SciELO - Scientific Electronic Library Online

 
vol.24 issue3Qualitative study of perceptions on poverty and present status of assets in a mayan community in the Yucatan PeninsulaDirect in vitro regeneration of the chrysanthemum, Dendranthema X grandiflorum Kitam, from stem segments author indexsubject indexsearch form
Home Pagealphabetic serial listing  

Services on Demand

Journal

Article

Indicators

Related links

  • Have no similar articlesSimilars in SciELO

Share


Universidad y ciencia

Print version ISSN 0186-2979

Universidad y ciencia vol.24 n.3 Villahermosa Dec. 2008

 

Artículos

 

Development of a model for in vitro culture of Vallisneria americana Michx.

 

Desarrollo de un modelo de cultivo in vitro para Vallisneria americana Michx.

 

V Ruiz–Carrera1* y AJ Sánchez1

 

1 Diagnóstico y Manejo de Humedales Tropicales. División Académica de Ciencias Biológicas. Universidad Juárez Autónoma de Tabasco. km 0.5 carretera Villahermosa–Cárdenas. Villahermosa, Tabasco 86150, México. (VRC) (AJS) *Correo electrónico: violeta@cicea.ujat.mx

 

Recibido: 2 de septiembre de 2008
Aceptado: 6 de octubre de 2008

 

ABSTRACT

An exploratory experimental design was developed to establish a model for Vallisneria americana Michx. following conventional in vitro culture procedures for aquatic vegetation. The design included five experiments with stages of presterilization or washing with 0.1 % Tween 20®, sterilization with NaClO and poststerilization of explants (leaf base, rhizome, caulinar apex and seeds), and culture in monophasic or biphasic nutrient media. Leaves and rhizomes were sterilized with 0.3 and 0.6% NaClO, and contact times of 2.5 and 5 min. Both explants cultured in gellified monophasic White medium with 58.4 mM sacarose and a pH of 7.5 presented on average a 60% contamination by translucid lipidic exudates, followed by darkening. The presterilization of leaves and rhizomes caused the production of exudates, and the addition of 0.01 % ascorbic acid to the nutrient medium caused its inhibition. Comparing the White medium with the 0.5 MS medium, both with 0.88 x 10–3 mM of bencyladenine, asepsia of explants was improved in White and leaf pigmentation was significantly favored in 0.5 MS, although no explant presented regeneration. Presterilization was omitted in the experiments with caulinar apices and seeds, and sterilization was carried out with 0.6 % NaClO for 15 min. The monophasic culture of caulinar apices in liquid 0.5 MS with doses from 0.0 to 8.88 x 10–3 mM of bencyladenine regenerated leaves but resulted in excessive contamination and death. In contrast, both the non–aseptic control and the in vitro seedlings in biphasic culture were 100% aseptic in 0.5 MS, White and semi–hard sterile local water. However, the White medium produced lower quality seedlings. The biphasic germination in aqueous medium with local water and gellified support was selected considering its lower cost and germination efficiency.

Key words: Aseptic culture, viable explant, biphasic germination, Vallisneria americana, wild celery.

 

RESUMEN

Con procedimientos convencionales de cultivo in vitro efectuados en vegetación acuática se desarrolló un diseño experimental exploratorio para establecer un modelo de cultivo para Vallisneria americana Michx. El diseño incluyó cinco experimentos con etapas de preesterilización o lavados de 0.1% de Tween 20®, esterilización con NaClO y postesterilización de explantes (base de hoja, rizoma, ápice caulinar y semillas), así como su cultivo en medio nutritivo monofásico o bifásico. Las hojas y rizomas fueron esterilizados con 0.3 y 0.6% de NaClO y tiempos de contacto de 2.5 y 5 min. Ambos explantes cultivados en medio monofásico gelificado de White con 58.4 mM de sacarosa y pH de 7.5 presentaron en promedio 60% de contaminación por exudados translúcidos lípidicos que después obscurecieron al explante. La preesterilización de la hoja y rizoma causó la producción del exudado y la adición de 0.01 % de ácido ascórbico al medio nutritivo causó su inhibición. Cuando se compararon los medios monofásicos de White y 0.5 MS, ambos con 0.88 x 10–3 mM de benciladenina, la asepsia de los explantes fue mejorada en White y la pigmentación foliar fue significativamente favorecida en 0.5 MS, pero ningún explante presentó regeneración. La preesterilización fue omitida en los experimentos con ápices caulinares y semillas y la esterilización se realizó con 0.6% de NaClO por 15 min. El cultivo monofásico de ápices caulinares en 0.5 MS líquido con dosis desde 0.0 hasta 8.88 x 10–3 mM de benciladenina regeneró hojas pero hubo excesiva contaminación y murieron. En cambio, los germinados en el control no aséptico y en el cultivo in vitro, ambos en cultivo bifásico, fueron 100% asépticos en 0.5 MS, White y agua local estéril semidura. Sin embargo, el medio White produjo menor calidad de germinados. La germinación bifásica con medio acuoso de agua local y soporte gelificado fue seleccionada por su menor costo y eficiencia germinativa.

Palabras clave: Cultivo aséptico, explante viable, germinación bifásica, Vallisneria americana, cintilla.

 

INTRODUCTION

Submerged rooted angiosperms are highly productive and are important in providing substrate and services in aquatic ecosystems (Hemminga & Duarte 2000; Hobbs & Harris 2001; Short et al. 2006; Best et al. 2008). The loss or decrease of this vegetation in coastal areas are related to natural and anthropogenic variations in flood cycles, organic loads, water quality and loss of emergent rooted macrophytes (Mackay et al. 2003; Mony et al. 2007; Best et al. 2008), all of which affect hydro–logical dynamics and productivity, biodiversity and the abundance of associated flora and fauna and, in consequence, the optimum use of natural resources, including water resources (Hemminga & Duarte 2000).

