Research Paper
International Journal on Environmental Sciences 8 (1) : 64-86, January-June 2017
ISSN No.: 0976-4534
Diversity of Pleurothallidinae in Guatemala: An Endangered Orchid
Subtribe with High Economic and Horticultural Potentials
EDGAR MÓ1, WILLIAM CETZAL-IX2,*, SAIKAT KUMAR BASU3,
ELIANA NOGUERA-SAVELLI4, HERMES VEGA5,
FERNANDO CASANOVA-LUGO6 & JEAN-MARC PALLANDRE7
1
Orquigonia, Reserva Natural y Centro de Conservación de Orquídeas, Cobán, Alta Verapaz, Guatemala
Instituto Tecnológico de Chiná, Calle 11 entre 22 y 28, Colonia Centro Chiná 24050, Campeche, México
3
Department of Biological Sciences, University of Lethbridge, Lethbridge, AB Canada T1K 3M4
4
Catedrática CONACYT, Colegio de Postgraduados Campus Campeche. Carretera Haltunchén-Edzná Km.17
5
Sichochac, Champotón, Campeche, México
5
MAPANCE, Mancomunidad de Municipios del Parque Nacional Celaque, Bo. Mercedes
Edif. de Gobernación, Gracias, Lempira, Honduras
6
Instituto Tecnológico de la Zona Maya, Quintana Roo, México
7
Vineuil-Saint-Firmin 60500, France
2
Received: 25 February 2017;
Revision: 15 March 2017
Accepted: 15 May 2017
ABSTRACT
The orchid flora of Guatemala includes 1,200 species; representing 10% of the total species present in the
world, demonstrating rich biodiversity. Among the orchids, the subtribe with the highest number of
endangered species is Pleurothallidinae; because their species lack pseudobulbs and are plants that die during
the summer from dehydration. However, plants produce flowers more than once during the year for seed
generation and maintain their populations. In the neotropics this subtribe comprises 4000 species and in
Guatemala 211 species and four natural hybrids in 20 genera have are recorded; distributed in wet forests and
subtropical lower rainforests, at an elevation of 300-3000 m. The genera and number of species are:
Lepanthes (70 species and four hybrids), Stelis (47), Specklinia (22), Platystele (15), Trichosalpinx (13),
Acianthera (12), Pleurothallis (11), Lankesteriana (6), Restrepia (6), Anathallis (5), Masdevallia (5),
Dryadella (3), Myoxanthus (3), Octomeria (3), Dresslerella (2), Lepanthopsis (2), Barbosella (1), Draculla
(1), Kraenzlinella (1), Restrepiella (1), Scaphosepalum (1). Of these taxa, 57 species are known only from a
few localities of Guatemala and 29 are restricted to the southeast Mexico and Guatemala. Hence, several
species are classified as Least Concern or Near Threatened by IUCN; however, they should be categorized as
Endangered due to their restricted distribution and serious anthropogenic pressure impacting local
populations. The ornamental and horticultural potentials of Pleurothallidinae diversity in the fragmented
forests can be harnessed in establishing a model for the sustainable management. This will help in
conservation of endangered local orchid species; and in the restoration of fragmented forest areas by
integrating that to the judicious economic development of impoverished local communities.
Key words: Orchid, Pleurothallidinae, Guatemala, conservation, anthropogenic threats.
INTRODUCTION
In this sense, the epiphytes that are mainly orchids
become essential elements for the maintenance of the
biodiversity; as well the balance of the natural forest
communities. They positively influence the
ecosystems to provide nutritional resources and
specialized microenvironments for the canopy fauna
The Pleurothallidinae subtribe is one of the largest
groups of orchids with over 4000 species and is one of
the main components of the neotropic epiphytic flora
(Viveros & Higgins 2007, Higgins & Williams 2009).
*Corresponding author: rolito22@hotmail.com
64
International Journal on Environmental Sciences 8 (1)
EDGAR MÓ et al.,
65
plateau systems that originates in Chiapas and ranges
into northern Honduras along a NW-SE general
direction. These species predominantly grow in
different ecosystems ranging from lowland moist
forests to the dry or humid oak and pine-oak forests at
higher elevations of up to 1600 m; often occurring in
cloud forests (Mó et al. 2014; Cash et al. 2016).
that actively participate in nutrient cycling process
(Lugo & Scatena 1992; Delio Endres et al. 2014). Also,
the biological importance of this group of plants is that
they can be comprehensively considered as biological
or ecological indicators of disturbance; since they have
an unique habitat specificity and preference for
specialized hosts. The density of their wild populations
decreases significantly in disturbed forests (SolanoGómez et al. 2008).
