2010 - The rediscovery

EL REDESCUBRIMIENTO DE MEXIPEDIUM XEROPHYTICUM

The rediscovery of Mexipedium xerophyticum

Eduardo A. Pérez-García

Lankesteriana 9(3): 557-563. 2010

Note: The translation is an unofficial document provided for information purposes only. The official source is the original publication: https://www.lankesteriana.org/indiceGENERAL.htm

The discovery of Mexipedium xerophyticum has been regarded as one of the most remarkable discoveries of the Neotropical orchid flora in recent decades (Salazar and Hágsater, 1997). Although this species has some horticultural interest, its importance lies more in biological terms, as it has changed previously held ideas about the phylogenetic and biogeographic relationships of the subfamily Cypripedioideae (Albert, 1994; Albert & Chase, 1992; Chase, 1996; Salazar & Hágsater, 1997; Shefferson, 2007; Leitch, 2009).

The history of the discovery of this species has been documented since its original description (Soto-Arenas et al., 1990) and has been recounted on other occasions (Salazar-Chávez & Hágsater, 1997; Hágsater & Soto Arenas, 1998). Similarly, some detailed descriptions of this species have already been published (Soto-Arenas et al., 1990; Soto, 2003; Soto-Arenas & Solano-Gómez, 2007). Thus, we now know that M. xerophyticum is a paleoendemic genus, exclusive to the Los Chimalapas region in the Mexican state of Oaxaca. It should be noted that the description of its habitat was also made since the original publication of this species; however, the information on its habitat has been deformed in subsequent publications, to the point of considering Mexipedium as a desert species (Koopowitz, 2008). Other aspects of this species have also been studied, such as its cytology (Cox, 1997) or its vegetative anatomy (Sandoval et al., 2003), but due to its rarity it still has many important unknown aspects (Cox et al., 1998; Shefferson, 2007).

The cultivation of this plant has caused some impact among orchidologists and hobbyists, and several works have already been developed on this subject (Koopowitz, 1995, 2008; Pasetti, 1995; LeDoux, 1996; Reddy, 2008; Anonymous 2009a,b). Therefore, this note will focus on two of the main points of the biological value of this species: (I) its particular phylogenetic situation and its evolutionary interpretation, and (II) the habitat and conservation status of this species.

Evolution and phylogeny

Since its publication, Phragmipedium xerophyticum has changed its generic position and has also been placed in two other genera: Mexipedium and Paphiopedilum, in chronological order of the respective publications. So far, these are the only known synonyms for this species:

  • Phragmipedium xerophyticum Soto Arenas, Salazar & Hágsater. Orquídea (Mexiko) 12(1):2. 1990.
  • Mexipedium xerophyticum (Soto Arenas, Salazar & Hágsater) V.A. Albert & M.W. Chase, Lindleyana 7(3):174. 1992.
  • Paphiopedilum xerophyticum (Soto Arenas, Salazar & Hágsater) V.A. Albert & Bórge Pett., Lindleyana 9(2):138. 1994.

Although its position in any of the three genera is feasible according to phylogenetic analyses, its placement as a distinct monotypic genus is now accepted (Pridgeon et al., 1999; Soto, 2003). It has been postulated that M. xerophyticum is a relict species that represents the only survivor of a basal clade among the conduplicate-leaved slipper orchids, with intermediate traits between the Phragmipediums that are distributed exclusively in the neotropical region and the Paphiopedilum that are typical of the old world (Salazar-Chávez & Hágsater, 1997; Sandoval et al., 2003; Soto-Arenas & SolanoGómez, 2007). The genome of Mexipedium has a size of 1C ¼ 6.73 pg, and 2n ¼ 26 chromosomes, making it very similar to Phragmipedium, which is why it is considered its sister genus (Leitch et al., 2009). Consistent with these results, based on molecular studies, Albert (1994) found that the separation between Mexipedium and Paphiopedilum dates back between 16.4 and 23 million years, so at the biogeographical level it has been considered as an example of the ancient boreotropical flora of the early Miocene (Salazar-Chávez & Hágsater, 1997; Soto-Arenas & Solano-Gómez, 2007). The presence of elements of the boreotropical flora, which relates the North American flora to the Asian flora (Tiffney, 1985a,b; Cevallos-Ferriz & González-Torres, 2005), seems to be very important in the Mexipedium habitat region (Wendt, 1989). In fact, it can be argued that in general, the orchid flora of Oaxaca consistently has several of the most basal Orchidaceae lineages in their respective phylogenetic groups (Soto & Salazar, 2004). It should be noted that the Cypripedioideae are one of the oldest groups of the Orchidaceae, and therefore the analysis of this group of plants is relevant for the understanding of the evolutionary history of a family that has an origin from 111 to 119 million years ago (Janssen & Bremer, 2004).

