1. Introduction
Orchidaceae is one of the most diverse and largest families of flowering plants, with more than 27,000 species [
1,
2]. Orchids are globally distributed; they can be found on all continents except Antarctica, with the tropics being the region with the greatest orchid diversity [
3,
4]. Specifically, the tropical Andes is considered the largest plant biodiversity hotspot worldwide [
5], with orchids being one of the main contributors to species richness in this area [
6]. A clear example of this extraordinary orchid diversity is found in Ecuador, the smallest country in Andean South America, where more than 4200 orchid species have been reported [
7,
8]. Most of these orchid species (3214) occur in the ecosystem of the Andean forest, located 1000 to 2500 m.a.s.l. [
9].
The genus
Epidendrum is the second-largest orchid genus in Ecuador. The genus is comprised of 1200 species, of which 453 occur naturally in Ecuador [
7].
Epidendrum species are distributed throughout tropical America, from the sea level up to 3700 m.a.s.l. These species can be found in most habitats in Ecuador, but the highest diversity and abundance are in wet cloud Andean forests [
10].
Epidendrum geminiflorum Kunth is a native orchid species distributed in Venezuela, Guianas, Colombia, Ecuador, and Peru [
11,
12]. In Ecuador, the species can be found in the coastal, Andean, and Amazonian regions, from 1000 to 3500 m.a.s.l [
11]. Plants are epiphytic, sympodial, 20–50 cm in height, characterized by cane-like stems, with coriaceous but flexible leaves, and resupinate green to greenish flowers without fragrance (
Figure 1) [
12].
Epidendrum geminiflorum is very common and widely distributed; therefore, its conservation status is qualified as “less concerned” (LC) [
12,
13]. However, orchids that are common today may not be common tomorrow.
Several biological and ecological factors have been attributed to the high diversity and worldwide distribution of Orchidaceae [
14]. Mycorrhizal associations developed during seed germination and seedling establishment in situ are likely to have a significant effect on orchid distribution and population structure [
15,
16,
17]. Orchid seeds are the smallest produced in flowering plants. They are produced in large numbers, with small undifferentiated embryos containing minimal nutrient reserves [
3,
18]. Therefore, orchid seeds fully depend on the establishment of mycorrhizal associations for enhanced nutrients and water during the germination and early seedling stages [
19]. Adult plants may develop different fungal associations or may no longer require such associations [
20].
Epiphytic and terrestrial green (photosynthetic) orchids usually associate with fungal species from Ceratobasidiaceae, Sebacinales, and Tulasnellaceae in the Basidiomycota taxa [
15,
21]. Many of these mycorrhizal fungi are widespread and occur in a wide variety of habitats [
17]. The degree of specificity for their mycorrhizal fungi varies with orchid species. Epiphytic and terrestrial orchids may be associated with a very narrow or very wide range of mycorrhizal fungi [
22,
23]. Patterns of specificity towards mycorrhizal associates throughout the orchid life cycle have been described mostly for terrestrial orchid species. The seed of four terrestrial orchid species germinate and develop into protocorms when co-cultured with many fungal isolates; however, only a subset of compatible fungi support the development of more advanced orchid seedling stages [
24].
Reductions in the diversity and distribution of orchid populations are often the result of anthropogenic activities [
14,
25]. Many endangered orchid species occur in the neotropics, a region recognized for its species richness and high levels of endemism but with high rates of habitat loss [
5]. Illegal collection also threatens many orchid species with extinction. In Ecuador, the collection of wild species for commercial use in local and international markets is the second major threat to the conservation of orchids [
26]. The potential effects of climate change on the long-term survival of orchid populations are difficult to predict due to the complexity of the obligated interactions with other sympatric organisms for orchid survival [
25].