This area of Guatemala is considered as priority
conservation for its tropical montane cloud forests and
tropical rain forests. The wet forest and subtropical
lower rainforest habitats, where different species of
Pleurothallidinae are distributed in Guatemala are
seriously threatened due to several anthropogenic
factors like extensive conversion of forest to
agricultural lands, rapid changes in land use due to
extensive cattle ranching, unmonitored forest fires,
indiscriminate removal of the plants by scraping since
local coffee growers believe that the orchids are
parasitic and their elimination is necessary to boost
coffee production and incentives by the local forest
department to replace native vegetation with Pinus
maximinoi (Mó et al. 2014; Cash et al. 2016).
The Pleurothallidinae species has a wide range of
forms of growth (epiphytic, terrestrial, rheophyte,
lithophyte etc) and occupies diverse habitats (e.g.,
nearly all Neotropical forests, paramo, Mangroves,
deserts) (Higgins & Williams 2009). These species of
this group are characterized by an articulation between
the ovary and the pedicel, and by the stem (ramicaul)
bearing one leaf that always lacks pseudobulbs (Luer
1986; Higgins & Williams 2009). According to
Higgins & Williams (2009), a typical pleurothallid is
an epiphyte with a restricted distribution, frequently
endemic, that lives in sympatry with other
pleurothallids in extremely moist forests to elevation
between 1800-2800 m. However, endemism and the
restricted distribution of its species are making them
more vulnerable to extinction (Viveros & Higgins
2007).
Furthermore, these plants and their small flowers have
niche markets for plant collectors, tourists and for
commercial use in special events like birthdays and
weddings among local communities. Since the sale of
these plants is prohibited in the country, these are
illegally traded in markets in the states of Alta Verapaz,
Baja Verapaz, Chiquimula, El Progreso, Guatemala,
Jalapa, Quiché and Zacapa (Mó et al. 2014; Cash et al.
2016). However, unfortunately no comprehensive
study of ornamental potential and the implications
associated with its conservation of Pleurothallidinae
species of Guatemala till date.
The species of this subtribe have wide geographic
range from southern Florida, the West Indies, and
extending from Mexico to as far as southern Brazil and
northern Argentina (Viveros & Higgins 2007). The
greatest diversity of this group is reported from South
America, in the Andes of Colombia, Ecuador and Peru
(Luer 1986). In Central America, the countries with the
greatest diversity of Pleurothallidinae species are
Costa Rica (459), Panama (375), Mexico (215) and
Guatemala (206), while countries with lower diversity
are Nicaragua (143), Honduras (124), El Salvador (79)
and Belize (65) (Ossenbach et al. 2007). Despite the
valuable contributions of collectors and growers,
Guatemala has not yet performed a comprehensive
survey and determined any reliable conservation status
of the local Pleurothallidinae species.
Our objective has been to explore the ornamental
potential and recording of the habitats of different
endangered species of Pleurothallidinae
(Orchidaceae) with photographs and to identify any
anthropogenic factors impacting the survival and
existence of these endangered orchid species in
Guatemala. Furthermore, we propose a model for the
long term, sustainable management and conservation
of the endangered local orchid species threatened by
anthropogenic actions and help in the restoration of
fragmented forest areas in the region.
The largest number of the Pleurothallidinae species
reported from Guatemala is distributed mostly in the
central part of the country; where the diversity of the
vegetation types is dominated by high mountains and
65
66
Diversity of Pleurothallidinae in Guatemala.....
Botanical collections
As part of our project reintegration of the knowledge of
orchid flora of Guatemala and as an effort to contribute
to the conservation of the diverse flora of the country,
photographic collections were made between
September 2010 and December 2016 in different areas
JANUARY-JUNE 2017
of the Guatemala. The specimens were photographed
in their natural habitat and at orchid exhibitions (Table
1, Figs. 1-8). The identification of the specimens
photographed on site were made based on Icones
Pleurothallidinarum (Luer 1986a, 1986b, 1991, 1994,
1996, 2000, 2002, 2004, 2005, 2006).
Table 1: Pleurothallidinae species in Guatemala. SA = South America, ORN = Ornamental. MED = Medicinal. IT =
Illegal Trade. PIU = Prices in USA Dollars. * Endemic species. † Present in Alta Verapaz Department.
