-250 g), medium (251-350 g) and large (> 351 g). Subsequently, the fruits were dried at room temperature until the capsules opened (3-5 days). The seeds from each fruit were counted and separated from the silky fiber that covers them. From each fruit, 20 seeds were randomly selected to determine fresh seed mass; these seeds were used for the germination test (N = 1,400). The seeds were sown in 10 germination trays with independent compartments and a capacity of 200 ml, and the trays were filled with a mixture of sand and soil (1:1) from the TDF. In each tray, 20 seeds were sown at 0.5 cm in depth. The germination tests were carried out in a greenhouse, at 24 °C. The trays were watered every day at field capacity and monitored daily for 30 days. A seed was considered germinated when the radicle emerged from the seed coat (sensuFenner & Thompson 2005). To determine seedlings dry mass, seedlings were harvested when they begun to produce true leaves (approximately 35 days after germination). The seedlings were dried for 72 hours, until they reached a stable weight and were weighed separating stems and root. Then, the root:shoot ratio was calculated.

Seed lipid and water content. Seed lipid content of each fruit category was determined in 28 mg of dry tissue in accordance with the Bligh and Dyer (1959) method of extraction. Seed water content was calculated as an oil-free percentage (OF) on a wet (WCofwb) and dry basis (WCofdb) in accordance with Caddick (2005):

WCofdb=(100×WCdb)(100-OCdb)-1

where OCdb is the oil content on a dry basis.

Data Analysis. Fruit mass, fruit length:width ratio, seed fresh mass and seedlings dry biomass, were all compared among the three categories with ANOVA tests. Multiple comparisons were performed with the Tuckey´s test (P ≤ 0.05) using JMP software (Version 8.0.2., SAS Institute Inc., Cary NC, USA). The number of seeds per fruit, seed lipid and water contents (fresh and dry basis) were analyzed using a generalized linear model (GLM) with a Poisson distribution and a log link function. These statistical analyses were conducted in R 2.5.2 (R development core team) with the glme function (in the gmodels library). To fit linear effects, model contrasts were performed with the estimable function (Warnes et al. 2006).

Accumulated germination percentage of each category was adjusted to the sigmoid exponential model, Y = a + b(-cx), with the program Table Curve 2Dv 5 (AISN. Software, Inc., Chicago IL USA), with which, lag time and germination rates (velocity) for seeds of each fruit category were calculated (González-Zertuche et al. 2001). Subsequently, both variables were compared among the fruit categories, using a generalized linear model (GLM) with a Poisson distribution and a log link function. The final germination percentage among fruit categories, dry seedling mass and root shoot ratio were also analyzed with ANOVA tests. Percentages were previously arc-sin transformed. The relationships between seed and fruit variables were determined with linear regression analysis, and the following relationships were analyzed: 1) dry and fresh seed mass, 2) seed lipid content with seed dry mass, fresh mass and water content; 3) dry or fresh mass with seed water content (fresh and dry basis), 4) the relationship between seed water content on a wet basis with the water content on a dry basis 5) seedling dry mass and oil seed content. Fittings were done using Table Curve, v.3 software (AISN Software, Chicago, IL, USA).

Results

Shape and mass of fruits and seeds. Among the fruit categories of C. aesculifolia, there were significant differences in fruit mass, shape (length:width ratio) and seed mass (Figure 1). The average mass of the fruits varied between 194.2 and 382.0 g, the highest values were recorded in the large category (F (6,67) = 126.9, P < 0.0001; Figure 1a). Regarding fruit shape, based on the length:width ratio, the small and large categories showed the most elongated fruits (F (6,67) = 6.11, P < 0.01; Figure 1b). There were significant differences in the number of seeds per fruit category (χ2 = 51.27, d.f. = 2, P=0.0001), the small category had a lower mean value than medium and large categories (χ2 = 47.51, d.f. = 2, P < 0.0001; χ2 = 27.52, d.f. = 2, P < 0.000; respectively, Figure 1c). Seed fresh mass varied between 256.6 and 298.1 mg; the heaviest seeds were recorded in the large category (F (2,69) = 8.13, P = 0.0007; Figure 1d).

Figure 1 Morphological traits of fruits and seeds of three mass fruit categories of C. aesculifolia. Different letters on bars indicate significant differences between categories. Mean values (+SE). 

