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Madera y bosques

versão On-line ISSN 2448-7597versão impressa ISSN 1405-0471

Madera bosques vol.27 no.3 Xalapa  2021  Epub 28-Mar-2022

https://doi.org/10.21829/myb.2021.2732263 

Scientific papers

Storage time effect on the germination of Haematoxylum campechianum in Campeche, Mexico

Efecto del tiempo de almacenamiento en la germinación de Haematoxylum campechianum en Campeche, México

Joel Leonel Euan-Tun1 

Enrique Alfonso González-Durán1 

José Efraín Ramírez-Benítez1 

Pedro Zamora-Crescencio2 

Jorge Albino Vargas-Contreras1 

Ulises Rodríguez-Robles3  4 

Jane Kelita Enríquez-Hernández1 

José Humberto Caamal-Velázquez5 

José Luis Aragón-Gastélum1  * 

1Universidad Autónoma de Campeche. Facultad de Ciencias Químico-Biológicas. San Francisco de Campeche, Campeche, México.

2Universidad Autónoma de Campeche. Centro de Investigaciones Históricas y Sociales. San Francisco de Campeche, Campeche, México.

3Universidad de Guadalajara. Centro Universitario de la Costa Sur. Departamento de Ecología y Recursos Naturales. Autlán de Navarro, Jalisco, México.

4Universidad de Guadalajara. Centro Universitario de la Costa Sur. Laboratorio de Ecosistemas y Agroecosistemas. Autlán de Navarro, Jalisco, México.

5Colegio de Postgraduados. Campus Campeche. Champotón, Campeche, México.


Abstract

Haematoxylum campechianum L. (Fabaceae), is an economically and culturally important tropical tree distributed across Central America and the Yucatán Peninsula, Mexico. To contribute to the conservation of this species, it is important to understand the seed germination process; however, research in this subject on H. campechianum remains scarce. We evaluated the relationship between the H. campechianum seed storage time and its fresh weight and germination. Mature seeds were collected in the municipality of Palizada, Campeche, Mexico, from 2016 to 2019, stored at 25 °C and 60%-80% relative humidity until experimentation after the 2019 collection. Seed replicates (10, comprising 25 seeds) were weighed to estimate fresh weight per collection year. Seed viability was determined by means of the tetrazolium test, while germination was carried out in Petri dishes using cotton as a substrate under a 12-hr photoperiod at 25 °C. The seeds collected in 2019 presented a high viability and germination (100% and 98.5% respectively), in contrast with those collected in 2018, which presented a drastic reduction in the values for these parameters (55% and 54%, respectively). Null viability and germination were observed in seeds collected in 2016 and 2017. The seeds collected in 2016 showed the highest fresh weight values than the other years sampled. The results indicate that the viability and germination of H. campechianum seeds were observed to be affected by storage time, the recently harvested seeds presented a higher viability and germination than older seeds. Therefore, the H. campechianum seeds could be recalcitrant because they presented an accelerated ageing process over the collection periods.

Keywords: conservation; fresh weight; palo de tinte; recalcitrance; viability

Resumen

Haematoxylum campechianum L. (Fabaceae), es una un árbol tropical de importancia económica y cultural distribuida en Centroamérica y la Península de Yucatán, México. Para contribuir a la conservación de esta especie, es importante entender el proceso de germinación de semillas, sin embargo, las investigaciones sobre este tema en H. campechianum siguen siendo escasas. Se evaluó la relación entre el tiempo de almacenamiento de las semillas de H. campechianum y su peso fresco y germinación. Se recolectaron semillas maduras en el municipio de Palizada, Campeche, México, de 2016 a 2019, y se almacenaron a 25 °C y 60%-80% de humedad relativa hasta la experimentación después de la recolecta de 2019. Se pesaron lotes de semillas (10, conteniendo 25 semillas) para estimar el peso fresco por año de recolecta. La viabilidad de semillas se determinó mediante la prueba de tetrazolio, mientras que la germinación se realizó en cajas de Petri utilizando algodón como sustrato bajo un fotoperíodo de 12 h a 25 °C. Las semillas recolectadas en 2019 presentaron una alta viabilidad y germinación (100% y 98.5% respectivamente), en contraste con las recolectadas en 2018, que presentaron una reducción drástica en los valores para estos parámetros (55% y 54% respectivamente). Se observó nula viabilidad y germinación en semillas recolectadas en 2016 y 2017. Las semillas recolectadas en 2016 mostraron los valores de peso fresco más altos que los otros años muestreados. Los resultados indican que la viabilidad y la germinación de las semillas de H. campechianum se vieron afectadas por el tiempo de almacenamiento, las semillas recién cosechadas presentaron mayor viabilidad y germinación que las semillas más viejas. Por lo tanto, las semillas de H. campechianum pudieran ser recalcitrantes debido a que presentaron un proceso de envejecimiento acelerado durante los períodos de recolección.

Palabras clave: conservación; peso fresco; palo de tinte; recalcitrancia; viabilidad

Introduction

The Yucatán Peninsula (YP), is a region in south-eastern Mexico, covering 450 000 km2 bordered by the Gulf of Mexico and the Caribbean Sea, including the states of Campeche, Quintana Roo and Yucatan. It is considered a biotic province in the Neotropical region showing a high diversity (Morrone, 2005). In the YP, 2300 plant species have been documented across 956 genera and 161 families, of which the family Fabaceae is the best represented, with 78 genera and 225 species (Fernández Carnevali et al., 2012).