The decline in submerged aquatic vegetation has reached 60 % in the last 20 to 30 years in some altered environments (Rybicki & Carter 1986; Rybicki et al. 2001). The decrease in the abundance and natural regeneration of seed banks is also considered important (Westcott et al. 1997; Ke & Li 2006). Meso and microcosm in situ studies have been carried out to evaluate the factors that change submerged vegetation populations (Twilley & Barko 1990; Touchette & Boulkoldher 2002), where the availability of enough organisms and the elimination of epiphytes has been fundamental in obtaining good experimental results. Also, the system of in vitro plant culture is useful for evaluations as it excludes the macro and microbiota that is associated with the plants, and it has the capacity to maintain a permanent supply of high quality material for research (Moffler & Durako 1984; Ailstock et al. 1991; Li & Gallagher 1996; Kane & Philman 1997).

The aseptic reproduction of aquatic plants has been carried out heterotrophically in nutrient media with different phytoregulators. Diverse plant structures such as tissue fragments, organs and seeds cultivated in specific nutrient media have generated seedlings from which in vitro clones may be obtained (Kane & Gilman 1991; Kane & Philman 1997; Jenks et al. 2000, Kane et al. 2002; Zhou et al. 2006).

In vitro plants have been used to identify abiotic stress as their greater flexibility favors the design of experiments, lower analyses costs and independence from natural temporal variations (Hall et al. 1997; Mohan & Hosetti 1999; McCann et al. 2000; Murphy et al. 2003). Several ecologically important submerged species such as the sea–grasses Halophila decipiens (Bird et al. 1998), Posidonia oceanica (Balestri & Bertini 2003), Ruppia maritima (Murphy et al. 2003) and Cymodocea nodosa (García–Jiménez et al. 2006), as well as the freshwater grass Potamogeton pectinatus (Ailstock et al. 1991; Hall et al. 1997; Zhou et al. 2006), have been cultivated in vitro with this in mind. However, Vallisneria ssp. has been studied little (Uma & Mohan–Ram 1972) under this point of view. In vitro propagation of this species is required to maintain and re–populate populations that have been reported in drastic reduction and those in ecosystems where it is disappearing (Xiong & Li 2002; Sánchez et al. 2007). A permanent supply of plant matter of this macrophyte is needed to experimentally prove the hypotheses generated with respect to the environmental variations and the interactions with other species that are resulting in its declination or disappearance, as well as to sustain programmes to re–populate and restore altered ecosystems where biodiversity has been negatively impacted. Examples of research results include those of Wigand & Stevenson (1994, 1997), Wigand et al. (2000), Kurtz et al. (2003), Genkai–Kato (2007) and Mony etal. (2007).

The Reserva de la Biosfera Pantanos de Centla in one of the greatest wetlands in Mesoamerica, and it harbours the aquatic vascular flora that is representative of this region (Guadarrama & Ortiz–Gil 2000). The dominant species of rooted aquatic vegetation in this wetland, Vallisneria americana Michx., has been reported with a wide variety of values of density, biomass, surface area of beds and distribution (Sánchez et al. 2007). However, the causes of its spatial–temporal changes and their effects in Pantanos de Centla have not been evaluated, in spite of it harbouring a high biodiversity of associated fauna (Rozas & Minello 2006; Sánchez et al. 2007) and providing ecological services similar to those of other species of submerged aquatic vegetation in estuarine ecosystems (Short et al. 2006; Genkai–Kato 2007; Best et al. 2008). The in vitro culture model for submerged aquatic vegetation under these conservation conditions is basic for the development of environmental stress bioas–says and of restoration programmes for impacted ecosystems, as is the case of the Reserva de la Biosfera Pantanos de Centla. The purpose of this study was to prove the feasibility of cultivating vegetative explants and seeds of V. americana in vitro, by reproducing the conventional procedures used for this species and other species of aquatic vegetation. The experiments focused on evaluating the asepsia and viability of explants, and inducing regeneration to micropropagate healthy plants.

 

MATERIALS AND METHODS

Focal species

Vallisneria americana (Hydrocharitaceae) is a submerged, perennial, dioic and rooted hydrophyte that is distributed from North America to Central America (Korschgen & Green 1988; Ellison 2004). The number and density of vegetation beds in the Reserva de la Biosfera Pantanos de Centla (RBPC) (17° 57' 53"–18° 39' 03" N – 92° 06' 39" –92° 47' 58" W) have recorded a marked seasonal variation and have tended to decline or disappear (Sánchez et al. 2007). Populations of this species are monospecific and produce a maximum of flowers and fruits during the low–flood cycle that occurs from May to August (Jiménez 2003). This species presents rosette leaves on a short vertical stem (orthotropic rhizome or caulinar apex) that produces roots and rhizomes with stolons (plagiotropic rhizome). The leaves are strap–like and reach lengths of 50 cm or greater in relation to the local level of flooding (Jiménez 2003). The reproduction of V. americana is predominantly vegetative through the stoloniferous rhizome that grows horizontally and develops shoots (ramets). The reproductive ramets fall to the ground and act like turions or dormant buds (Sculthorpe et al. 1967).

Sampling

Vallisneria americana plants were collected in Laguna de San Pedrito, in the RBPC (54° 25' 50" N – 20° 30' 63.2" W), during the minimum flooding season of 2004. It has recorded its greatest biomass averages in this lagoon (Jiménez 2003) at a maximum salinity of 4 psu (4450 μS cm–2) and a pH of 7.8 (Sánchez et al. 2007). Collection of ramets was done manually and they were washed in situ to remove sediment from the roots. Mature fruit was collected the following year. They were recognized by their size, brown color and withering of the pistilate stem. The plant samples were transported in lagoon water at ambient temperature. The V. americana seeds were extracted by dissecting the surface of the fruit lengthwise with a scalpel and were preserved, together with their mucilage, in refrigeration (12 ± 2 °C) for a maximum of three months with periodic changes of water every 15 days.