The fruit length:width ratio and the number of seeds had a low but significant negative relationship (R 2 = 28, P < 0.001). The fruit mass and the seed mass had a positive relationship (R 2 = 0.22; P < 0.0001). The more spherical fruits had more seeds. The heaviest fruits had seeds with greater mass.

Seeds lipid and water content. Seed lipid content significantly varied among the categories (χ2 = 17.45, d.f. = 2, P < 0.0001) from 19.27 % to 28.89 % (Figure 2a). The significantly highest values were found in the large and medium seed categories (χ2 = 17.05, d.f. = 1, P < 0.0001; χ2 = 5.37, d.f. = 1, P < 0.05; respectively). Seed water content on fresh and dry basis also showed significant differences among the categories (χ2 = 18.88, d.f. = 2, P < 0.0001; χ2 = 23.38, d.f. = 2, P < 0.0001, respectively), with values between 9.58 ± 0.31 % and 13.49 ± 0.31 % on a fresh basis, and between 10.35 ± 0.4 % and 14.93 ± 0.26 % on a dry basis (Figure 2b, c). In both cases the highest values were found in the large category, and the lowest values were found in the small (χ2 = 12.18, d.f. = 1, P < 0.001; χ2 = 14.78, d.f. = 1, P < 0.001; respectively) and medium categories (χ2 = 15.11, d.f. = 1, P < 0.001; χ2 = 18.87, d.f. = 1, P < 0.0001, respectively).

Figure 2 Lipid and water content in seeds and germination traits of the three mass fruit categories of C. aesculifolia. Different letters on bars indicate significant differences between categories. Mean values (+SE). 

All relationships between seed variables of the three categories were significant and positive. The functions that describe each of these relationships, as well their statistical values, are shown in Table 1.

Table 1 Relationships between seed variables of Ceiba aesculifolia. WCofwb =water content oil free fresh basis, WCofdb = water content oil free dry basis. 

Seed variables function R2 F P
Fresh mass and dry mass Y = a + bx 0.99 26192.4 0.00001
Fresh mass and lipid content Y = a + bxc 0.91 178.55 0.00001
Dry mass and lipid content Y = a + bxc 0.88 152.52 0.00001
Fresh mass and WCofwb Y = a + bx3 0.93 476.09 0.00001
Fresh mass and WCofdb Y = a + bxc 0.92 197.87 0.00001
Dry mass and WCofwb Y = a + bxc 0.91 179.15 0.00001
Dry mass and WCofdb Y = a + bxc 0.91 173.53 0.00001
WCofwb and WCofdb Y = a + bx 0.99 136003.1 0.00001

Germination. Seed lag time varied between 9.8 and 11.5 days (Figure 2d), but there were no significant differences among seeds of the three fruit categories (χ2 = 4.14, d.f. = 2, P = 0.126). Germination rates varied between 9.7 and 14.4 % d-1 (Figure 2e). Seeds from the fruits of the small and large categories showed the highest values (χ2 = 25.69, d.f.= 2, P < 0.0001), and were significantly different from the medium category (χ2 = 20.22, d.f. = 2, P < 0.001; χ2 = 17.94, d.f. = 2, P < 0.0001, respectively). Final germination percentage did not change between categories (P > 0.05, Figure 2f). Accumulated germination is shown in Figure 3.

Figure 3 Cumulative germination of the seeds of Ceiba aesculifolia from the: (○) small, (●) medium and (▲) large mass fruit categories. 

There were significant differences in seedling total dry mass between fruit categories (F (2,248) = 24.76, P < 0.0001), and the large category had the highest values (Figure 4a). In the root: shoot ratio, no significant differences were found among the categories (F (2,248) = 0.46, P = 0.625; Figure 4b). Seed mass significantly influenced seedling dry mass (R 2 = 0.62, P = 0.001, Figure 4c); heavier seeds produced larger seedlings. Seed lipid content had also a significant positive relationship with seedling dry mass (R 2 = 0.96, P = 0.02).

Figure 4 Dry mass of seedlings and relationships between seed mass and seedling dry mass of the three mass fruit categories of C. aesculifolia. Different letters on bars indicate significant differences between categories. Mean values (+SE). 

Discussion

In the TDFs, spatial-temporal variations in soil moisture, light, temperature, nutrients and intensity of predation can affect the reproductive traits of plants (Khurana & Singh 2001, Herrerías et al. 2008). Our results suggest that variation in the mass and shape of fruits of Ceiba aesculifolia is positively related with the number of seeds per fruit and seed mass. These results also suggest that the size of seeds affected the early growth of seedlings.