Haematoxylum campechianum L. (Fabaceae), commonly known as Palo de Tinte, is a species of tree native to the tropical region of the American continent and distributed across Guatemala, Belize, and the YP in Mexico (Niembro, 2002). In the YP, this species grows on deep clay substrata with poor drainage and a high moisture content, generally known as lowlands (Niembro, 2002). As a significant biocultural resource, H. campechianum is raw source for the extraction of dyes from pre-Columbian times, exponentially increasing during the Spanish colonization at the beginning of the 16th century (Dampier, 2004; Villegas & Torras, 2014). It is used for bioprospecting anti-inflammatory, antioxidant, and antiseptic active compounds (Norton, 1996; Duke, 2008), histochemical properties (reviewed by Avwioro, 2011) as well as anticarcinogens (Peng et al., 2014). Moreover, its trunks are used to produce posts for perimeter fences on rural land, coal and as firewood, while its leaves and shoots are used for fodder and ornamental purposes (Plasencia-Vázquez, Villegas, Ferrer-Sánchez, & Zamora-Crescencio, 2017). The latter due to its colorful flowers, nectar-polleniferous and visited by bees of the species Apis mellifera L. (Quezada-Euán, May-Itzá, & González-Acereto, 2001); thus, H. campechianum is a potential resource in the Mexican meliponiculture to production of honey and wax.

Studies undertaken on H. campechianum have mainly focused on aspects of its natural history (Niembro, 2002; Villegas & Torras, 2014), ecological restoration (Zamora-Cornelio, 2010), resilience in degraded environments (Pérez, 2014), as well as its distribution (Plasencia-Vázquez et al., 2017; Chablé-Vega et al., 2019), tree morphometric structure (Chablé-Vega et al., 2019) and ethnobotanical characteristics (Contreras, 2010). However, research seeking knowledge on the germination of the H. campechianum seeds has received little attention (Zamora-Cornelio, Ochoa-Gaona, Vargas Simón, Castellanos Albores, & de Jong, 2010).

The germination of seeds is one of the most crucial stages in plant development (Baskin & Baskin, 2014). Environmental factors, such as temperature, water, light, and pH determine the success of the germination process (Baskin & Baskin, 2014). However, as seeds do not indefinitely conserve their germination capacity, a high viability and germination rate depends, in large part, on storage conditions (Baskin & Baskin, 2014). For example, a high viability rate in dry-stored seeds (45 °C - 50 °C) depends, in large part, on the balance between the storage container moisture and oxygen (Ellis & Hong, 2007). However, this balance varies from species to species and depends on the seeds’ chemical composition and seed type.

Various adaptation strategies are observed in seed morphometry (e.g., size, biomass and/or fresh weight) and play an important role in the germination process and the establishment of seedlings (Rojas-Aréchiga, Mandujano, & Golubov, 2013). Large seeds and/or those with greater fresh weight present a higher level of nutrient reserves in the cotyledons, which tends to increase their viability, germination, survival, and emergence speed, making them more tolerant to adverse conditions than small seeds (Khurana & Singh, 2001; Loza-Cornejo, López-Mata, & Terrazas, 2008; Wang, Baskin, Cui, & Du, 2009).

Since many plant species develop under adverse environmental conditions (e.g., water scarcity as well as high temperatures and light intensity; Nobel, 2010), an important aspect to consider in the natural dynamics of the germination process is the differential response observed in seeds’ desiccation tolerance over time (Farrant, Pammenter, & Berjak, 1993; De Oliveira-Gentil, 2001). Therefore, desiccation tolerance is a crucial functional characteristic of the ecology of plant regeneration (Tweddle, Dickie, Baskin, & Baskin, 2003).

Typically, seeds can be classified as orthodox (Roberts, 1973; Tweddle et al., 2003; Wyse & Dickie, 2017), meaning that they are able to tolerate desiccation under low humidity conditions (3% - 7%), thus drastically reducing metabolic activity and, by means of prior rehydration, conserving a high viability rate (Roberts, 1973; Rangel Fajardo et al., 2011). These seeds can be easily conserved either in situ, via the formation of persistent seed banks in the soil (Thompson, 2000), or ex situ, where they are stored in germplasm banks (Rangel Fajardo et al., 2011).

Seeds can also, in contrast, be classified as recalcitrant when they remain metabolically active and do not tolerate desiccation, rapidly losing their viability below humidity levels of 12% - 31% (Roberts, 1973; Tweddle et al., 2003; Wyse & Dickie, 2017). Consequently, these seeds do not form persistent seed banks in the soil, they are not able to be stored in germplasm banks (Tweddle et al., 2003; Rangel Fajardo et al., 2011). A third seed type can be classified as intermediate, with these seeds capable of tolerating desiccation within a range of 7% - 20% humidity; however, their viability decreases more rapidly when stored at low (0 °C) rather than warm (12 °C - 21 °C) temperatures, over the long term (Roberts, 1973; Pritchard, 2004).

To date, few studies have focused on evaluating the germination of H. campechianum seeds. Zamora-Cornelio et al. (2010), found a high and speed germination (86%) in freshly harvested seeds of this species. These authors suggest a recalcitrant effect in the seeds of this species. Nevertheless, to test this hypothesis, long-term studies focused on assess variations in fresh weight, viability, and germination of the H. campechianum stored seeds are necessary.

Objectives

The present study aimed to analyze the effect of storage time on the fresh weight, viability, and germination of H. campechianum seeds.