MEX
GUA
BEL
Acianthera angustifolia (Lindl.) Luer †
TAXA
1
1
1
Acianthera angustisepala (Ames & Correll)
Pridgeon & M.W. Chase †
1
1
1
Acianthera breedlovei Soto Arenas,
Solano & Salazar
1
1
Acianthera circumplexa (Lindl.)
Pridgeon & M.W. Chase
1
1
Acianthera herrerae (Luer)
Solano & Soto Arenas
1
1
Acianthera hondurensis (Ames)
Pridgeon & M.W. Chase †
1
1
Acianthera johnsonii (Ames) Pridgeon
& M.W. Chase †
1
1
Acianthera pubescens (Lindl.) Pridgeon
& M.W. Chase †
1
1
Acianthera tikalensis (Correll & C. Schweinf.)
Pridgeon & M.W. Chase
1
1
Acianthera violacea (A. Rich. & Galeotti)
Pridgeon & M.W. Chase†
1
1
Anathallis lewisiae (Ames) Solano &
Soto Arenas†
1
1
Anathallis minutalis (Lindl.) Pridgeon & 1
M.W. Chase
1
Anathallis sertularioides (Sw.) Pridgeon &
M.W. Chase†
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
Acianthera javieri Archila* †
Dresslerella archilae Luer & Béhar* †
Dryadella greenwoodiana Soto Arenas, Salazar
& R. Solano
NIC
CR
PAN
SA
I
1
1
Dryadella linearifolia (Ames) Luer †
1
1
Kraenzlinella erinacea (Rchb. f.) Solano †
1
Lankesteriana abbreviata (Schltr.) Karremans†
1
1
ORN
MED
IT
PIU
I
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
Dryadella guatemalensis (Schltr.) Luer †
Lankesteriana barbulata (Lindl.) Karremans†
HON
1
Barbosella prorepens (Rchb. f.) Schltr. †
Dracula pusilla (Rolfe) Luer †
ELS
1
1
1
1
1
1
1
1
1
1
1
1
Lankesteriana comayaguensis (Ames)
Karremans†
1
1
1
1
1
1
1
10
1
1
10
1
15
Lankesteriana duplooyi (Luer & Sayers)
0Karremans
Lankesteriana involuta (L.O. Williams)
Karremans
10
Lepanthes × fonacytii Archila* †
1
1
20
Lepanthes × mendiatae Archila* †
1
1
20
66
International Journal on Environmental Sciences 8 (1)
EDGAR MÓ et al.,
67
Lepanthes × stenosepala Luer & Béhar* †
1
1
20
Lepanthes × tuerckheimii Schltr.* †
1
1
25
1
15
1
15
1
25
Lepanthes acuminata Schltr. †
1
1
Lepanthes almolongae Luer & Béhar
1
1
Lepanthes ancylopetala Dressler
1
1
Lepanthes any Archila*
1
Lepanthes archilae Luer & Béhar* †
1
Lepanthes appendiculata Ames †
1
1
1
1
1
1
10
20
1
15
1
1
25
1
1
25
Lepanthes carvii Archila* †
1
1
15
Lepanthes chapina Luer & Béhar* †
1
1
Lepanthes cleistogama Archila* †
1
1
Lepanthes cobanensis Archila* †
1
1
10
1
1
20
1
15
1
25
Lepanthes beharii Luer* †
Lepanthes breedlovei Salazar & Soto Arenas †
1
Lepanthes denticulata Luer & Béhar
1
Lepanthes disticha Garay & R.E. Schult. †
1
1
1
Lepanthes doeringii Archila †
1
Lepanthes enca-barcenae Archila †
1
Lepanthes excedens Ames & Correll
1
Lepanthes fratercula Luer & Béhar †
1
Lepanthes geniculata Luer & Béhar
1
1
1
Lepanthes gustavo-romeroi Archila
1
1
1
1
1
1
20
1
1
1
1
25
1
20
1
1
20
1
1
1
Lepanthes hondurensis Ames †
1
10
20
1
Lepanthes herrerae Luer & Béhar
1
1
1
Lepanthes gibberosa Ames †
Lepanthes guatemalensis Schltr. †
1
1
1
1
1
20
1
15
1
10
1
25
Lepanthes huehuetenangensis Archila †
1
1
10
Lepanthes ibanezii Luer & Béhar †
1
1
20
Lepanthes inaequalis Schltr. †
1
Lepanthes isabelii Archila †
1
Lepanthes javieri Archila †
1
1
1
1
Lepanthes johnsonii Ames †
1
Lepanthes lenticularis Luer & Béhar
1
1
1
1
1
1
20
1
15
1
20
1
30
15
1
1
Lepanthes loboauriculatus Archila †
1
1
10
Lepanthes luisii Archila †
1
1
25
15
Lepanthes matudana Salazar & Soto Arenas †
1
1
1
Lepanthes maxima Salazar & Soto Arenas
1
1
1
30
Lepanthes migueliana Luer & Béhar †
1
1
10
Lepanthes milciadesmejiae Archila,
Jiménez Rodr. & Véliz †
1
1
1
1
35
1
1
25
Lepanthes mittelstaedtii Luer & Béhar †
Lepanthes motozintlensis Salazar & Soto Arenas
1
Lepanthes necae Archila Archila
1
1
20
Lepanthes noelii Luer & Béhar
1
1
10
Lepanthes ordonezii Luer & Béhar
1
1
10
1
12
Lepanthes oreocharis Schltr.