Despite the extraordinary diversity and abundance of epiphytic orchid species in the Andean forest [
27,
28], most information regarding the mycorrhizal association during seed germination and seedling establishment is well documented for terrestrial orchids in temperate zones [
15]. In Ecuador, research on orchid mycorrhizal associations has been focused on the isolation and identification of endophytes isolated from orchid species from the Andean cloud forest of south Ecuador [
22,
23,
29,
30]. Successful germination and seedling development using symbiotic seed culture have been obtained only on
Epidendrum secundum Jacq., a native terrestrial Ecuadorian orchid species using fungal species:
Ceratobasidum sp. and
Sebacina vermifera, isolated from native orchid species located in the southern Andes of Ecuador [
31].
Symbiotic seed germination and seedling development involve the co-culture of orchid seeds with their fungal associates, which promote the establishment of the mycorrhizal association in vitro under sterile and controlled environmental conditions [
32]. Physiological compatibility, patterns of in vitro fungal specificity, dependency, and environmental factors that control germination and seedling development, can be studied using this approach [
24]. Stewart and Kane [
33] reported that mycobionts isolated from
Spiranthes floridana promoted the high percent germination of
Spiranthes brevilabris; however, subsequent early seedling development was only supported by a fungus isolated from the same species. These results suggested that the high degree of mycobiont specificity observed under in vitro culture conditions may be linked to the rarity of this Florida orchid species in situ. Symbiotic seed culture can also be used as an ex situ conservation strategy for the effective sexual propagation of plant material that may reduce collection pressure on wild populations [
25]. The production of plant material with compatible symbiotic fungi can be used in restoration projects to ensure the long-term survival of the populations [
32,
34].
Factors that affect seed germination and seedling development, mycorrhizal diversity, and the degree of specificity and dependency of orchids on certain fungi species need to be experimentally evaluated. This scientific information will be critical to developing effective strategies for orchid conservation and the restoration of native orchid species from Ecuador [
14,
20,
35]. Consequently, the objectives of the present study are to: (1) evaluate the effects of photoperiods on symbiotic seed germination and seedling development in
E. geminiflorum; (2) document the morphological development from seed to the mature seedling stage; and (3) screen putative mycorrhizal fungi isolated from native Ecuadorean orchid species for their ability to facilitate seed germination and seedling development in vitro.
2. Materials and Methods
2.1. Sample Collection Permits
Permits to collect and transport seed capsules and root pieces for research purposes were obtained from Ministerio del Ambient del Ecuador (MAE). All these permits had the institutional support of Instituto Nacional de Biodiversidad (INABIO) through a contract (Contrato Marco MAE-DNB-CM-2016-0045) of this research institution with MAE, which allowed the collection of native flora and research that includes DNA analysis. All regulations were followed to comply with the legal collection of the native orchids. Orchid seeds were imported into the United States under USDA/APHIS permit number P37-16-0-5568. For the import of fungal mycelia to the USA, a permit to move live plant pests, noxious weeds, and soil (P526P-19-02945) was obtained from the US Department of Agriculture (USDA).
2.2. Seed Collection
Recently dehisced mature capsules of Epidendrum geminiflorum Kunth were collected from a small native orchid population located in Cuyuja (S 00.42885 W 078.01733, 2616 m.a.s.l.), Napo Province, in September 2018. Capsules were placed in sterile paper bags and then transported to the laboratory in Ecuador. Seeds were removed from the capsules and stored in loosely capped glass vials over CaSO4 desiccant inside sealed 50 mL Falcon® tubes in the dark at 22 ± 2 °C until shipping to the in vitro plant culture laboratory located at the University of Florida, Gainesville, Florida, USA. Seeds were dried for 10 weeks after collection before being stored at −10 °C in the dark until used for experimentation. A vial with seeds was also maintained at 22 ± 2 °C in the dark for 7 additional weeks to test seed viability loss over time under these storage conditions.