Materials and methods

Study species

Haematoxylum campechianum L. (Fabaceae) (Palo de Tinte), is a tree species growing to a height of up to 15 m, with leaves that grow to lengths of 3 cm to 10 cm and comprise three to four pairs of sessile leaflets (Durán & Souza, 2014). Its nectar-polleniferous flowers are observed in axillary and terminal inflorescence arrangements, which are up to 12 cm in length, while its fruit is a 3 cm to 6 cm long flattened pod containing 1 to 2 seeds, 12 mm long, 3.9 mm wide, and 1 mm thick flattened seeds (Niembro, 2002). There is no information about seed production per tree, seed size and soil seed bank dynamics in H. campechianum. Research about phenology of this species also limited (Durán & Souza, 2014; Niembro, 2002).

Seed collection

The H. campechianum seeds were harvested in the municipality of Palizada, Campeche, Mexico (Fig. 1), in 2016, 2017, 2018, & 2019, between the months of March to July, the species’ fructification period (Centro de Investigación Científica de Yucatán [CICY], 2010). The climate is tropical monsoon (Am), the average annual temperature at the site is 26.2 °C, with temperatures of over 46 °C in spring (March-May) and below 18 °C in winter (December-February), and a mean precipitation of 1634.5 mm is observed during the rainy season, occurring between June and October (Comisión Nacional del Agua [Conagua] 2010); Servicio Meteorológico Nacional [SMN], 2020).

Figure 1 Location of the natural populations of Haematoxylum campechianum in the study area, in the municipality of Palizada, Campeche, Mexico. 

In the YP, this species forms dense monospecific groups in clay soils subject to periodic flooding that have poor drainage knowns as “tíntales (Niembro, 2002; Plasencia-Vázquez et al., 2017). For the four collection cycles, the seeds were obtained from pods of 20 mature individuals (at least 20 pods of three branches per mature individual were collected) pertaining to two adjacent tíntales in the study area (Fig. 1). A polyethylene mesh (1.83 m × 6.10 m) at 50% was placed under the tree canopy to retain the collected pods; subsequently, they were cleaned, and the seeds were extracted manually from pods, stored in muslin bags under 60% - 80% relative humidity conditions and a standard temperature of 25 °C, until the experiments inherent to this research began after the 2019 harvest.

Fresh weight

The seeds obtained in the abovementioned harvests were separated into ten replicates, comprising 25 seeds (n = 25) per each year of collection (2016, 2017, 2018, and 2019). Each replica was individually weighed, using a Cole-Parmer Symmetry analytical balance (precision ± 0.2 mg), to estimate the individual fresh weight (g, ± standard error = SE) per seed, per replicate and collection year.

Seed viability

This test was carried out in 2019 after all seed collections were completed. The tetrazolium test (Peters, 2000) was used with a 0.5% triphenyl tetrazolium chloride solution to determine the viability of the H. campechianum seeds. Five 20-seed replicates (n = 20) per collection year (2016, 2017, 2018, and 2019) were used to evaluate viability. The seeds in each replicate were placed in beakers and embedded in distilled water for 24 h prior to placement in the tetrazolium solution. Subsequently, each replicate of seeds was placed in a beaker, to which 50 ml tetrazolium solution was added and which was then wrapped in aluminium foil, in order to keep it in dark conditions, and a temperature of 25 °C for 24 h. In order to facilitate the ingress of the solution into the seed, an incision was made parallel to the hypocotyl axis using a scalpel (Aragón-Gastélum et al., 2018). Finally, the seeds were cut transversally with a scalpel to observe the embryos and ascertain whether they were viable. The embryos of the viable seeds presented a reddish hue under the microscope (Baskin & Baskin, 2014). With these data, the percentage seed viability (± SE) for each collection year was obtained.

Seed germination

The seed germination experiments were carried out in 100 mm × 15 mm Petri dishes using a sterile cotton layer as a substrate, moistened with 8 mL distilled water, 20 seeds per dish (10 replicas per collection year; n = 200), each of which were sealed with plastic film to avoid moisture loss. Once sealed, the Petri dishes were not watered during the entire experiment. The Petri dishes were incubated continuously at 25 °C (optimum temperature for the germination of H. campechianum seeds; Sánchez-Rendón, Pernús-Álvarez, Torres-Arias, Barrios, & Dupuig, 2019) and for a 12 h light/darkness photoperiod with 80% relative humidity for 30 days (period in which these experiments are typically monitored; see Baskin & Baskin, 2014) in a grow room. The germination data were recorded daily in this period, with a seed considered germinated when the radicle was visible. The data obtained was used to calculate the final germination percentage (± SE) for each collection. The H. campechianum seeds of each collection year (2016, 2017, 2018, and 2019) did not have any germination pre-treatment (Sánchez-Rendón et al., 2019).

Statistical analysis

The normality assumption for the variables was determined by means of the Kolmogorov-Smirnov and Lillifor tests (Hill & Lewicki, 2006). Since a normal adjustment for the fresh weight and viability data was not possible, in both cases, the X2 analysis was used for the comparison of medians. As no viability and germination were observed for the seeds collected in 2016 and 2017, germination performance over time was solely considered for the years 2018 and 2019 as treatments and was analyzed by means of the Wilcoxon signed-rank test, taking the germination times (days) as categories and the differences in daily germination values from 2018 to 2019 as di (Daniel & Cross, 2018).