Fruit and seed traits. The relationships between fruit size and seed size are well understood in species with fleshy fruits dispersed by animals (Bolmgren & Eriksson 2010); however, among dry fruits, such as the dehiscent capsules of C. aesculifolia, these relationships have not been well studied. In general, in fleshy fruits there is a positive relationship between fruit mass and seed mass (Bolmgren & Eriksson 2010). In Ceiba aesculifolia, we found a similar relationship; the heaviest fruits produced heavier seeds. Moreover, fruit shape was related to the number of seeds; the most elongated fruits produced fewer seeds. The advantages of heavier seeds for the survival and establishment of seedlings have been recognized in moist and shady environments; however, in dry environments, their role is ambiguous and has been strongly questioned (Leishman & Westoby 1994, Orozco-Segovia & Sánchez-Coronado 2009). In the case of C. aesculifolia, heavier seeds produced larger seedlings; nevertheless, the advantages of heavier seeds for seedling establishment should be viewed with caution and tested in the field, because heavier seeds have more limited dispersal capabilities, and are more predated than smaller seeds (Herrerías et al. 2008).

Both in dry and humid tropical forests, environmental conditions experienced by mother plants in temporal or spatial scales affect the traits of their seeds (Grubb & Coomes 1997, Khurana & Singh 2001, Soriano et al. 2011). In some species of the TDF, it has been recorded that heavier seeds, with greater nitrogen and lipid content are produced in drier years (Soriano et al. 2011); conversely in trees and shrubs of the rainforest, nutrient concentration in the seeds is associated with the nutritional status of the soil in which the mother plants grow (Grubb & Coomes 1997). In the case of Ceiba aesculifolia, there is no evidence to help us discern which factors determine the variation recorded in fruits and seeds. The soil in the lava field where the TDF develops is heterogeneously deposited within rocks cavities, pockets, crevasses and slight depressions. In some of these, the soil depth and organic matter is higher than in others (Castillo-Campos et al. 2007). This soil variation might determine the resources available for the reproduction of individuals of C. aesculifolia. Trees with heavier seeds and fruits are mainly distributed in deeper soil sites (cavities, pockets) close to the farming areas (30 % of the trees in the collection showed this condition); while individuals with smaller fruits are more frequently found in areas with shallow soil (N. Velázquez-Rosas unpublished data).

Seed size, germination response and establishment of seedlings. In the TDF trees, it has been recognized that seed size affects germination percentage (Khurana & Singh 2001); heavier seeds have higher germination rates than smaller ones (Dileep et al. 1994, Singh & Khan 1998), because they have greater energetic reserves that can be used for germination (Khurana and Singh 2001). Previous studies showed that in Ceiba aesculifolia, heavier seeds germinate in greater proportions (95 %; Herrerías et al. 2008). Our results differ, because germination percentages recorded in all seed sizes were lower than 60 % and did not differed between fruit size categories. In C. aesculifolia, it is difficult to discern the causes that determine the relationship between seed size and the evaluated germination traits in terms of energy reserves (as has been suggested for other species), but we found no relationship between germination and seed lipid content. This pattern has been reported for other species of TDF (Vargas et al. 2015). The differences in the recorded germination responses in C. aesculifolia could be originated genetically, or due to phenotypic plasticity associated with maternal effects; the latter has been noted as a frequent trait among species growing in environments with heterogeneous and unpredictable conditions (Fenner 1991, Khurana & Singh 2000, Khurana & Singh 2001, Moles & Westoby 2006, Soriano et al. 2011).

Seed size and its influence on the establishment and survival of the seedlings have been discussed under a cost-benefit approach, between the number of seeds produced and their probability of establishment (Moles & Westoby 2006). In general, it is assumed that species with small seed produce more seedlings, but their establishment and survival success are lower, compared to those of species with larger seeds (Moles & Westoby 2006). These differences may be due to the amount of reserves stored by seed cotyledons, which are used for growth in early development stages (roots and photosynthetic tissue) (Hewitt 1998, Kitajima 2002, Soriano et al. 2011). In the case of Ceiba aesculifolia, trees with larger seeds, which show the highest contents of lipids and water, produced seedlings with greater biomass, which could increase their establishment and survival probabilities. This is consistent with what was reported for Albizia procera; larger seeds produce the most vigorous seedlings, and they have a greater ability to withstand water stress for longer periods, thus increasing their chances of establishment (Khurana & Singh 2000).