1
1
1
Lepanthes oroscoi Archila
1
1
12
Lepanthes oscarii Archila
1
1
15
Lepanthes pantomima Luer & Dressler †
Lepanthes papillipetala Dressler †
1
1
Lepanthes parvula Dressler †
1
1
1
67
1
25
1
20
1
20
68
Diversity of Pleurothallidinae in Guatemala.....
JANUARY-JUNE 2017
Lepanthes purulhaensis Archila †
1
1
20
Lepanthes quetzalensis Luer & Béhar †
1
1
25
Lepanthes rodrigogonzalesii Archila †
1
Lepanthes salazarii Archila †
1
Lepanthes samacensis Ames †
1
1
Lepanthes scopula Schltr. †
1
1
1
1
1
1
25
1
10
Lepanthes sotoi Archila †
1
Lepanthes stefaniae Archila †
1
1
1
1
5
1
1
30
Lepanthes stenophylla Schltr. †
1
Lepanthes systole Luer †
Lepanthes tactiquensis Archila †
1
15
1
1
35
Lepanthes tecpanica Luer & Béhar
1
1
1
15
Lepanthes tenuiloba R.E. Schult. &
G.W. Dillon
1
30
1
1
Lepanthes velifera Luer & Béhar †
1
1
35
Lepanthes verapazensis Archila †
1
1
35
Lepanthes vilchezii Archila
Lepanthes williamsii Salazar & Soto Arenas
1
1
Lepanthes yunckeri Ames †
1
1
1
1
1
1
1
Lepanthopsis floripecten (Rchb. f.) Ames †
Masdevallia adamsii Luer †
1
Masdevallia chontalensis Rchb. f. †
1
1
1
Masdevallia corinnea Archila, Jiménez
Rodr. & Véliz
†
Masdevallia floribunda Lindl. †
1
Masdevallia tubuliflora Ames †
1
1
1
Masdevallia tuerckheimii Ames †
1
1
Myoxanthus congestus (A.Rich. &
Galeotti) Soto Arenas †
1
1
Platystele compacta (Ames) Ames †
1
1
Platystele jungermannioides (Schltr.) Garay †
1
1
Platystele minimiflora (Schltr.) Garay
1
1
1
1
1
1
20
10
10
1
25
1
1
1
1
1
1
1
1
15
1
1
1
15
1
1
1
1
5
1
30
1
1
Platystele pedicellaris (Schltr.) Garay †
1
1
Platystele repens (Ames) Garay †
1
Platystele oxyglossa (Schltr.) Garay †
1
1
Platystele sancristobalensis Archila †
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
Platystele taylorii Luer †
Platystele escalerae Archila †
Pleurothallis antonensis L.O. Williams †
20
1
1
1
1
Platystele stenostachya (Rchb. f.) Garay †
1
1
1
Platystele ovalifolia (H. Focke) Garay &
Dunst †
Platystele ovatilabia (Ames & C. Schweinf.)