2.3. Seed Size and Weight
Seed weights were estimated as follows: three samples of dry seed, taken from cold storage, were weighed on an ultra-microbalance instrument (Model No. XP2U Mettler-Toledo LLC, Columbus, OH, USA). Seeds were then rinsed with water to facilitate counting over a black cloth using a stereomicroscope. The weight of each sample was divided by the number of seeds per sample. Estimated seed weight was used to calculate the solution volume required to deliver uniform 60 μL aliquots, each containing ca. 100 sterile seeds, to ensure similar numbers of seeds per sub-replicate in each experiment.
2.4. Seed Viability Testing
Percentage viability was tested using triphenyl tetrazolium chloride (TTC) staining before being stored, after 7 wks under storage conditions (−10 °C in the dark and at 0% RH) and 17 wks at 22 ± 2 °C in the dark and 0% relative humidity after field collection. Seed samples (1.5 mL microtubes containing 10 mg seed) were preconditioned in 1 mL 10% sucrose solution for 24 h at 22 ± 2 °C. Seeds were then rinsed twice with deionized distilled (dd) water; 1 mL 1% TTC solution was added to the microtubes, and samples were incubated in the dark at 36 °C for 24 h. To avoid embryo discoloration, the TTC solution was replaced with dd water and samples were stored at 4 °C until their evaluation using light microscopy. Seeds with rose-red stained embryos were considered viable, while white embryos were recorded as non-viable [
36,
37].
2.5. Seed Sterilant Screening
Different hypochlorite solutions and sterilization time combinations were evaluated for their effectiveness on orchid seed surface sterilization and their subsequent effects on percent seed germination. Approximately 5 mg of seeds contained in sterile 1.5 mL microtubes were surface sterilized with either 0.3%, 0.5% sodium hypochlorite/ethanol or 2% calcium hypochlorite solutions for 1, 3, and 5 min. The sodium hypochlorite (NaOCl)/ethanol solutions were prepared by adding 250 μL 100% ethanol and 250 (0.3% v/v) or 416 μL (0.5% v/v) 6.0% sodium hypochlorite (Clorox© Bleach), and then diluting the solution to 5 mL with sterile dd water. To prepare a saturated Ca(OCl)2 solution, 307 mg powder (65% available chlorine) was dissolved in 10 mL sterile dd water. This gave a final solution that provided 2% available chlorine. Sterile filter paper (Whatman ®, Qualitative 1, Cat# 1001-125) was used to filter the solution immediately before use. Once the sterilization times were completed under constant agitation, the solutions were removed by placing a sterile pipette tip into the bottom of the microtube. Seeds were then rinsed three times for 1 min each with sterile dd water. The control treatment consisted of no sterilization and three rinses for 1 min each with sterile dd water.
Surface-sterilized seeds were sown on Petri dishes (100 × 15 mm) containing 30 mL Orchid Seed Sowing Medium (PhytoTechnology Laboratories, Shawnee Mission, KS, Cat# P723). Three 60 μL aliquots of sterile seeds in sterile dd water were pipetted and placed in 3 different sections on the surface of the germination media. Seeds were then evenly spread using a sterile inoculating loop. Four Petri dishes per treatment were sealed with one layer of sealing film (PhytoTechnology Laboratories, Cat# A003) and incubated for 4 wks at 20 °C under a 12 h-light/12 h-dark photoperiod in a Percival I-35LL growth chamber (Percival Scientific, Boone, IA, USA). Light was provided by cool-white florescent tubes (General Electric F20T12/CW) at 35 μMm−2s−1 (photosynthetic active radiation, PAR).