The 2018 and 2019 germination data not adjusted to normal distribution were compared via the application of the Kruskal-Wallis test by ranks under non-parametric ANOVAs, while the data with a higher number of samples than the category size was analyzed via a one-way ANOVA with Newman-Keuls weighting (Daniel & Cross, 2018). The model explaining the germination observed considered the value of the residuals, the coefficient of determination R2, and the Fisher’s F value (McKellar & Lu, 2004), while the Chow test was used to compare the projections via a generalized logarithmic linear model, taking into account the difference in the residuals (Gujarati & Porter, 2009).

Results

Fresh weight

The statistical results indicate significant fresh weight differences between the treatments (collection year), considering an X2 = 27.20 and p < 0.05. The highest fresh seed weight (4.94 g ± 0.03 g, SE) was obtained in 2016. The 2017 seeds showed low mean fresh weight values than 2016, but also statistically differed between collection years (3.84 g ± 0.01 g). For the 2018 and 2019 seeds, lower in fresh weight values were found (3.63 g ± 0.02 g, and 3.67 g ± 0.06 g, respectively), no statistical differences between both treatments (Fig. 2).

Figure 2 Mean fresh weight of Haematoxylum campechianum seed batches (± standard error) harvested over four years of collection (X2 = 27.20 and p < 0.05). 

Seed viability

The highest viability was obtained in the seeds collected in 2019 (100%), while 2 years to 3 years of storage was found to drastically reduce seed viability. The results of the analysis revealed a value of X2 = 220.25, and p < 0.05, indicating statistically significant differences between the years of collection. The 2018 sample presented intermediate seed viability values with an average of 55% + 3.2%, while the percentage of viability for the 2017 and 2016 samples was zero.

Seed germination

Significant differences in germination over time between the results obtained for 2018 and 2019 (T0.05(2),28; =116) were found. In all categories, the germination observed for the 2019 sample surpassed the germination of seeds stored for a year (44.5% - 71.5% respectively) (Table 1).

Table 1 Wilcoxon signed-rank test based on the differences in germination performance over time (di). 

2018 2019 di Hierarchy of |di| Signed hierarchy of |di|
0 0 0 1 +1
5 66.5 -61.5 12 -12
15 81 -66 13 -13
25.5 95 -69.5 14 -14
25.5 97 -71.5 15 -15
25.5 97 -71.5 15 -15
40 98 -58 11 -11
41.5 98.5 -57 10 -10
43.5 98.5 -55 9 -9
47 98.5 -51.5 8 -8
48.5 98.5 -50 7 -7
49 98.5 -49.5 6 -6
52 98.5 -46.5 5 -5
52.5 98.5 -46 4 -4
52.5 98.5 -46 4 -4
52.5 98.5 -46 4 -4
52.5 98.5 -46 4 -4
53.5 98.5 -45 3 -3
53.5 98.5 -45 3 -3
54 98.5 -44.5 2 -2
54 98.5 -44.5 2 -2
54 98.5 -44.5 2 -2
54 98.5 -44.5 2 -2
54 98.5 -44.5 2 -2
54 98.5 -44.5 2 -2
54 98.5 -44.5 2 -2
54 98.5 -44.5 2 -2
54 98.5 -44.5 2 -2
54 98.5 -44.5 2 -2
54 98.5 -44.5 2 -2
T+=1 T- =29 T=28

Significant differences are based on the probability of T0.05(2),28; =116.

Germination: 2018 vs 2019

Significant differences in germination were found for both years. The 2019 seeds germinated in a shorter time and showed a higher germination percentage than the 2018 seeds (66.5% ± 0.76% vs 5% ± 0.21%, respectively) in the first two days of the experiment (Fig. 3). The maximum germination percentage also differed significantly between both years (F(19,360) = 41. 919; p ≤ 0.05), with the 2019 sample reaching 98.5% ± 3.43% in eight days, while the 2018 sample reached maximum germination, 54% ± 2.84%, in 20 days. The residual difference (SCRR 2018= 16.435, SCRR 2019= 0.868, SCRNR= 17.303; F(2,102) = 204; p < 0.01) indicate significant differences in accumulated germination between the seeds collected in 2018 and 2019, with the latter presenting rapid germination, in contrast to the former (Fig. 4).

Figure 3 Comparison of the daily percentage of Haematoxylum campechianum seed germination from 2018 to 2019. 

The difference between models concurs with the comparison undertaken via the Chow test.

Figure 4 Adjusted models for the germination of Haematoxylum campechianum seeds for 2018 and 2019. 

Discussion

The seed viability and germination of H. campechianum were affected by storage time, with our results showing that the seeds collected in 2019 displayed higher viability and germination percentages than those collected in 2018 while viability and germination were null for the 2016 and 2017 samples.

The morphometric attributes of seeds, such as size, fresh weight, and biomass are important to the germination process, as they influence seedling development (Rojas-Aréchiga et al., 2013). In this sense, in some species of the family Fabaceae, seeds with greater biomass present differential responses in germination (Huyghe, 1993; Lobos, Miranda, & Mera,2008), although they also have reater commercial value (Lobos et al., 2008); however, few seed morphometry studies have been conducted on this plant family.

Pérez (2014), found differences in several attributes, including mass and germination, in the seeds of wild species of the genus Lupinus (L. campestris, L. exaltatus, L. hintonii, and L. montanus) collected in 2011 and 2012. He documented that these four species presented intraspecific variations in seed weight (L. hintonii =35.51 g ± 0.087 g, L. montanus = 1.8 g ± 0.002 g, L. campestris = 1.6 g ± 0.002 g, and L. exaltatus = 1.33 g ± 0.014 g) and germination (with and without mechanical scarification), which was higher in treated seeds (90%).