The persistence of a wide variation in the size of the seeds at an intra-specific level has been interpreted as a favorable condition for many species to thrive in highly heterogeneous, or unpredictable environments (Khurana & Singh 2000, Khurana & Singh 2001, Coomes & Grubb 2003). The results recorded for Ceiba aesculifolia in the relationships among seed size, lipid and water content and seedling biomass suggest that seed size variation can determine differential capabilities for settling in the TDF. It is necessary to develop field experiments to analyze where the most suitable microclimate conditions for germination, development and establishment of seedlings of different morph seeds are found.

Implications for ecological restoration. Knowledge of the functional characteristics of seeds and germination patterns, as well as the ecological requirements for germination and seedling growth, will encourage the development of ecological restoration strategies for the recovery of ecosystems (Khurana & Singh 2001, Orozco-Segovia & Sánchez-Coronado 2009). The ability to adapt to various environmental conditions may be an important attribute found in Ceiba aesculifolia that can be used in ecological restoration programs of the TDF (Valle-Díaz et al. 2009). For instance, in TDFs with nutrient deficient soils and low water retention, the selection of large seeds of a desired species might increase their establishment and survival success rates (Khurana & Singh 2001). This strategy can be applied for the introduction of C. aesculifolia in disturbed sites, whereas the use of small and medium size seeds could be considered for sites with more favorable environmental conditions. The introduction of adequate phenotypes to specific microclimatic conditions can increase their establishment success in restoration programs of the TDFs.

Acknowledgments

The authors thank David Montano and Mauricio Juárez for their assistance with the field work. The study was funded by Biological Conservation Program of Tropical Research Center, Universidad Veracruzana and the Universidad Nacional Autónoma de México (DGAPA, PAPIIT IN205715). We thank H. Paz and two anonymous reviewers for comments on a previous draft.

Literature cited

Andersson L, Milberg P. 1998. Variation in seed dormancy among mother plants, populations and years of seed collection. Seed Science Research 8:29-38. DOI: https://doi.org/10.1017/S0960258500003883 [ Links ]

Aparicio N, Villegas D, Araus JL, Blanco R, Royo C. 2002. Seedling development and biomass as affected by seed size and morphology in durum wheat. Journal of Agricultural Science 139:143-150. DOI: 10.1017/S0021859602002411 [ Links ]

Avedaño S. 1998. Bombacaceae. Flora de Veracruz 107:1-40. [ Links ]

Baloch HA, Di Tommaso A, Watson AK. 2001. Intrapopulation variation in Abutilon theophrasti seed mass and its relationship to seed germinability. Seed Science Research 11:335-343. DOI: 10.1079/SSR200190 [ Links ]

Bligh EG, Dyer WJ. 1959. A rapid method of total lipid extraction and purification. Canadian Journal of Biochemistry and Physiology 37:911-917. DOI: 10.1139/o59-099 [ Links ]

Bolmgren K, Eriksson O. 2005. Fleshy fruits - origins, niche shifts, and diversification. Oikos 109:255-272. DOI: 10.1111/j.0030-1299.2005.12663.x [ Links ]

Bolmgren K, Eriksson O. 2010. Seed mass and the evolution of fleshy fruits in angiosperms. Oikos 119:707-718. DOI: 10.1111/j.1600-0706.2009.17944.x [ Links ]

Bu H, Chen X, Xu X, Liu K, Jia P, Du G. 2007. Seed mass and germination in an alpine meadow on the eastern Tsinghai-Tibet plateau. Plant Ecology 191:127-149. DOI: 10.1007/s11258-006-9221-5 [ Links ]

Caddick L. 2005. Moisture isotherms and conversion of indices used to describe moisture relations in stored grain. < http://sgrl.csiro.au/storage/moisture/conversion.html > (accessed June 24, 2007). [ Links ]

Castillo-Campos G, Dávila-Aranda P, Zavala-Hurtado JA. 2007. La selva baja caducifolia en una corriente de lava volcánica en el centro de Veracruz: lista florística de la flora vascular. Boletín de la Sociedad Botánica de México 80:77-104. DOI: http://www.redalyc.org/articulo.oa?id=57780008Links ]