2.6. Symbiotic Seed Germination
Fungal isolation and molecular identification. Field collection of roots from young or adult plants and seedlings, when available, was made from native orchid populations located in the northern tropical Andes in Ecuador. Collections were made in May 2016, July 2017, and August 2018. At most, three active growing roots or seedlings were detached from the tree bark using a sterile scalpel and placed in sterile plastic bags. Fungal isolation from mature roots of
E. germiniflorum was not possible due to the absence of fungal pelotons. Likewise, no young plants or seedlings were observed in the population. Samples were transported over ice in an insulated container to the Idgen Molecular Diagnostic Laboratory located in Quito, Ecuador. Isolation of root endophytes from root cortical tissue was performed following standard methods described by Zettler et al. [
38] and Zettler and Corey [
34]. Briefly, roots were rinsed with sterile distilled (d) water to remove bark debris and then surface-sterilized in a solution containing 6% NaClO:98% ethanol:d water (8:5:87) for 1 min followed by two 1-min rinses with sterile distilled (d) water.
Roots were cut into 1 cm long segments starting at the tip. Each segment was placed into a separate sterile Petri dish with 200 μL sterile d water. Using a sterile scalpel and forceps, root segments were chopped to break open the cortical cells harboring fungal pelotons. Aliquots (25 mL) of sterile warm fungal isolation medium (FIM) [
39], supplemented with 10 mg/L streptomycin sulfate antibiotic, were slowly poured into individual Petri dishes. Dishes were then gently swirled to disperse the cortical tissue homogenate throughout the medium. Plates were sealed with one layer of sealing film and incubated for 24–48 h at 22 ± 2 °C. Using a stereo microscope, plates were observed for actively growing hyphae emerging from pelotons. Individual pelotons with hyphal tips were subcultured into separate Petri dishes containing 25 mL ½X potato dextrose agar (PDA,
PhytoTechnology Laboratories, Cat# P772). Plates were sealed and incubated again at 22 ± 2 °C. After 24–72 h, pelotons with short hyphal tips or hyphal tips alone were transferred to fresh 1⁄2 PDA on slants in glass tubes. Culture tubes were sealed with a layer of sealing film and incubated at 23 ± 2 °C for at least 48 h and then stored at 4 °C until their transportation to the in vitro culture laboratory located at the University of Florida, Gainesville, Florida, USA.
Fungal cultures in tubes were subcultured into Petri dishes containing 25 mL 1⁄2 PDA. Pure cultures with morphological features assigned to the form-genus
Rhizoctonia [
39] were kept for further identification to the genus level using Sanger sequencing of the ribosomal DNA internal transcribed spacer (ITS) sequences [
40]. Pure cultures of putative mycorrhizal fungi were transferred to fresh 1⁄2 PDA slants in glass tubes maintained in the dark at 10 °C and subcultured every 4 months. These cultures are permanently stored at the University of Alberta Microfungus Herbarium in Toronto, Canada (UAMH). (
Table 1).
Symbiotic seed culture. Sterile seeds of
E. geminiflorum were co-cultured with fungal strains isolated from different native Ecuadorean orchid species (
Table 1) and one
Tulasnella calospora strain (University of Alberta Microfungus Herbarium UAMH 9824) isolated from a root of
Spiranthes brevilabris in Levy County, Florida, USA [
41]. Fungal isolates, stored in the dark at 10 °C, were subcultured onto fresh 1⁄2 PDA for 2 wks in the case of
Tulasnella and 2–3 days for
Ceratobasidium strains to obtain actively growing mycelia prior to experiment initiation.
The symbiotic seed germination medium used was oatmeal agar (OMA), which was prepared with 2.5 g/L oat flour and 7 g/L TC agar (
PhytoTechnology Laboratories, Cat# A296). The medium was sterilized by autoclaving at 117.7 kPa and 121 °C for 40 min. After solidification of 30 mL OMA in each Petri dish (100 × 15 mm), a triangle-shaped cellophane membrane (BIO-RAD, Cat# 1650922) was placed over the surface of the medium to improve visualization of the growing hyphae. A 1 × 4 cm black filter paper strip (Thomas Scientific, Cat# 4740C10) was placed parallel to each side of the triangle to support the sterile seeds (
Figure 2c). Black filter paper instead of standard white paper facilitates seeing the light-colored seeds more clearly.