Ecologically, all seeds differing in their desiccation tolerance (Farrant et al., 1993; De Oliveria-Gentil, 2001); thus, seeds can be classified into orthodox, recalcitrant, and intermediate (Roberts, 1973; Pritchard, 2004). Desiccation tolerance in seeds of species in the Fabaceae family has also been little researched. Giamminola, Morandini, and de Viana, (2012), did not find significant differences in the germination of Prosopis nigra Hieron., with a storage time of three months applied prior to scarification. The seeds of this species were germinated 90% and presented a shorter germination time (4.8 days) and a higher moisture content (CH = 10% - 12%) than desiccated seeds (CH = 3% - 5%), which germinated at a level of 80%, results which indicate that the seeds of P. nigra are orthodox. Galíndez et al. (2015), identified the presence of physical dormancy and the effect of storage on two subtropical species of Fabaceae, Amburana cearensis (Allemao) A.C. Sm and Myroxylon peruiferum Lf. seeds, using different scarification methods. They found that the A. cearensis seeds stored at -18 °C ± 2 °C for three and 12 months were orthodox, while the M. peruiferum seeds were sensitive to desiccation and storage at -18ºC.

Furthermore, Morandini, Giamminola, and de Viana (2013), determined both desiccation tolerance and germination in Prosopis ferox Griseb and Pterogyne nitens Tul., subjecting the seeds to mechanical scarification and storing them for six months at -20 °C and at CH = 10% - 12% and 3% - 5%, respectively. Their results show that máximum germination occurred in seeds with a lower 3% - 5%, and that the effect of storage for six months at -20 °C did not influence germination; therefore, seeds of both species are classified as orthodox, given that the germination level was over 80% when CH was reduced to 3% - 5% and after storage for six months at -20 °C.

The findings found here are contrary to most results documented above. This is due to the fact that the studies described indicates that the majority of the Fabaceae species studied showed different strategies for increasing their perpetuation potential over time, despite being subject to adverse environmental conditions, as is the case with the induction of dormancy. Although the moisture content of the H. campechianum seeds was not evaluated due to poor seed availability over the years of collection, it is assumed that this was high in the collection years, given that H. campechianum trees in the YP are normally distributed in lowland areas (tíntales) characterized by a high-water content in the soil (Niembro, 2002; Plasencia-Vázquez et al., 2017), and that moisture content reduced as storage time increased; however, this hypothesis should be tested in future research.

The results obtained in the present study indicate that the H. campechianum seeds could be considered as recalcitrant due to the high germination percentage in recently harvested seeds in 2019 and an accelerated ageing process, which was characterized by a low viability and germination rate in seeds stored in previous years. Based only in germination data during one collected year, Zamora-Cornelio et al. (2010), suggested that the H. campechianum seeds were recalcitrant because both a high and speed germination (86%). Our research is novel and incorporates variations in the fresh weight, biochemical viability tests as well as germination essays under a multi-year stored approach of the H. campechianum seeds and support the assumption proposed by Zamora-Cornelio et al. (2010).

In the case of this study, it was found that independent of the year of collection, the seeds presented an inverse relationship between seed fresh weight and both viability and germination. The fresh weight results are contrary to those previously reported for some Fabaceae species (Huyghe, 1993; Lobos et al., 2008) and show the great variability of morphometric and physiological attributes in these species. Moreover, seeds of this family show a great range of ecophysiological, genetic, and micro-environmental adaptations which enable them to establish themselves in most of the ecosystems worldwide (Langer & Hill, 1991).

A possible explanation for the greater percentage fresh weight found in H. campechianum seeds subject to a longer storage time may be related to the increased number of toxic radicals at a cellular level, such as reactive oxygen species (ROS). They consist in free radicals (O2●-, superoxide anion radical; OH●, hydroxyl radical; HO2●, perhydroxy radical and RO●, alkoxy radicals) and non-radical (molecular) forms (H2O2, hydrogen peroxide and 1O2, singlet oxygen (Halliwell, 1987; Huang, Ullah, Zhou, Yi, & Zhao, 2019). ROS are produced naturally during cellular metabolism in different parts of the plant cell (Huang et al., 2019). In seeds, during the first stages of germination, the principal sources for the generation of ROS are mitochondria, peroxisomes, and cell membranes. Considering that, in most cases, the first stages of germination occur in darkness, chloroplasts do not contribute to ROS generation (Huang et al., 2019); however, once the seedling is produced, it will begin to form chloroplasts, which are also a source of ROS.

According to the oxidative window model proposed by Bailly, El-Maarouf-Bouteau, and Corbineau (2008), an adequate and optimal ROS level is required for germination to occur. Therefore, very high ROS levels, for example in seeds that have aged due to prolonged storage periods or those subject to high temperatures, would cause damage at an embryo level and prevent said seeds from germinating (Bailly et al., 2008). It is possible that the higher percentage of fresh weight in older H. campechianum seeds documented in the present study is related to a potentially higher ROS level, and that this caused structural damage to the embryos and consequently, negatively affected the viability and germination in stored seeds of this species. However, more research is required to support this hypothesis.