Garay †
25
1
1
Platystele narvalis Archila †
20
1
1
1
Platystele bernoullii Luer †
1
30
1
1
1
Pleurothallis archilarum Chiron †
1
1
1
Pleurothallis correllii Luer †
1
1
Pleurothallis crocodiliceps Rchb. f. †
1
Pleurothallis leucantha Schltr. †
1
1
1
1
1
1
1
Pleurothallis pansamalae Schltr. †
1
1
15
15
35
1
1
1
1
68
1
5
8
1
1
1
1
1
1
1
35
20
1
1
1
Pleurothallis matudana C. Schweinf. †
1
1
15
1
1
30
20
1
1
Pleurothallis cardiothallis Rchb. f. †
1
1
1
1
1
1
1
1
1
1
15
1
8
1
8
8
International Journal on Environmental Sciences 8 (1)
Pleurothallis saccatilabia C. Schweinf.
1
Pleurothallis sanchoi Ames †
†
1
Pleurothallopsis ujarensis (Rchb. f.)
Pridgeon & M.W. Chase †
1
Pleurothallis testifolia (Sw.) Lindl.
Restrepia archilae Chiron & Szlach.
†
1
1
1
1
1
1
1
1
1
1
69
1
1
1
Restrepia cobanensis Archila,
Chiron & Szlach. †
Restrepia guatemalensis Archila
EDGAR MÓ et al.,
1
20
1
15
1
15
1
25
1
†
1
Restrepia mayana Archila, Chiron & Szlach.
Restrepia muscifera (Lindl.) Rchb. f. ex Lindl.
1
†
1
1
1
1
Restrepia valverdei Archila, Jiménez Rodr.
& Véliz †
Restrepiella ophiocephala (Lindl.)
Garay & Dunst. †
1
1
1
1
1
1
1
25
1
1
12
1
1
1
5
Scaphosepalum microdactylum Rolfe †
1
15
Scaphosepalum standleyi Ames †
1
15
1
15
Specklinia acicularis (Ames & C. Schweinf.)
Pridgeon & M.W. Chase †
1
Specklinia alata (A. Rich. & Galeotti) Solano
& Soto Arenas †
Specklinia blancoi (Pupulin) Soto Arenas &
Solano
1
1
1
1
1
Specklinia brighamii (S. Watson) Pridgeon
& M.W. Chase †
25
1
Specklinia corniculata (Sw.) Steud. †
15
1
Specklinia fimbriata (Ames & C. Schweinf.)
Solano †
1
1
1
Specklinia fuegii (Rchb. f.) Solano &
Soto Arenas †
1
1
1
1
5
Specklinia glandulosa (Ames) Pridgeon
& M.W. Chase
1
12
Specklinia grobyi (Bateman ex Lindl.)
F. Barros †
1
5
1
1
20
1
1
Specklinia juddii (Archila) Archila †
1
1
1
Specklinia marginata (Lindl.) Pridgeon
& M.W. Chase †
1
1
1
1
25
1
Specklinia lanceola (Sw.) Lindl. †
1
1
1
Specklinia pisinna (Luer) Solano
& Soto Arenas †
Specklinia remotiflora Pupulin & Karremans †
1
1
1
5
1
15
1
15
Specklinia samacensis (Ames) Pridgeon
& M.W. Chase †
1
Specklinia segregatifolia
(Ames & C. Schweinf.)
Solano & Soto Arenas †
1
15
Specklinia spectabilis (Ames & C. Schweinf.)
Pupulin & Karremans †
1
Specklinia tribuloides (Sw.)
Pridgeon & M.W. Chase †
1
10
8
Specklinia yucatanensis
(Ames & C. Schweinf.)
Pridgeon & M.W. Chase †
Stelis aemula Schltr. †
15
Stelis aeolica Solano & Soto Arenas †
1
10
Stelis anagraciae Archila & Szlach. †
1
1
1
15
Stelis annedamoniae Solano †
1
1
1
25
69
Diversity of Pleurothallidinae in Guatemala.....
70
Stelis argentata Lindl.
JANUARY-JUNE 2017
†
Stelis chiapensis Solano †
Stelis chihobensis Ames †
1
10
1
10
1
10
1
10
Stelis ciliaris Lindl. †
Stelis cleistogama Schltr. †
1
1
Stelis cobanensis (Schltr.)
Pridgeon & M.W. Chase †
1
1
Stelis emarginata (Lindl.)
Soto Arenas & R. Solano †
1
1
Stelis fulva Schltr. †
1
1
1
1
1
1
1
1
1
1
10
2
Stelis despectans Schltr. †
10
1
5
1
10
Stelis gracilis Ames †
Stelis greenwoodii Soto Arenas & Solano
0
5
1
Stelis guatemalensis Schltr. †
1
1
1
Stelis hymenantha Schltr. †
1
1
1
Stelis immersa (Linden & Rchb. f.)