Seeds were removed from cold storage and maintained at 22 ± 2 °C for at least 4 h before sterilization. Three seed samples weighing ca. 20 mg each were surface-sterilized using a 0.5% sodium hypochlorite/ethanol solution for 3 min, followed by three 1-min rinses with sterile dd water. After sterilization, dd water was added to the seeds to obtain a solution containing 100 seeds per 60 µL aliquot. Three aliquots were pipetted out and placed over the surface of the black filter paper strips. A 1 × 1 × 0.5 cm3 PDA block containing the mycelium from each isolate was inoculated over the cellophane membrane. A control treatment consisted of OMA without fungal inoculation. Based on a preliminary asymbiotic media germination screening, P723 was included as the asymbiotic treatment.
Petri dishes were sealed with one layer of sealing film and incubated under both 0/24 h and 12/12 h light/dark photoperiods at 20 °C in a Percival I-35LL growth chamber (Percival Scientific, Boone, IA); light was provided by cool-white florescent tubes (General Electric F20T12/CW) at 35 μMm
−2s
−1 PAR. Plates were examined for germination after 2 wks. Germination and seedling development stages (
Table 2) were recorded every 2 wks using a stereomicroscope. After 6 wks of culture, Petri dishes under continuous dark treatment were unwrapped from the aluminum foil and exposed to a 12-h photoperiod for the remainder of the experiment. Roots from seedlings produced on the symbiotic media were finely sliced and stained using an aqueous 0.5% Toluidine Blue staining solution for 24 h to evaluate the presence of fungal pelotons in the cortical tissue using a microscope.
2.7. Experimental Design and Statistical Analysis
Treatment effects were evaluated using a completely randomized experimental design. Each factor or combination of factors consisted of 7 replicates with 3 sub-replicates (
Figure 2). The experimental unit consisted of a Petri dish containing 30 mL culture medium with three areas, each containing a filter paper strip with ca. the same number of seeds on the surface of each strip (
Figure 2c). These areas were considered sub-replicates. The number of seeds in each developmental stage was recorded at each data collection time. All experiments were repeated once. Percent data were arcsine-transformed prior to the analysis using a multi-factor ANOVA by each data collection point. Mean separation was assessed using Tukey’s methods at the α = 0.05 significant level. Statistical analyses were completed with JMP Pro15 (Manufacture, SAS Institute Inc., Cary, NC, USA). Survival analysis was performed using the survival package in R studio 3.2.5. Time-to-event data, in this case, the time from sowing to germination (Stage 2), were analyzed. A Kaplan–Meier estimator was used to estimate the survival function with 95% confidence intervals. Log-rank tests were performed to evaluate differences between survival curves at the α = 0.05 significant level. Multiple pair-wise comparisons were performed using a log-rank test with Bonferroni correction to adjust
p-values at the α = 0.05 significance level.
4. Discussion
Our results demonstrated that
E. geminiflorum seedlings can be produced in vitro on asymbiotic media (P723) or through symbiotic seed culture with
T. calospora (US266-UAMH 9824) isolated from
S. brevilabris, an endangered terrestrial orchid native to Florida, USA [
41]. After 42 weeks, very few seedlings in early developmental stages were also produced in OMA with a
Tulasnella strain isolated from a native population of
L. acarina, located in the same location where
E. geminiflorum seeds were collected. To the best of our knowledge, this study represents the first report on the in vitro seed germination and early seedling development of
E. geminiflorum. Morphological developmental stages, from seed to early seedling development, were also documented for the first time for this native species collected in the northern Andes of Ecuador.
Open capsules were collected from an individual in a small patch of the Andean forest located on a private property in Cuyuja, Ecuador. Small numbers of individuals at the collection site reflected the scattered distribution, with a few individuals restricted to small areas, a typical characteristic described for populations of epiphytic orchids of the neotropics [
43]. In addition, the absence of local seedling recruitment may be the result of the altered or degraded habitat where seeds were collected. Favorable conditions for germination and seedling establishment may no longer be present at the site, leading to an eventual population decline [
20]. The possible senile nature of this population may have contributed to the difficulty of isolating compatible fungal associates of this orchid.