Given the current high deforestation rate from anthropogenic activities documented in the YP (Rueda, 2010), the present study seeks to promote the use and sustainable exploitation of H. campechianum within its natural area of distribution and contributing to the creation of effective conservation and restoration strategies as well as biotechnological purposes. Moreover, it could be the key to a paradigm shift about the exploitation of natural resources, not only of this species but also any other timber and non-timber resources in the state of Campeche and the YP. Future research on H. campechianum may be focused on evaluating different seed storage mechanisms considering variations in germination between a same year of collection in order to maximize the propagation both in vitro and ex situ of its natural populations; in addition, include other variables such as length, thickness, colour, number of seeds per pod and/or tree among others. It may also seek to analyze the effect of various environmental factors, such as drought, thermal tolerance thresholds, magnetism, photoblastism, salinity and dynamic of the ROS in different organelles of plant, on germination and seedlings establishment under both laboratory and field conditions. Future studies may also explore the capacity of H. campechianum as a soil restorer, evaluating its potential as a nitrogen fixer in the soil, which is typical of many Fabaceae species. This would require long-term research in the field, evaluating the regeneration cycle and reproductive characteristics of the natural populations of this species, the production and dispersal of seeds, dynamic of the seed bank in the soil as well as the establishment, survival, and performance of seedlings and young individuals.

Conclusions

The viability and germination of H. campechianum seeds were observed to be affected by storage time. The recently harvested seeds presented a higher viability and germination percentage than older seeds. As the findings of the present study indicate an accelerated ageing process in this species, it could be considered recalcitrant. The present research is the first long-term seed ecology study of H. campechianum, presenting an evaluation of the seed germination dynamics and delineating preliminarily the thresholds desiccation tolerance in H. campechianum, a charismatic and key forest species with high sociocultural value to the state of Campeche and the YP, Mexico.

Acknowledgments

We thank Juan Carlos García and PLANALTO S.P.R de R.I. (Sociedad de Producción Rural de Responsabilidad Ilimitada; Rural Production Society of Unlimited Responsibility) for its technical support to harvest seeds in field and Ana Che Tun for its support to laboratory work. In addition, we thank Jessica Cruz Hernández and National Laboratory of Climatic Variability Remote Sensing and Evaluation of Agricultural Risks of Autonomous University of San Luis Potosí (VARICLIM-UASLP) for its assistance in generating the map of the study area. This research was jointly supported by the Secretaría de Educación Pública (Ministry of Public Education) Programa de Mejoramiento del Profesorado (Program for the Improvement of Higher Education Teachers) [project: Germinación de semillas de Haematoxylum campechianum (Leguminosae) bajo condiciones de estrés hídrico inducido; No. 511-6/18-8491] and the Cátedra-Conacyt (Cátedra del Consejo Nacional de Ciencia y Tecnología) project “Adaptación al Cambio Climático en la Producción Agopecuaria y Forestal en la Frontera Sur” (No. 2179).

References

Aragón-Gastélum, JL., Flores, J., Jurado, E., Ramírez-Tobías, HM., Robles-Díaz, E., Rodas-Ortiz, JP., & Yáñez-Espinosa, L. (2018). Potential impact of global warming on seed bank, dormancy and germination of three succulent species from the Chihuahuan Desert. Seed Science Research, 28(4), 312-318. doi: 10.1017/S0960258518000302 [ Links ]

Avwioro, G. (2011). Histochemical uses of Haematoxylin: A review. Journal of Physical Chemistry Solids, 1(5), 24-34. [ Links ]

Bailly, C., El-Maarouf-Bouteau, H., & Corbineau, F. (2008). From intracellular signaling networks to cell death: the dual role of reactive oxygen species in seed physiology. Comptes Rendus Biologies, 331(10), 806-814. doi: 10.1016/j.crvi.2008.07.022 [ Links ]

Baskin, C. C., & Baskin, J. M. (2014). Seeds: ecology, biogeography, and evolution of dormancy and germination. San Diego, United States: Academic Press. [ Links ]

Chablé-Vega, MA., Plasencia-Vázquez, AH., García-González, A., Ferrer-Sánchez, Y., Riverón-Giró, F.B., & Zamora-Crescencio, P. (2019). Distribución, densidad y estructura dasométrica de Haematoxylum campechianum y Haematoxylum calakmulense en Campeche, México. Ecosistemas y Recursos Agropecuarios, 6(16), 65-77. doi: 10.19136/era.a6n16.1784 [ Links ]

Centro de Investigación Científica de Yucatán [CICY]. (2010). Flora digital: Península de Yucatán. Herbario CICY. Recuperado de https://www.cicy.mx/sitios/flora%20digital/ficha_virtual.php?especie=1463Links ]

Contreras, A. C. (2010). Biodiversidad perdida: el caso de los colorantes. In R. Durán, & M. Méndez (Eds.), Biodiversidad y desarrollo humano en Yucatán (pp. 368-372). Mérida, Yucatán México: CICY, PPD-FMAM, Conabio, Seduma. [ Links ]

Comisión Nacional del Agua [Conagua] (2010). Base de datos mensuales climatológicos correspondientes a la estación de Campeche. Dirección Local Campeche, residencia técnica. Campeche, México. [ Links ]

Durán R., C., & Sousa, M. (2014). Haematoxylum calakmulense (Leguminosae, Caesalpinoideae), una nueva especie Mesoamericana. Novon: A Journal for Botanical Nomenclature, 23(1), 31-36. doi: 10.3417/2011106 [ Links ]