Handling of plants in aquaria

Plants without damaged leaves were transplanted into glass aquaria (40 L) in a polycarbonate greenhouse. Fifteen ramets were cultivated in the aquaria on a substrate of 10 cm of pre–washed and dried sand and a 30 cm aerated water column. The aqueous medium was renovated every 15 – 20 days throughout an adaptation period of three months. During this time, the greenhouse maintained an average ambient temperature of 29.5 °C and an average relative humidity of 57% (Thermo–Hygro® Control Company). The aquaria with V. americana received a light intensity of 61 to 360 /mol photons m–2 s–1 (Light Meter® Extech Instruments), the water temperature varied between 25 and 30 °C and the pH varied from 8 to 8.8 (pHmeter 240 Corning®). These parameters were monitored two or three times per week between 11 and 13 h. The V. americana ramets produced in the laboratory were placed in transparent polyethylene aquaria with 1 L of White medium (White 1963) at a pH of 7.5. The ratio of water column to sand layer was 3:1 cm. The culture medium was renovated every 15 days to avoid overgrowth of epiphytes. The cultures remained in a laboratory with controlled temperature (25 ± 5 °C), shade, and natural light and photoperiod. The new ramets were used for the first in vitro experiments.

General conditions of in vitro culture

The leaf, plagiotropic rhizome and orthotropic rhizome without roots were extracted whole and washed with running water for 10 min. The corresponding explants were dissected with a scalpel and cultivated according to the experimental set.

The in vitro culture technique of the ex–plants included the phases of presterilization, sterilization, poststerilization and planting in a culture medium (Torres 1989). Presterilization included washing with Tween 20® for 15 min at 250 rpm. Sterilization or chemical disinfecting was carried out with diluted solutions of Cloralex® (6% NaClO) at 250 rpm. Poststerilization included three to five rinsings with sterile water to wash and eliminate the NaClO remaining on the explants. The phases of the procedure and the culture media were modified or omitted in regard to the objectives and hypotheses of each experiment, to insure the most adequate conditions of asepsia and viability for the seeds and vegetative structures.

The culture media used in the experiments were White (1963) with 700 μS cm–2 and a pH of 6 or 7.5, and Murashige & Skoog (1962) at half ionic strength (0.5 MS) with 3000 μS cm–2 and a pH of 6. Both media were used in some experiments. All media were enriched with vitamins and 58.4 or 29.2 mM sucrose.

The monophasic culture was prepared in liquid form or with a gellified support (0.6% of bacteriological agar) in glass jars (5 cm diameter and 7 cm height). The volume of dosified culture medium was 20 ml. The biphasic cultures were prepared in two receptacles: 1) test tubes with 3 ml of aqueous medium on a support of 15 glass pearls and 2) jars (5 cm diameter and 9 cm height) with 100 ml of aqueous phase on a 20 ml gellified support. The tubes were covered with reinforced aluminum paper and the culture jars with polycarbonate lids (Magenta®). Sterilization of the culture units with nutrient medium was carried out in an autoclave at 121 °C and 104 kPa.

The cultures with explants remained at 25 ± 5°C under 20 /mol photons m–2 s–1 for 16 h light:8 h night. Diffuse light equivalent to 1 /mol photons m–2 s–1 was used to germinate the seeds.

Experiments with leaves and rhizomes

Leaves and plagiotropic rhizomes were obtained from the ramets regenerated under laboratory conditions. The percentage of asepsia in the experiments with leaves and rhizomes was visually diagnosed by observing fungus and bacterial growth in the gellified culture medium. Viability was measured at three levels (0, 50 and 100%) and was defined with respect to the conservation of color in the leaf and rhizome. The experiment lasted 14 days.

Experiment 1. A random factorial design with three factors and two levels was applied in order to define the effect of the sterilization stage on the asepsia and viability of the leaf and rhizome explants (Zar 1999). The factors included the type of ex–plant (presterilised leaves and rhizomes), the dosis of NaClO (0.3 and 0.6 %) and the time of exposition to the chemical disinfectant (2.5 and 5 min). Each treatment presented five repetitions with a completely random distribution (Underwood 1997). Two 1 cm explants of the same type were placed in each experimental unit. The culture unit was monophasic and was prepared with semi–solid White medium at a pH of 7.5 with 58.4 mM sucrose. The exudates and white halos in the cultures were stained with Gram and the smear was observed with a microscope to identify the origin of the contamination. The analyzed samples were selected considering the type of contaminant, and were obtained from two cultures of leaves and two of rhizomes (10 % of the total).

Experiment 2. The lipidic contamination generated over the explants in experiment 1 was evaluated in the presterilization stage, and a culture medium with a random incomplete factorial arrangement with three factors and two levels (Zar 1999). A hypothesis was established to demonstrate that the asepsia and viability of the leaves and rhizomes were affected by the presence of exudates that were generated by the use of Tween in the aseptic procedure of V. americana, and that an anti–oxidant added to the culture medium might reduce this effect. The factors included the type of explant (leaf and rhizome), the presterilization with Tween 20® (0.0 and 0.1 %) and the addition of an anti–oxidant (0.0 and 0.01 %) to the culture medium. The design included only five treatments with a completely random distribution (Underwood 1997). The anti–oxidant was ascorbic acid added in solid form to the sterile nutrient medium before gellification. From this experiment onwards, the sterilizing condition for these explants was fixed at 0.3% NaClO for 2.5 min, and the general conditions of the ex–plant cultures (size of explants, experimental unit, repetitions and culture medium) were similar to those of the first experiment.

Experiment 3. The viability and asepsia of the leaves and rhizomes were determined with respect to the composition of the culture medium. The White nutrient medium and the 0.5 MS with 0.88 x 10–3 mM of bencyladenine (BA) and 58.4 mM sucrose were compared in this experiment. BA was used to induce organogenesis (Ailstock et al. 1991). One 1.5 cm explant was placed in each receptacle. The other general culture conditions were not modified. Viability was determined through leaf regeneration.