The viability of seeds is highly variable within orchid species [
3]. It is commonly known that if seeds are allowed to dry and then stored at low temperatures (0–10 °C), seeds may remain viable for long periods of time. However, if they are maintained at ambient temperatures, they will rapidly lose their viability [
3]. However, this seems not to be the case for
E. geminiflorum seeds, which exhibited 93.2% viability after being stored for 17 wks at 22 ± 2 °C in the dark. Despite the high percentage of seeds with no embryos, a high viability of seeds with visible embryos (~96%) was observed, and the maximum germination obtained in P723 (87.0–88.8%) did not differ from the seed viability estimated with the TTC staining test. Consequently, TTC seed viability can be used as a reliable test to estimate the seed viability and germination potential of seed samples of this species. This could be valuable for germination trials for preservation purposes [
36].
Sterilization treatments are used under in vitro culture conditions to eliminate cultivable bacterial or fungal contamination from orchid seed surfaces. Since compounds that block water imbibition, such as suberin, are eliminated with hypochlorite solutions, sterilization has also been used as a scarification treatment to improve germination percentages [
44,
45]. Our sterilant screening showed that reliable seed sterilization was possible either with 2% Ca(OCl)
2 or 0.5% NaOCl solutions, with either no detrimental or positive effect on germination percentages. However, faster development into advanced protocorm stages was observed when the seeds were sterilized with NaOCl solutions. Faster protocorm development could probably also ensure faster and higher seedling development. Therefore, the use of a 0.5% sodium hypochlorite/ethanol solution is recommended as a sterilant for
E. geminiflorum seeds.
Symbiotic seed culture can result in higher germination percentages compared with those obtained with asymbiotic germination in some orchid species [
46]. Our results showed the opposite response. Significantly lower germination was observed when seeds were co-cultured with fungal strains compared with that on P723 medium (asymbiotic control). The required nutrients that may be available in P723 for the optimal germination of
E. geminiflorum may not have been sufficient to provide for any of the fungi tested. Seeds of
E. geminiflorum were also able to germinate (Stage 2) in the symbiotic control in the absence of nutrients or readily available carbohydrates. Other orchid seeds, such as
Cynorkis purpurea (Thouars) Kraez from Madagascar, were also able to germinate in OMA without fungal inoculation [
46]. The presence of
Tulasnella strains significantly improved germination percentages over the control treatment once fungal mycelia reached the
E. geminiflorum seeds on the filter paper.
Tulasnella calospora (US266) grows faster than the other
Tulasnella strains isolated from native orchid species from Ecuador, which possibly resulted in earlier and higher germination rates with US266 compared to the other
Tulasnella strains. Only one
Ceratobasidium isolate, ER2C, significantly increased germination rates compared with the control. However, embryos germinated with
Ceratobasidium strains displayed browning on one side. This browning may be the result of localized decomposition by the fungus, which is not considered a typical characteristic of symbiotic culture [
47].
Tulasnella calospora (UAMH 9824) has been recognized for its ability to promote successful germination and seedling development in a variety of orchid species from different geographical locations after decades of subculturing [
48]. These include
Epidendrum species such as
E. nocturnum, an epiphytic orchid native to Florida, USA [
49], and other genera:
Habenaria repens, a semi-aquatic orchid from Florida [
42], and
Platanthera holochila, a terrestrial endangered orchid from Hawaii [
50].