Dampier, W. (2004). Dos viajes a Campeche (García Bergua A, Trans). CDMX, México: MA Porrúa. [ Links ]

Daniel, W. W., & Cross, C. L. (2018). Biostatistics: a foundation for analysis in the health sciences (11th ed). Hoboken, United States: John Wiley & Sons. [ Links ]

De Oliveira-Gentil, D. F. (2001). Conservação de sementes do cafeeiro: resultados discordantes ou complementares. Bragantia, 60, 149-154. doi: 10.1590/S0006-87052001000300001 [ Links ]

Duke, J. A. (2008). Duke’s handbook of medicinal plants of Latin America. Boca Raton, United States: CRC Press. [ Links ]

Ellis, RH., & Hong, T. D. (2007). Seed longevity - moisture content relationships in hermetic and open storage. Seed Science and Technology, 35(2), 423-431. doi: 10.15258/sst.2007.35.2.17 [ Links ]

Farrant, J.M., Pammenter, N.W., & Berjak, P. (1993). Seed development in relation to desiccation tolerance: a comparison between desiccation sensitive (recalcitrant) seeds of Avicennia marina and desiccation tolerant types. Seed Science Research , 3(1), 1-13. doi: 10.1017/S0960258500001513 [ Links ]

Fernández Carnevali, G.C., Tapia Muñoz, J.L., Duno de Stefano, R., Ramírez Morillo, I.M., Can-Itzá, L., Hernández Aguilar, S., & Castillo, A. (2012). La Flora de la Península de Yucatán Mexicana: 250 años de conocimiento florístico. Biodiversitas, 101, 6-10. [ Links ]

Galíndez, G., Malagrina, G., Ceccato, D., Ledesma, T., Lindow-López, L.T., & Ortega Baes, F. P. (2015). Dormición física y conservación ex situ de semillas de Amburana cearensis y Myroxylon peruiferum (Fabaceae). Boletín de la Sociedad Argentina de Botánica, 50(2), 153-161. doi: 10.31055/1851.2372.v50.n2.11660 [ Links ]

Giamminola, E. M., Morandini, M. N., & de Viana, M. L. (2012). Respuesta a la desecación ya la temperatura de almacenamiento del germoplasma de Prosopis nigra (Grisebach) Hieron. y Ziziphus mistol Griseb. Gest. Ambiente, 15(1), 19-26. [ Links ]

Gujarati, D. N., & Porter, D. C. (2009). Basic Econometrics (5th ed.). New York, United States: McGraw-Hill/Irwin. [ Links ]

Halliwell, B. (1987). Oxidants and human disease: some new concepts. The FASEB Journal, 1(5), 358-364. doi: 10.1096/fasebj.1.5.2824268 [ Links ]

Hill, T., & Lewicki, P. (2006). Statistics: methods and applications. Tulsa, United States: StatSoft. [ Links ]

Huang, H., Ullah, F., Zhou, D. X., Yi, M., & Zhao, Y. (2019). Mechanisms of ROS regulation of plant development and stress responses. Frontiers in Plant Science, 10, 800. doi: 10.3389/fpls.2019.00800 [ Links ]

Huyghe, C. (1993). Growth of white lupin seedlings during the rosette stage as affected by seed size. Agronomie, 13(2), 145-153. [ Links ]

Khurana, E., & Singh, J. S. (2001). Ecology of seed and seedling growth for conservation and restoration of tropical dry forest: a review. Environmental Conservation, 28(1), 39-52. doi: 10.1017/S0376892901000042 [ Links ]

Langer, R., & Hill, G. (1991). Fabaceae. In Agricultural Plants (pp. 217-282). Cambridge: Cambridge University Press. doi: 10.1017/CBO9781139170284.013 [ Links ]

Lobos, J., Miranda, H., & Mera, M. (2008). Weight and volume gain by hydrated grains of bitter albus lupins grown in Chile. In J. A. Palta, & J. B. Berger (Eds.), Lupins for health and wealth. International Lupin Association (pp. 105-107). Canterbury, New Zealand. [ Links ]

Loza-Cornejo, S., López-Mata, L., & Terrazas, T. (2008). Morphological seed traits and germination of six species of Pachycereeae (Cactaceae). Journal of the Professional Association for Cactus Development, 10, 71-84. [ Links ]

McKellar, R. C., & Lu, X. (2004). Modeling microbial responses in foods. Boca Raton, United States: CRC. [ Links ]

Morandini, N. M., Giamminola, E. M., & de Viana, M. L. (2013). Tolerancia a la desecación de semillas de Prosopis ferox y Pterogyne nitens (Fabaceae). Revista de Biología Tropical, 61(1), 335-342. [ Links ]

Morrone, J. J. (2005). Toward a synthesis of Mexican biogeography. Revista Mexicana de Biodoversidad, 76(2), 207-252. [ Links ]

Niembro, A. (2002). Haematoxylum campechianum L. In J. A. Vozzo (Ed.), Tropical tree seed manual, Part 2 Species Descriptions (pp. 497-499). Washington DC: USDA Forest Service. [ Links ]

Nobel, P. S. (2011). Sabiduría del desierto, agaves y cactos: CO2, agua, cambio climático/Desert wisdom/agaves and cacti (No. 625.9525 N664s Ej. 1 024989). Biblioteca Básica de Agricultura. [ Links ]

Norton, S. A. (1996). The useful plants of dermatology. II. Haematoxylum and hematoxylin. Journal of the American Academy of Dermatology, 34(1), 149-151. doi: 10.1016/S0190-9622(96)90867-1 [ Links ]