Experiments with the caulinar apex

Caulinar apices were provided by the greenhouse plants, as the laboratory plants cultivated in the White medium died after approximately three months due to conditions that are analyzed in the discussion. Asepsia percentages were calculated visually as in the previous experiments. The percentage of viability was quantified through leaf regeneration, and the level of viability was quantified through the number of leaves produced.

Experiment 4. The asepsia and viability of caulinar apices were evaluated with a random unifactorial design (Zar 1999) that included doses of 0.0, 2.22 x 10–3, 4.44 x 10–3 and 8.88 x 10–3 mM of BA in the culture medium. Sterilization was carried out in two phases to reduce the contamination of the explants. The apices were disinfected with 0.3% NaClO for 1 min, washed in sterile water and disinfected a second time with 0.6 % for 10 min. The culture medium was 0.5 MS prepared with 29.2 mM sucrose in liquid form. A 1.5 cm explant was placed in each receptacle. The treatments prepared with five experimental units remained static for 14 days.

Seed experiments and evaluations with germination kinetics

The aseptic procedure followed in the experiments with seeds was reduced to the stages of sterilization and poststerilization with five washings. Sterilization was carried out with 0.6% NaClO for 10 min.

Experiment 5. Aseptic seeds were germinated under the biphasic condition in test tubes with a completely random unifactorial design in order to obtain qualitatively healthy in vitro plants (Zar 1999). The studied factor was the aqueous phase, and its three levels were 0.5 MS, White and local potable water as culture media. The physicochemical characteristics of the local water (Table 1) indicated it was semi–hard (Anonymous 2000). The culture media were prepared with 29.2 mM sucrose and were adjusted to a pH of 6. Each treatment included five repetitions of the experimental unit distributed completely randomly (Underwood 1997). From 7 to 10 aseptically treated seeds were planted in each experimental unit. The seeds in the control group did not receive aseptic treatment and were cultivated in local sterile water without sucrose.

The effect of the treatments on the asepsia of the seeds and the quality of the regenerated material in the different aqueous treatments were recorded after 30 days. The criterium used to qualify the quality of the seedlings was the development of the whole plant (with coleoptile, at least one green leaf, and root growth).

Experiment 6. The germinative efficiency of V. americana in biphasic culture with gellified support was evaluated with local water with unchanged pH (Table 1). This aqueous medium was chosen as it provides low–cost plants of good quality. The design included culture time as a factor. Six repetitions of the experimental unit were carried out, each with 10 seeds that were distributed completely randomly (Underwood 1997). The seedlings were visually counted, considering the emergence of the coleoptile as the start of germination as the emergence of the radicle in this culture system is difficult to see. Germination was quantified on different days during one month. Germination kinetics were obtained through the germination percentages.

Statistical analyses

Kolmogorov–Smirnov & Lilliefords tests were used to determine the normality of the data, and the Cochran C test was used for the heterogeneity of variances (Underwood 1997). Variability of data was estimated with an ANDEVA of principal effects (experiments 2 and 3), and with a one–way analysis (experiment 1, 4) in the experiments with vegetative explants (Zar 1999). Post–hoc comparisons were analyzed with a Fisher LSD test. Contamination with fungus and dry white colonies (experiment 1), asepsia (experiments 2 and 3), viability (experiments 3 and 4) and the level of pigmentation (experiment 3) measured in the corresponding experiments did not present a normal distribution due to the abundance of cero values. In consequence, these variables were analyzed with the Kruskall Wallis (H) test, except for the level of pigmentation for which the Mann–Whitney (U) test was used. Statistical significance was established at p < 0.05. All statistical tests were carried out with general lineal models in the Statistica software (Anonymous 2004).

 

RESULTS

Asepsia and viability of leaves and rhizomes

All the cultures of V. americana leaves treated with NaClO presented contamination and were not viable. In contrast, 60% of the rhizomes were aseptic and survived with 0.3 % of NaClO 2.5 min. The two explants darkened in all the culture units.

Contamination by fungus in leaves and rhizomes accounted for 30 and 35 %. Another 5 % presented dry white halo forming bacteria. The other 65% of the leaves and 60 % of the rhizomes in the contaminated units presented mucilaginous translucid masses or exudates over the tissues. The microbiological analysis of the cultures with exudates and without mixed contamination showed only micelles. The dry white colonies were Gram negative.The explant, the concentration of chlorine and the time of exposition had no significant effect on the microbial contaminants that developed (p > 0.05, respectively).

The contamination by exudates disappeared in the leaf and rhizome cultures that did not receive treatment with Tween (F = 16. 29, p < 0.05) (Figure 1). No difference for this result was observed in relation to the type of explant (F = 0.63, p > 0.05). Ascorbic acid significantly inhibited the formation of exudates (F = 5.18, p < 0.05). The independent variables explant, Tween and ascorbic acid did not significantly affect asepsia (explant: H = 0.11, Tween H = 3.11, ascorbic acid: H = 2.25; p > 0.05), viability (explant: F = 0.9; Tween: F = 0.18; ascorbic acid: F = 0.43; p > 0.05) or contamination by dry white colonies (explant: F = 0.13, Tween: F = 0.65, ascorbic acid: F = 0.42; p > 0.05). This experimental set did not present fungal contamination.

The leaf and rhizome cultures turned out to be more aseptic when cultivated in the White medium than in 0.5 MS (H = 9.4; p < 0.05), independently of the type of explant (H = 1.92; p > 0.05) (Figure 2). The culture media did not generate significant differences in the viability percentage of the explants (H = 3.35; p > 0.05) or in regard to the structure that was cultivated (H = 0.37; p > 0.05). However, in the leaf cultures, a green pigmentation was favored when the 0.5 MS medium was used (U = 2.5; p < 0.05). The addition of BA to both culture media did not have a regenerative effect on any explant.