Cerabolini B, Ceriani RM, Caccianiga M, De Andreis R, Raimondi B. 2003. Seed size, shape and persistence in soil: a test on Italian flora from Alps to Mediterranean coasts. Seed Science Research 13:75-85. DOI: 10.1079/SSR2002126 [ Links ]

Cipollini ML, Stiles EW. 1991. Seed predation by the bean weevil Acanthoscelides obtectus on Phaseolus species: consequences for seed size, early growth and reproduction. Oikos 60:205-214. DOI: 10.2307/3544867 [ Links ]

Coomes DA, Grubb PJ. 2003.Colonization, tolerance, competition and seed-size variation within functional groups. Trends in Ecology and Evolution 18:283-291. DOI: httt://dx.doi.org/10.1016/S0169-5347(03)00072-7 [ Links ]

Dileep M, Sudhakara K, Santhoshkumar AV, Nazeema KK, Ashokan PK. 1994. Effect of seed size, rooting medium and fertilizers on the growth of seedlings of Ceiba pentandra (Linn) Gaertn. Indian Journal of Forestry 17:293-300. [ Links ]

Fenner M. 1991. The effects of the parent environment on seed germinability. Seed Science Research 1:75-84. DOI: https://doi.org/10.1017/S0960258500000696 [ Links ]

Fenner M, Thompson K. 2005. The ecology of seeds. Cambridge: Cambridge University Press. [ Links ]

Funes G, Basconcelo S, Díaz S, Cabido M. 1999. Seed size and shape are good predictors of seed persistence in soil in temperate mountain grasslands of Argentina. Seed Science Research 9:341-345. DOI: https://doi.org/10.1017/S09602585599000355 [ Links ]

García E. 1988. Modificaciones al sistema de clasificación climática de Köppen. México D.F.: Instituto de Geografía-UNAM [ Links ]

González-Zertuche L, Vázquez-Yanes C, Gamboa A, Sánchez-Coronado ME, Aguilera P, Orozco-Segovia A. 2001. Natural priming of Wigandia urens seeds during burial: effects on germination, growth and protein expression. Seed Science Research 11:27-34. DOI: https://doi.org/10.1079/SSR200057 [ Links ]

Grubb PJ, Coomes DA. 1997. Seed mass and nutrient content in nutrient-starved tropical rainforest in Venezuela. Seed Science Research 7:269-280. DOI: https://doi.org/10.1017/S0960258500003627 [ Links ]

Herrerías-Diego Y, Quesada M, Stoner KE, Lobo JA, Hernández-Flores Y, Sánchez-Montoya G. 2008. Effect of forest fragmentation on fruit and seed predation of the tropical dry forest tree Ceiba aesculifolia. Biological Conservation 141:241-248. DOI: https://dx.doi.org/10.1016/j.biocon.2007.09.017 [ Links ]

Hewitt N. 1998. Seed size and shade tolerance: a comparative analysis of North American temperate trees. Oecologia 114: 432-440. DOI: 10.1007/s004420050467 [ Links ]

Khurana E, Singh JS. 2000. Influence of seed size on seedling growth of Albizia procera under different soil water levels. Annals of Botany 86:1185-1192. DOI: https://doi.org/10.1006/anbo.2000.1288 [ Links ]

Khurana E, Singh JS. 2001. Ecology of seed and seedling growth for conservation and restoration of tropical dry forest: a review. Environmental Conservation 28:39-52. DOI: https://doi.org/10.1017/S0376892901000042 [ Links ]

Kitajima K. 1996. Cotyledon functional morphology, patterns of seed reserve utilization and regeneration niches of tropical tree seedlings. In: Swaine MD, ed. The ecology of tropical forest tree seedlings. New York: Parthenon, 193-210. [ Links ]

Lázaro A, Traveset A. 2009. Does the spatial variation in selective pressures explain among-site differences in seed mass? A test with Buxus balearica. Evolutionary Ecology 23:847-865. DOI: 10.1007/s10682.008-9275-z [ Links ]

Leishman MR, Westoby M. 1994. The role of seed size in seedling establishment in dry soil conditions-experimental evidence from semi-arid species. Journal of Ecology 82:249-258. DOI: http://links.jstor.org/sici?sici=0022-0477%28199406%2982%3A2%3C249%3ATROSSI%3E2.0.CO%3B2-FLinks ]