Habitat

 

Mexipedium xerophyticum has only been collected in one locality in the Chimalapas region, in the Isthmus of Tehuantepec, Oaxaca. In addition, it is only known from one particular limestone outcrop at 320 m asl. The exact locality of M. xerophyticum has been kept in the AMO Herbarium in order to avoid poaching.

Mexipediums are plants that produce fan-shaped growths from which stolons with new fans are produced, allowing some clonal expansion. However, this clonal expansion is apparently somewhat limited in the natural habitat to the existence of a microbial mat (Salazar & Hágsater, 1997). In the original search expedition for this species in 1988, only seven plant clumps were found, probably representing different genotypes (genets; Soto-Arenas et al., 1990). This number of genets was obtained considering a spatial separation between plants, but without using any molecular marker to see if they are really different genotypes or not. In that expedition a complete genet and a part of another one were extracted (Salazar & Hágsater, 1997, Hágsater & Soto Arenas, 1998). All plants known in cultivation outside Mexico have been propagated from these plants, both by vegetative propagation and from seed (LeDoux, 1996; Salazar & Hágsater, 1997; Hágsater & Soto Arenas, 1998; Soto-Arenas & Solano-Gómez, 2007).

Subsequent to their discovery, two more genets were extracted in their entirety by an amateur. So far little is known about the whereabouts of these two plants, except that they were originally taken to Minatitlán, Veracruz (Soto-Arenas & Solano-Gómez, 2007). In July 1996, in a new botanical survey in the locality, Gerardo Salazar found two new plants, so that by that date only six different genets had been counted in the wild. It should be noted that, although fruit production has been observed in the field (in 1988, 1996, 1997; Soto-Arenas & Solano-Gómez, 2007), all the plants observed are adults and apparently there is no recruitment of new individuals from sexual reproduction (Salazar & Hágsater, 1997). The Mexipedium habitat region has been explored in detail and no new localities have been detected, although their existence is not ruled out, apparently these rocky outcrops are not common at the site and much of the surrounding forest has already been transformed (Salazar & Hágsater, 1997). For these reasons, it has been considered that M. xerophyticum probably cannot maintain any viable population in the wild (Soto Arenas, 1996).

The precarious situation of M. xerophyticum became much more serious in 1998, when a fire destroyed its habitat. Since then, the locality had not been explored again to assess whether plants still survived in the wild. In August 2009 a new expedition was made to this locality, and it was found that of all the previously detected plants only one survived. This plant was severely damaged by fire and apparently has not flowered since, but is currently recovering. Mr. Heriberto Hernandez, who was one of the original collectors of this species, scoured the sites where the other plants had been found and concluded that they were gone. Together with his son, Gerobuam, we went back to explore the scree, especially in the less accessible places. Thus, in a gully with vertical walls, several more plants were located (Fig. 1). A couple of them had flowers and another one had buds (Fig. 2).

Figure 1: Images of different plant clusters (genets?) of Mexipedium xerophyticum growing in its habitat. Panel A shows the only surviving genet of the seven that were originally found.

Considering that Mexipedium has the potential to clone, it is difficult to know exactly how many different genotypes there are in the locality at present. However, considering a relevant distance between plant clusters, at least six new groups of plants could be recognized, which tentatively can be considered as different genotypes. In this sense, the development of molecular studies to try to know how many genotypes really exist in the wild becomes very relevant. Likewise, a detailed demographic study is required to know the dynamics of this population in order to know its viability.

Unfortunately, our visit to this locality was very brief, and not much information could be obtained in the field. However, there are some observations that can be made. One of them is that it was the first time that flowering was recorded during the month of August, thus extending the flowering period observed in the field, since previously flowers had only been seen in September (Soto-Arenas & Solano Gómez, 2007). However, this is not very surprising, since plants in cultivation start flowering as early as spring (Anonymous. 2009a) and their flowering can extend until November (Soto-Arenas & Solano-Gómez, 2007). There is information that flowering of this species can occur during different times of the year when grown under constant light intensities (Anonymous, 2009b).