Asepsia and regeneration in caulinar apices

No significant differences were recorded for the viability of the caulinar apices in the treatments with BA (H = 0.76; p > 0.05). All cultures turned turbid and 80 % were contaminated with fungus. The average total viability of the apices was 50 % and foliar regeneration was recorded for all BA concentrations. The cultures that were supplemented with 0.88 x 10–3 mM of BA presented a greater foliar regeneration (F = 5.20, p < 0.05) than the other three treatments (Figure 3). However, all the explants began to rot after 14 days and finally died due to the high contamination.

In vitro germination

The in vitro germination of V. americana in different aqueous media and in the control was established with no sign of contamination. Seedlings with a high visual quality were obtained in 0.5 MS and in local water (Figure 4). In contrast, seedlings in the White medium presented an arrested development after the emergence of the coleoptile (Figure 4). The control seedlings were of good quality except for a low foliar pigmentation. The maximum germination percentage of V. americana in biphasic culture with gellified support and local water was 97 % (Figure 5). Asepsia and seedling quality were comparable to the biphasic culture with glass pearls, as no microbial growth was recorded and whole plants developed with pigmented leaves.

 

DISCUSSION

The in vitro establishment of V. americana through vegetative explants presented complications due to excessive contamination, as has been recorded for other aquatic plants (Balestri et al. 1998; Jenks et al. 2000; García–Jiménez et al. 2006). The leaf and rhizome explants were contaminated mainly by exudates, and the caulinar apices by fungal and bacterial growth. The formation of exudates was a peculiar characteristic, and was apparently the main cause of the darkening of leaves and rhizomes. However, no bacterial cells were detected when the exudates of both explants were stained with Gram and observed microscopically. In contrast, the micellar or mucilaginous appearance presented evidence of the production of lipidic substances and opened the hypothesis of a masked asepsia with a probable effect on explant viability. Potentially allelopat–hic essential oils with a strong activity against algae and fungus have been identified in the leaves of Vallisneria spiralis (Qiming et al. 2006). Also, alle–lochemical auto–toxicity has been observed in vitro in aquatic plants (Ervin & Wetzel 1999).

The disappearance of the exudates in the later cultures of V. americana leaves and rhizomes that were not presterilized with Tween during the aseptic procedure indicated: 1) that extracellular lipidic products caused the mortality of the explants, and 2) the need to omit the use of this surfactant with V. americana. The low aseptic efficiency and viability of explants obtained in this study coincided with data recorded for other macrophytes (Balestri et al. 1998; Jenks et al. 2000; García–Jiménez et al. 2006). The low efficiency obtained in experiment 1 is explained by the use of surfactants in the presterilization stage, as the presence of mucilaginous substances in aquatic macrophytes has been associated with excessive mechanical cleaning which modifies the quality and composition of excreted organic substances (Godmaire & Nalewajko 1986). The use of Tween is commonly recorded in presterilization and sterilization procedures. However its exclusion has not been explained (McCann et al. 2000).

The addition of an antioxidant reduced the exudate on the leaves and roots cultivated in experiment 2. Antioxidant agents, such as ascorbic acid, modify the redox potential in the culture medium, as they donate electrons that inhibit the oxidation of labile substrates (George 1996). Ascorbic acid and other antioxidants inhibited senescence of V. spiralis leaves by increasing chlorophyll and protein content that retarded the decrease of Hill activity (Sasad–har & Choudhuri 1987). However, the exclusion of presterilization with Tween in the leaf and rhizome explants (experiment 2) proved that it is not necessary to add an antioxidant if the surfactant Tween is not included in the procedure. This result made it possible to modify the procedure of the culture in gellified nutrient media (experiment 3), as both explants became established with aseptic efficiency and without darkening (experiment 4).

The leaves and rhizomes that were cultivated heterotrophically in monophasic nutrient media with BA (experiment 3) showed no signs of regeneration, although the viability of the leaves increased in the MS medium, together with an increase in pigmentation. In contrast, the caulinar apex showed their potential to form new leaves in spite of the turbidity and the mass of fungus that developed. The foliar organogenesis in the apex of the plagiotropic rhizome of Cymodocea nodosa was favored only by TDZ (N–phenyl–N'–1,2,3–thidiazol–5–ylurea) through the formation of a callus. However, when the structure was a ramet, the regeneration and foliar extension of a leaf occurred with the phytoregulators GA (gi–berellic acid), BA, KIN (kinetin) and TDZ (García–Jiménez et al. 2006). It was experimentally demonstrated that the use of the whole ramet of C. nodosa was a necessary requirement for carbon fixation, its translocation to the rest of the tissue and the later stimulus in the process of foliar development (García–Jiménez etal. 2006). Similarly to C. nodosa, the caulinar apices of V. americana cultivated in experiment 4 were the most adequate structures to regenerate leaves in vitro, although the cultures were not completely aseptic. In agreement with results published by Bird et al. (1998) and García–Jiménez et al. (2006), it is probable that the in vitro morphogenesis of the leaves of some submerged species present a greater genetic (division and cellular expansion) and environmental (light, temperature and nutrients) control. Foliar regeneration in the caulinar apices of V. americana was favored with 8.88 x 10–3 mM of BA. Similar doses have been used to regenerate and multiply other submerged aquatic species (Bird et al. 1998; Ailstock et al. 1991; García–Jiménez et al. 2006).

The development of V. americana cultures via vegetative explants was considered a priority in this study as this leads to the propagation of more genetically homogeneous plants and to a lower experimental error in the bioassays, considering that the genetic plasticity of aquatic plants has been cited as a problem for their use in bioassays (Mohan & Hossetti 1999). Also, the sexual route to provide submerged plants for bioassays is limited as a result of the availability of pollen and seeds (Sullivan & Titus 1996; Ke & Li 2006). The establishment of fruit in natural populations of V. americana is also limited by the availability of pollen and this, in turn, is affected by water depth, exposure to air and waves, and surface current speed (Sullivan & Titus 1996). The acquisition of a sufficient amount of V. natans seeds has restricted its success as an alternative method for the restoration of Chinese lakes (Ke & Li 2006), although submerged aquatic vegetation in general boasts a relatively successful reproductive process (Hemminga & Duarte 2000; Ke & Li 2006). The species Ceratophyllum demersum and Halophila decipiens, both cultivated in vitro, have been recorded with low germination frequencies (Wyman & Francko 1986; Bird et al. 1998).