Peng, T., Wu, J.R., Tong, L.J., Li, M.Y., Chen, F., Leng, Y.X., Qu, R., Han, K., Su, Y., Chen, Y., Duan, W.H., Xie, H., & Ding, J. (2014). Identification of DW532 as a novel anti-tumor agent targeting both kinases and tubulin. Acta Pharmacologica Sinica, 35(7), 916-928. doi: 10.1038/aps.2014.33 [ Links ]

Pérez, I. (2014). Tolerancia y capacidad de fitorremediación de árboles nativos tropicales a suelo contaminado con petróleo. Tesis de Doctorado, El Colegio de la Frontera Sur. Villahermosa, Tabasco, México. [ Links ]

Peters, J. (2000). Tetrazolium Testing Handbook. Las Cruces, United States: Association of Official Seed Analysts. [ Links ]

Plasencia-Vázquez, A. H., Villegas, P., Ferrer-Sánchez, Y., & Zamora-Crescencio, P. (2017). Historical distribution of species of the genus Haematoxylum (Leguminosae) in the Yucatan Peninsula, Mexico, based on herbarium specimens. Acta Botánica Mexicana, 119, 51-68. doi: 10.21829/abm119.2017.1231 [ Links ]

Pritchard, H. W. (2004). Classification of seed storage types for ex situ conservation in relation to temperature and moisture. In E. O. Guerrant, K. Havens, & M. Maunder, (Eds.), Ex situ plant conservation: supporting species survival in the wild (pp. 139-161). Washington, United States: Island Press. [ Links ]

Quezada-Euán, J. J. G., May-Itzá, W. D. J., & González-Acereto, J. A. (2001). Meliponiculture in Mexico: problems and perspective for development. Bee World, 82(4), 160-167. doi: 10.1080/0005772X.2001.11099523 [ Links ]

Rangel Fajardo, M., Córdova-Téllez, L., López Andrade, A. P., Delgado Alvarado, A., Zavaleta Mancera, H. A., & Villegas Monter, A. (2011). Desiccation tolerance in seeds from three genetic origins of cocoa (Theobroma cacao L.). Revista Fitotecnia Mexicana, 34(3), 175-182. [ Links ]

Roberts, E. H. (1973). Predicting the storage life of seeds. Seed Science and Technology , 1, 499-514. [ Links ]

Rojas-Aréchiga, M., Mandujano, M. C., & Golubov, J. K. (2013). Seed size and photoblastism in species belonging to tribe Cacteae (Cactaceae). Journal of Plant Research, 126(3), 373-386. doi: 10.1007/s10265-012-0526-2 [ Links ]

Rueda, X. (2010). Understanding deforestation in the southern Yucatán: insights from a sub-regional, multi-temporal analysis. Regional Environmental Change, 10(3), 175-189. doi: 10.1007/s10113-010-0115-7 [ Links ]

Sánchez-Rendón, J. A., Pernús-Álvarez, M., Torres-Arias, Y., Barrios, D., & Dupuig, D. (2019). Dormancy and germination in tree and shrub seeds of Cuba: implications for ecological restoration. Acta Botánica Cubana, 218, 77-108. [ Links ]

Servicio Meteorológico Nacional [SMN]. (2020). Normales climatológicas por estado. Recuperado de https://smn.conagua.gob.mx/es/climatologia/informacion-climatologica/normales-climatologicas-por-estadoLinks ]

Thompson, K. (2000). The functional ecology of soil seed banks. In M. Fenner (Ed.), Seeds, the ecology of regeneration in plant communities (2nd ed.) (pp 215-235). London, United Kingdom: CABI Publishing. [ Links ]

Tweddle, J. C., Dickie, J. B., Baskin, C. C., & Baskin, J. M. (2003). Ecological aspects of seed desiccation sensitivity. Journal of Ecology, 91(2), 294-304. doi: 10.1046/j.1365-2745.2003.00760.x [ Links ]

Villegas, P., & Torras, R. (2014). The extraction and exportation of Campeche wood by foreign colonists: the case of B. Anizan and Cía. Secuencia, 90, 79-93. [ Links ]

Wang, J. H., Baskin, C. C., Cui, X. L., & Du, G. Z. (2009). Effect of phylogeny, life history and habitat correlates on seed germination of 69 arid and semiarid zone species from northwest China. Evolutionary Ecology, 23(6), 827-846. doi: 10.1007/s10682-008-9273-1 [ Links ]

Wyse, S. V., & Dickie, J. B. (2017). Predicting the global incidence of seed desiccation sensitivity. Journal of Ecology , 105(4), 1082-1093. doi: 10.1111/1365-2745.12725 [ Links ]

Zamora-Cornelio, L. F. (2010). Evaluación espacio-temporal del crecimiento de plántulas con potencial para la restauración de humedales. Tesis de Maestría. El Colegio de la Frontera Sur. Villahermosa, Tabasco, México. [ Links ]

Zamora-Cornelio, L. F., Ochoa-Gaona, S., Vargas Simón, G., Castellanos Albores, J., & de Jong, B. H. J. (2010). Germinación de semillas y clave para la identificación de plántulas de seis especies arbóreas nativas de humedales del sureste de México. Revista de Biología Tropical, 58(2), 717-732. [ Links ]

Received: September 17, 2020; Accepted: May 15, 2021; Published: December 30, 2021

*Corresponding author. jlaragon@uacam.mx

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