Responses to light during germination and seedling development stages vary within orchid species [
19,
44]. Inhibition of germination under illumination has been reported in both terrestrial and epiphytic species [
51]. Our result showed that light is not a requirement for the germination of
E. geminiflorum seeds as the seeds germinated under both 12 h-light and 24 h-dark photoperiods; however, light significantly promotes faster germination. After the exposure of seeds maintained under complete darkness conditions prior to a 12 h-light photoperiod, they continued to germinate until reaching cumulative germination, with no significant differences between photoperiod treatments at 126 days. This confirmed the ability of
E. geminiflorum to germinate regardless of light conditions. Seeds of the Florida native
E. nocturnum from south Florida cultured in OMA with
T. calospora (US266-UAMH 9824) also germinated (52–68%), with no significant differences between dark and light treatments [
49].
Although the seed germination of E. geminiflorum was not affected by photoperiod, the presence of light during symbiotic seed germination (US266) was critical for subsequent seedling development. Non-green protocorms produced under complete darkness failed to develop into the seedling stages. Immediate exposure of germinated embryos to light conditions will probably result in successful seedling establishment on site. Epiphyte position in tree canopies allows them to have access to light, which may be an important requirement to be met during the earlier developmental stages of E. geminiflorum.
Temperature has also been reported as an important environmental factor that influences the germination and seedling establishment of orchid species [
19,
20,
44]. Preliminary asymbiotic seed germination studies (data not shown) performed with
E. geminiflorum showed that seedling development was not possible at 23 °C, regardless of the availability of nutrients in the media. Constant temperatures higher than 20 °C are not present at the collection site (Cuyuja, Ecudor, 2616 m.a.s.l.) [
52]. Orchid species located at this altitudinal gradient may be sensitive to small increases in average temperature. Prediction models suggest a significant increase in temperature between 2 and 7 °C in the tropical Andean region toward the end of the 21st century [
53]. Between 2000 and 3500 m.a.s.l., observations and projections both suggested stronger warming scenarios in the western slope of the Andes [
53]. Future environmental conditions may not be favorable for the seedling establishment of this orchid species at its original locations. Given the wide altitudinal distribution (1000–3500 m.a.s.l.) of
E. geminiflorum [
11], ecological studies including seeds from different geographic locations are needed to determine if observed responses to temperature may be the result of ecotypic differentiation under local environmental conditions. Biomass allocation and corm formation timing during in vitro seed germination studies have been presented as evidence of ecotypic differentiation between different
Calopogon tuberosus var.
tuberosus populations collected from Michigan, South Carolina, and Florida. Seedlings from higher latitudinal populations tended to allocate biomass faster to their underground structures (corms) than plants from lower latitudinal populations [
54]. Scientific information from these studies will be critical for the selection of plant material adapted to restoration target sites. This may ensure the long-term survival of the restored populations [
55].
The presence of compatible mycorrhizal fungi during seed germination and seedling establishment are critical for the survival of orchid species in situ [
20]. Degrees of specificity towards fungal associates may change throughout the life cycle in the same orchid species. Some terrestrial orchids seem to be associated with a great number of diverse fungi during germination, but only a subset of these was able support seedling development [
24]. A similar pattern of specificity was observed in
E. geminiflorum in this study, where seed germination was supported with all fungal strains tested, but advanced seedling development was only observed with one fungus (US266-UAMH 9824).
Early seedling development of
E.
geminiflorum in situ may require specific fungi different than those screened in our study. These fungi may be expected to facilitate higher percentages of seedling production than those observed with US266. Symbiotic germination studies with fungi associated with
E. geminiflorum would be critical to determine the levels of specificity toward fungal associates of this orchid species, which may result in higher seedling production than that obtained in this study. Although
T. calospora (US266; US266-UAMH 9824) is considered ubiquitous, the release of orchid seedlings with this exotic fungus into the wild could pose an ecological risk to other orchid species, considering its foreign origin (Florida) [
49]. The survival of seedlings to ex vitro conditions needs to be evaluated for this orchid species, with the aim of developing an efficient protocol to produce suitable plant materials that ensure successful restoration or conservation projects.