In order to direct the in vitro culture of V. americana towards the development of ecophysio–logical or ecotoxicological experiments, it is fundamental to reproduce the natural submerged life conditions of the species. The in vitro culture of mature seeds was developed in a biphasic system with natural water or with a culture medium and glass pearl support considering the above statement. The seedlings in the biphasic culture with natural water and 0.5 MS were of good quality and there were no rhizospheric bacteria or microalgae. The efficiency of the system with respect to germination percentage was demonstrated when this was replaced by an agar layer to obtain the aseptic biphasic germination of V. americana in local water, and this was comparable to V. natans cultivated in non– aseptic, aerobic and light environment without the effect of the depth in boreal areas (Ke & Li 2006). The rooting of seedlings is also considered important in the growth of aquatic grasses (Bird et al. 1998).

The recommendation made by Uma & Mohan–Ram (1972) of using the White medium to cultivate V. spiralis seeds could not be reproduced in this study for the leaf and rhizome explants, nor for the seedlings or the stock of laboratory plants of V. americana. The White nutrient medium was prepared at a pH of 7.5 in this study, as this is the pH value recorded in Pantanos de Centla (Sánchez et al. 2007). The natural pH value is a basic factor in the procedure to cultivate V. americana. However, inorganic and organic components in culture media may modify the pH and affect the in vitro growth and propagation of plants (Owen et al. 1991). The White medium, compared with other better known media, is the formula with the lowest buffer capacity (Owen et al. 1991). According to Titus & Hoover (1993), the reproductive processes of V. americana in greenhouse conditions were affected at a pH of 5 as, under these conditions of acidity, the plants produced from seed did not flower, the rhizomes presented a lower biomass, they were different from those in the field, and they developed as very small plants. Nutrient enrichment has also represented an obstacle to micropropagate submerged marine vegetation (Balestri et al. 1998; Touchette & Boulkold–her 2002). Seedlings of the aquatic grass Halophila decipiens were found to be not viable in nitrate concentrations above 1.7 mM (Bird et al. 1998).

The in vitro germination in the biphasic system with an aqueous phase of local water or 0.5 MS produced healthy and rooted plants that are considered ideal for biological assays. In accordance with the results, the sterility of the seeds had a positive effect on germination, except when they were cultivated in the White medium. The hardness and alcalinity of the culture media may modify the speciation of ions, which favors the germination process or increases toxic effects (Owen et al. 1991).

Seeds were selected as candidates to obtain in vitro plants of V. americana, as the prevailing contamination in the three vegetative structures prevented their use as culture material. The genetic variability particular to the seeds is important in ecophysiological bioassays (Bird et al. 1998, Balestri & Bertini 2003). However, the in vitro production of plants from seeds has the inconvenience of depending on a natural seasonal and unpredictable supply, as has been frequently recorded for submerged aquatic vegetation (Zhou et al. 2006). The inter–annual availability of seeds of the V. americana populations distributed in Pantanos de Centla is very variable and unpredictable.

The choice of a culture medium is important for in vitro regeneration or multiplication (Kane et al. 2002). The MS medium at half ionic strength has been frequently used, and other aquatic plants have been micropropagated successfully (Jenks et al. 2000; Kane et al. 2002). In the case of V. americana, this nutrient medium did not affect the asepsia and viability of the seedlings, and it improved only the viability in the case of leaves and caulinar apices. Both results represent new possibilities for the in vitro clonation of V. americana in the MS medium, as an opportunity is opened to develop systems with fewer sources of contamination, extracting vegetative explants from aseptic seedlings.

Notwithstanding that the biphasic culture of V. americana with seeds in the MS medium was feasible (experiment 5), the model of in vitro plants with local water is even more advisable as its lower cost and simplicity present greater advantages for the development of ecophysiological and ecotoxico–logical tests with V. americana. The procedure of culture in water may also be reproduced and standardized if hard reconstituted local water is used in the development of tests under controlled conditions. This in vitro model of V. americana makes it possible to develop experimental studies to evaluate the factors that negatively affect its populations in Pantanos de Centla and other ecosystems. At present, the biphasic system with reconstituted water has been useful in starting in vitro tests with V. americana to determine tolerance to different ionic nitrogenated environments (Ruiz–Carrera, unpublished data).

The proposal to use alternative methods that include procedures with more natural in vitro cultures, with less stages and chemical substances, and with lower costs generates possibilities to prove hypotheses that will provide information to support the operation of programmes of wetland management where aquatic vegetation is declining or disappearing. This procedure offers this option for the V. americana populations in Pantanos de Centla or in any other ecosystem within its wide distribution from North America to Central America (Korschgen et al. 1988; Ellison 2004).

 

ACKONWLEDGMENTS

This study forms part of a project financed by the Fondos Mixtos and CONACyT (TAB–2003–CO3–11516). The authors thank Rosa Florido and Miguel Ángel Salcedo for valuable support, and Adriana Lizbeth Álvarez, Uriel Aguilar, Mórvila Cruz–Ascencio, Hugo Montalvo, Guadalupe Lara and Alberto Macossay for help in the field.