The habitat of this species is a karstic scree of less than two hectares in extension, which makes Mexipedium the only “Phragmipedium” that grows on limestone rock (Anonymous, 2009a). In this scree, low stature arborescent plants such as Beaucarnea sanctomariana, Bursera simaruba, Plumeria rubra and Pseudobombax ellipticum grow. In addition, plants of the genera Agave, Acanthocereus, Begonia, Catopsis, Peperomia, Phylodendrum, Pitcairnia, Selaginella, Tillandsia, several unidentified ferns and some other orchids such as Bletia sp., Cyrtopodium macrobulbon and Encyclia cf. parviflora proliferate in this environment. Although the vegetation of the Mexipedium microhabitat can be categorized as xerophytic shrubland, it is actually rock vegetation immersed in a matrix of high evergreen forest. Some detailed descriptions of similar environments but in seasonally dry forests can be found in Pérez-García and Meave (2004) and Pérez-García et al. (2009). It is worth mentioning that the limestone outcrops of the Isthmus of Tehuantepec are home to numerous endemic species, such as Beaucarnea sanctomariana L. Hernández (Hernández-Sandoval, 2001), Agave guiengola Gentry (Torres-Colín, 1989) and several more in the Nizanda region (Pérez-García & Meave, 2004). With this information it can be concluded that these screes are ancient environments that have allowed the diversification of a very particular flora.

So far, all the plants of M. xerophyticum that have been found were growing on vertical rock walls, with a northerly exposure. Due to the latitude at which this species is found, during part of the year these plants do not receive direct sunlight, but this situation changes substantially during the rainy season (which is concentrated in the summer; see Gallardo et al., 2009). Perhaps for this reason, the species has both adaptations to capture light in the leaves (Sandoval et al., 2003) and a very xerophytic morphology.

Figure 2: Plants of Mexipedium xerophyticum in the reproductive state. Panel A shows a flowering plant that differs from those shown in Figure 1. Panel B shows a close-up of a group of plants shown in Figure 1F. Panel C shows a close-up of an inflorescence of the plant shown in Figure 1B.

Conservation

It is difficult to make predictions about the future of this species in its natural habitat. With the information available it is clear that it is a plant that has very few individuals. This is true even if all the rooted growths are considered, regardless of their genetic origin. Moreover, all these plants are concentrated in a very small area of less than one hectare. Thus, both its demographic rarity and the restriction of its habitat make it very vulnerable. For this reason, this species is listed as Endangered in the Peligro de Extinción en la Norma Oficial Mexicana para especies en riesgo (SEMARNAT, 2002).

On the other hand, the owners of the property are interested in the conservation of this species. They do not allow access to strangers and are not interested in transforming the site for agricultural activities. Although the site is not suitable for agricultural or livestock activities, it is very susceptible to regular burning in the surrounding area, as was observed in the 1998 fires. Salazar and Hágsater (1997) proposed some measures for the in situ conservation of this species. However, the locality belongs to an ejido and many of the decisions have to be made collectively and through procedures that are somewhat complicated to understand. In addition, the ejido to which the locality belongs is highly politicized and it is not easy to accept outside guidelines.

In stark contrast, ex situ conservation of the species has been very successful. The manner followed by the discoverers of the species, of sending plants to growers and scholars of the group (see Hágsater, 1996; Hágsater & Soto Arenas, 1998) gave very good results. Today there are several commercial nurseries selling plants, and in some cases the prices of plants have fallen since 2002 (Reddy, 2008). In summary, the probability of survival of this species in the wild is not exactly known, but it can be predicted that its future is assured in cultivation.

I dedicate this work to the memory of Miguel Ángel Soto Arenas, who was one of the discoverers and researchers of this species, but who was also my teacher and friend.

Acknowledgments. To H. Hernández González for guiding us through the study site. We also thank Téc. Ftal. G. Hernández Jiménez and all the staff of the RPC Istmo Oaxaqueño/ RFSIPS/ of CONANP (SEMARNAT) for their assistance in the field work. DGAPA-UNAM funded the field trip through the PAPITT program (IN-216007-3).

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