Moegenburg SM. 1996. Sabal palmetto seed size: causes of variation, choices of predators, and consequences for seedlings. Oecologia 106:539-543. DOI: 10.1007/BF00329713 [ Links ]

Moles AT, Hodson DW, Webb CJ. 2000. Seed size and shape and persistence in soil in the New Zealand Flora Oikos 89:541-545. DOI: http://www.jstor.org/stable/3547639Links ]

Moles AT, Westoby M. 2006. Seed size and plant strategy across the whole life cycle. Oikos 113:91-105. DOI: 10.1111/j.0030-1299.2006.14194.x [ Links ]

Niembro-Rocas A, Vázquez-Torres M, Sánchez-Sánchez O. 2010. Árboles de Veracruz, 100 especies para la reforestación estratégica. Xalapa: Comisión Organizadora del Estado de Veracruz de Ignacio de la Llave para la Commemoración del Bicentenario de la Independencia Nacional y del Centenario de la Revolución Méxicana / Secretaría de Educación-Gobierno del Estado de Veracruz. [ Links ]

Orozco-Segovia A, Sánchez-Coronado ME. 2009. Functional diversity in seeds and its implications for ecosystem functionality and restoration ecology. In: Gamboa-de Buen A, Orozco-Segovia A, Cruz-García F, eds. Functional diversity of plant reproduction. Kerala: Research Signpost, 175-216. [ Links ]

Pieta FC, Ellis RH. 1991.The development of seed quality in spring barley in four environments. II. Field emergence and seedling size. Seed Science Research 1:179-185. DOI: https://doi.org/10.1017/S096025800000842 [ Links ]

Primack RB. 1987.Relationships among flowers, fruits, and seeds. Annual Review of Ecology and Systematics 18:409-430. DOI: 10.1146/annurev.es.18110187.002205 [ Links ]

Rossignol JP, Geissert D. 1987. Morfoedafología del área de Xalapa-Coatepec: Recursos en Tierras, escala 1:75,000. Xalapa: Instituto Nacional de Investigaciones sobre Recursos Bióticos,Institut de Recherche pour le Développement (ORSTOM). [ Links ]

Singh ND, Khan ML. 1998. Influence of fruit weight and soil fertility on seed germination and seedling fitness of Dillenia indica Linn. Ecology, Environment and Conservation 4:45-47. [ Links ]

Silvertown J. 1989. The paradox of seed size and adaptation. Trends in Ecology & Evolution 4:24-26. DOI: http://dx.doi.org/10.1016/0169-5347(89)90013-X [ Links ]

Soriano D, Orozco-Segovia A, Márquez-Guzmán J, Kitajima K, Gamboa-de Buen A, Huante P. 2011. Seed reserve composition in 19 tree species of a tropical deciduous forest in Mexico and its relationship to seed germination and seedling growth. Annals of Botany 107:939-951. DOI: 10.1093/aob/mcr041 [ Links ]

Trejo I, Dirzo R. 2000. Deforestation of seasonally dry tropical forest: a national and local analysis in Mexico. Biological Conservation 94:133-142. DOI: http://dxdoi.org/10.1016/S0006-3207(99)00188-3 [ Links ]

Valle-Díaz O, Blanco-García A, Bonfil C, Paz H, Linding-Cisneros R. 2009. Altitudinal range shift detected trough seedling survival of Ceiba aesculifolia in an area under the influence of an urban heat island. Forest Ecology and Management 258:1511-1515. DOI: http://dxdoi.org/10.1016/j.foreco.2009.07.001 [ Links ]

Vargas GG, Werden LK, Powers JS. 2015. Explain legume success in tropical dry forests based on seed germination niche: a new hypothesis. Biotropica 47:277-280. DOI: 10.1111/btp.12210 [ Links ]

Warnes GR, Bolker B, Lumley T, Johson RC. 2006. gmodels: various R Programing tools for model fitting. v. 2.14.0 <http:// cran.r-project.org/src/contrib/PACKAGES.html > (accessed March 25, 2014) [ Links ]

Received: August 07, 2015; Accepted: February 11, 2016

* Corresponding author: Noé Velázquez-Rosas, e-mail: nvelazquezro@gmail.com

Creative Commons License This is an open-access article distributed under the terms of the Creative Commons Attribution License