 

REFERENCES

Ailstock MS, Fleming WJ, Cooke TJ (1991) The characterization of axenic culture systems suitable for plant propagation and experimental studies of the submerged aquatic angiosperm Potamogeton pectinatus (sago pondweed). Estuaries 14: 57–64.         [ Links ]

Anonymous (2000) Standard methods for the examination of water and wastewater. APHA, AWWA, WPCF. Joint Editorial Board, Washington D.C. 139 pp.         [ Links ]

Anonymous (2004) Statistica (data analysis software system), version 7. http://www.statsoft.com.         [ Links ]

Balestri E, Bertini S (2003) Growth and development of Posidonia oceanica seedlings treated with plant growth regulators: possible implications for meadow restoration. Aquat. Bot. 76: 291–297.         [ Links ]

Balestri E, Piazzi L, Cinelli F (1998) In vitro germination and seedling development of Posidonia oceanica. Aquat. Bot. 60: 83–93.         [ Links ]

Best EPH, Teeter AM, Landwehr KJ, James WF, Nair SK (2008) Restoration options for potential persistence of submersed aquatic vegetation: combining ecological, hydrodynamic and sediment transport modelling. Freshwater Biol. 53: 814–826.         [ Links ]

Bird KT, Johnson JR, Jewett–Smith J (1998) In vitro culture of the seagrass Halophila decipiens. Aquat. Bot. 60: 377–387.         [ Links ]

Ellison AM (2004) Wetlands of Central America. Wetlands Ecology and Management 13: 3–55.         [ Links ]

Ervin GN, Wetzel R G (1999) Allelochemical autotoxicity in the emergent wetland macrophyte Juncus effuses (Juncaceae). Am. J. Bot. 87: 853–860.         [ Links ]

García–Jiménez P, Navarro EP, Santana CH, Luque Á, Robaina RR (2006) Anatomical and nutritional requeriments for induction and sustained growth in vitro of Cymodosea nodosa (Ucria) Ascherson. Aquat. Bot. 84: 79–84.         [ Links ]

Genkai–Kato M (2007) Macrophyte refuges, prey behaviour and trophic interactions: consequences for lake water clarity. Ecol. Letters 10: 105–114.         [ Links ]

George EF (1996) Plant propagation by tissue culture. Part 2. In practice. Exegetics Ltd. Edington. 1361 pp.         [ Links ]

Godmaire H, Nalewajko C (1986) Axenic culture of Myriophyllum spicatum L.: importance to extracellular product estimates. Aquat. Bot. 26: 385–392.         [ Links ]

Guadarrama MA, Ortiz–Gil G (2000) Análisis de la flora de la Reserva de la Biosfera de los Pantanos de Centla, Tabasco, México. Universidad y Ciencia 15: 67–104.         [ Links ]

Hall LW, Anderson RD, Ailstock MS (1997) Chronic toxicity of atrazine to sago pondweed at a range of salinities: implications for criteria development and ecological risk. Arch. Environ. Contam. Toxicol. 33:261–267.         [ Links ]

Hemminga MA, Duarte CM (2000) Seagrass Ecology. Cambridge University Press, Cambridge. 298 pp.         [ Links ]

Hobbs RJ, Harris JA (2001) Restoration ecology: repairing the Earth's ecosystems in the new millennium. Restoration Ecol. 9: 239–246.         [ Links ]

Jenks MA, Kane ME, McConnell DB (2000) Shoot organogenesis from petiole explants in the aquatic plant Nymphoides indica. Plant Cell Tissue Organ Cult. 63: 1–8.         [ Links ]

Jiménez GGL (2003) Variación temporal de biomasa y área foliar de V. americana en Pantanos de Centla, Tesis DACBiol – UJAT, Villahermosa. 39 pp.         [ Links ]

Kane ME, Gilman EF (1991) In vitro propagation and bioassay systems for evaluating growth regulator effects on Myriophyllum species. J. Aquat. Plant Management 29: 29–32.         [ Links ]

Kane ME, Philman NL (1997) In vitro propagation and selection of superior wetland plants for habitat restoration. Comb. Proc. Intl. Plant Prop. Soc. 47: 556–560.         [ Links ]

Kane ME, Philman NL, Emshousen C (2002) Wetland plant propagation: Comparative growth and reproduction of micropropagated Sagittaria latifolia ecotypes. Comb. Proc. Intl. Plant Prop. Soc. 52: 454–459.         [ Links ]

Ke X, Li W (2006) Germination requeriment of Vall/'sner/'a natans seeds: implications for restoration in Chinese Lakes. Hydrobiologia 559: 357–362.         [ Links ]

Korschgen CE, Green WL (1988) American wildcelery (Vallisneria americana): ecological considerations for restoration. U.S. Fish and Wildlife Service, Fish and Wildlife Technical Report 19. Jamestown, ND: Northern Prairie Wildlife Research Center Online. http://www.npwrc.usgs.gov/resource/plants/wildcel/index.htm (Version 16–Jul–97).         [ Links ]

Kurtz JC, Yates DF, Macauley JM, Quarles RL, Genthner FJ, Chancy CA, Devereux E (2003) Effects of light reduction on growth of the sumerged macrophyte Vallisneria americana and the community of root–associated heterotrophic bacteria. J. Exp. Marine Biol. Ecol. 291: 199–218.         [ Links ]

Li X, Gallagher JL (1996) Tissue culture and plant regeneration of big cordgrass, Spartina cynosuroide: implications for wetlands restoration. Wetlands 16: 410–415.         [ Links ]

Mackay SJ, Arthington AH, Kennard MJ, Pusey BJ (2003) Spatial variation in the distribution and abundance of submersed macrophytes in an Australian subtropical river. Aquat. Bot. 77: 169–186.         [ Links ]

McCann JH, Greenberg BM, Solomon KR (2000) The effect of creosote on the growth of an axenic culture of Myrioph/lum spicatum L. Aquat Toxicol. 50: 265–274.         [ Links ]

Moffler MD, Durako MJ (1984) Axenic culture of Thalassia testudinum banks ex König (Hidrocharitaceae). Am. J. Bot. 71: 1455–1460.         [ Links ]

Mohan BS, Hosetti BB (1999) Aquatic plants for toxicity assessment. Environ. Res. Section A 81: 259–274.         [ Links ]

Mony C, Koschnick TJ, Haller WT, Muller S (2007) Competition between two invasive Hydrocharitaceae (Hydrilla verticillata (L.f.) (Royle) and Egeria densa (Planch)) as influenced by sediment fertility and season. Aquat. Bot. 86: 236–242.         [ Links ]

Murashige T, Skoog F (1962) A revised medium for rapid growth and bioassays with tobacco tissue cultures. Physiol. Plant 15: 473–497.         [ Links ]

Murphy LR, Kinsey ST, Durako MJ (2003) Physiological effects of short–term salinity changes on Ruppia maritima. Aquat. Bot. 75: 293–309.         [ Links ]

Owen HR, Wengerd D, Miller AR (1991) Culture medium pH is influenced by basal medium, carbohydrate source, gelling agent, activated charcoal, and medium storage method. Plant Cell Reports 10: 583–586.         [ Links ]

Qiming X, Haidong Ch, Huixian Z, Daqiang Y (2006) Chemical composition of essential oils of two submerged macrophytes, Ceratophyllum demersun L. and Vallisneria spiralis L. Flavour Fragr. J. 21: 524–526.         [ Links ]

Rozas LP, Minello TJ (2006) Nekton use of Vallisneria americana Michx. (Wild Celery) beds and adjacent habitats in coastal Louisiana. Estuaries and Coasts 29: 297–310.         [ Links ]

Rybicki NB, Carter V (1986) Effects of sediment depth and sediment type on the survival of Vallisneria americana grown for tubers. Aquat. Bot. 24: 233–240.         [ Links ]

Rybicki BN, McFarland DG, Ruhl HA, Reel JT, Barko JW (2001) Investigations of the availability and survival of submersed aquatic vegetation propagules in the tidal Potomac. Estuaries 24: 407–424.         [ Links ]

Sánchez AJ, Salcedo MA, Florido R, Armenta A, Rodríguez–Leal C, Galindo A, Moguel E (2007) Pantanos de Centla, un humedal costero tropical. En: de la Lanza G, García–Calderón JL (eds) Las Aguas Interiores de México. Conceptos y Casos. AGT Editor S.A. Ciudad de México. 695 pp.         [ Links ]

Sasadhar J, Choudhuri MA (1987) Effects of antioxidants on senescence and hill activity in three submerged aquatic plants. Aquat. Bot. 27: 203–206.         [ Links ]

Sculthorpe CD (1967) The biology of aquatic vascular plants. St. Martin's. New York. 610 pp.         [ Links ]

Short FT, Koch EW, Creed JC, Magalhães KM, Fernandez E, Gaeckle JL (2006) SeagrassNet monitoring across the Americas: case studies of seagrass decline. Mar. Ecol. 27: 277–289.         [ Links ]

Sullivan G, Titus JE (1996) Physical site characteristics limit pollination and fruit set in the dioecious hydrophilous species Vallisneria americana. Oecologia 108: 285–292.         [ Links ]

Titus JE, Hoover DT (1993) Reproduction in two submersed macrophytes declines progressively at low pH. Freshwater Biol. 30: 63–72.         [ Links ]

Torres KC (1989) Tissue culture techniques for horticultural crops. Chapman & Hall. New York. 285 pp.         [ Links ]

Touchette BW, Burkholder JM (2002) Seasonal variations in carbon and nitrogen constituents in eelgrass (Zostera marina L.) as influenced by increased temperature and water–column nitrate. Bot. Mar. 45:23–24.         [ Links ]

Twilley RR, Barko JW (1990) The growth of submersed macrophytes under experimental salinity and light conditions. Estuaries 13: 311–321.         [ Links ]

Uma MC, Mohan–Ram HY (1972) In vitro culture of Vallisneria spiralis. Phytomorphology 22: 121–124.         [ Links ]

Underwood AJ (1997) Experiments in Ecology. Cambridge University Press, Cambridge. 522 pp.         [ Links ]

Westcott K, Whillans TH, Fox MG (1997) Viability and abundance of seeds of submerged macrophytes in the sediment of disturbed and reference shoreline in Lake Ontorio. Can. J. Bot. 75: 451–457.         [ Links ]

White PR (1963) The Cultivation of Animal and Plant cells. Ronald Press Co., New York. 60 pp.         [ Links ]

Wigand C, Stevenson JC (1994) The presence and possible ecological significance of mycorrhizae of the submersed macrophyte Vallisneria americana. Estuaries 17: 206–215.         [ Links ]

Wigand C, Stevenson JC (1997) Facilitation of phosphate assimilation by aquatic mycorrhizae of Vallisneria americana Michx. Hydrobiologia 342/343: 35–41.         [ Links ]

Wigand C, Wehr J, Limburg K, Gorham B, Longergan S, Findlay S (2000) Effect of Vallisneria americana (L.) on community structure and ecosystem function in lake mesocosms. Hydrobiologia 418: 137–146.         [ Links ]

Wyman C, Francko DA (1986) Germination of Ceratophyllum demersum seeds in aseptic liquid culture. Proc. Okla. Acad. Sci. 66: 27–29.         [ Links ]

Xiong BH, Li W (2002) Winter buds of Vallisneria in Banghu and Zhonghuci, two lakes in Poyang lake Nature Santuary. Acta Hydrobiol. Sin. 26: 19–24 (in Chinese).         [ Links ]

Zar JH (1999) Biostatistical Analysis. Prentice–Hall Inc. Upper Saddle River. 663 pp.         [ Links ]

Zhou C, An S, Jiang J, Yin D, Wang Z, Fang C, Sun Z, Qian C (2006) An in vitro propagation protocol of two submerged macrophytes for lake revegetation in east China. Aquat. Bot. 85: 44–52.         [ Links ]

Creative Commons License All the contents of this journal, except where otherwise noted, is licensed under a Creative Commons Attribution License