Pridgeon & M.W. Chase †
1
Stelis jalapensis (Kraenzl.)
1
Stelis johnsonii Ames †
1
Stelis kellogi (Archila) Mó &
Cetzal, comb. nov. †
1
1
1
1
1
1
1
1
15
5
10
1
1
5
1
25
1
20
1
Stelis lamprophylla (Schltr.) Karremans †
1
5
Stelis microchila Schltr. †
1
10
Stelis ornata (Rchb. f.) Pridgeon &
M.W. Chase †
1
1
Stelis ovatilabia Schltr. †
1
1
Stelis oxypetala Schltr. †
1
1
Stelis pachyglossa (Lindl.) Pridgeon &
M.W. Chase †
1
1
1
1
25
1
10
1
10
1
1
10
Stelis pardipes Rchb. f.
Stelis parvula Lindl. †
Stelis platystylis (Schltr.) Solano &
Soto Arenas †
10
1
1
1
1
1
5
Stelis punctulata (Rchb. f.) Soto Arenas †
1
Stelis purpurascens A. Rich. & Galeotti †
1
Stelis rubens Schltr. †
1
1
Stelis scariosa (Lex.) Karremans †
1
1
Stelis segoviensis (Rchb. f.) Pridgeon
& M.W. Chase †
Stelis superbiens Lindl. †
1
1
1
1
Stelis tenebrosa (Archila, Szlach. & Chiron)
Karremans †
10
1
1
1
1
1
Stelis tenuissima Schltr. †
1
1
1
1
1
Stelis vestita Ames †
1
1
1
1
Stelis villosa (Knowles & Westc.)
Pridgeon & M.W. Chase †
1
1
1
1
1
1
1
1
1
5
1
25
1
1
1
15
10
1
1
Trichosalpinx carvii (Archila) J.M.H.Shaw †
Trichosalpinx cortezii Archila †
1
1
Stelis vespertina Solano & Soto Arenas †
Trichosalpinx ciliaris (Lindl.) Luer †
1
1
Stelis megachlamys (Schltr.) Pupulin †
10
1
1
Stelis tacanensis R. Solano & Soto Arenas
Trichosalpinx blaisdellii (S. Watson) Luer †
20
1
1
1
1
1
1
1
1
1
1
1
1
1
1
5
5
5
1
1
1
1
1
5
10
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71
Trichosalpinx crucilabia (Ames & Correll)
Luer †
1
1
Trichosalpinx cunorensis (Archila)
J.M.H.Shaw †
1
1
Trichosalpinx dura (Lindl.) Luer †
1
Trichosalpinx franciscantha (Archila)
J.M.H.Shaw †
Trichosalpinx fruticosa Luer †
Trichosalpinx greenwoodiana Soto Arenas †
1
1
1
1
1
1
1
1
1
1
1
1
1
Trichosalpinx memor (Rchb. f.) Luer †
1
1
Trichosalpinx pringlei (Schltr.) Luer
1
1
Trichosalpinx trachystoma (Schltr.) Luer †
1
Trichosalpinx triangulipetala
(Ames & Correll) Luer †
1
1
1
1
1
1
15
1
15
1
10
1
20
1
1
Data collection of species plants illegally trade in
Guatemala
Between September 2010 and December 2016,
different markets and plant nurseries of the Guatemala
(Alta Verapaz, Baja Verapaz, Chiquimula, El Progreso,
Guatemala, Jalapa, Quiché and Zacapa) were visited to
identify which species of Pleurothallidinae are being
sold as ornamental plants; additionally their
comparative prices in US$ as well as major and minor
uses were consulted (Table 1).
threatened due to extensive cultivation of corn (Zea
mays L.), beans (Phaseolus vulgaris L.), tomatoes
(Lycopersicon esculentum Mill.), potatoes (Solanum
tuberosum L.), and chili (Capsicum annuum L.). The
other factors impacting the survival of the species have
been uncontrolled wildfires, incentives to replace
native vegetation with Pinus maximinoi H.E.Moore by
the local forest department and the rapid changes in
land use patterns due to extensive cattle ranching in the
locality (Fig. 11). The Pleurothallidinae species that
grow on the stems and branches of the coffee plant or
other trees are indiscriminately removed (scraped)
from the bark, because as coffee growers believe that
orchids are parasitic species and their elimination will
boost coffee production.
Floristic inventory and current conservation status
A total of 211 species and four natural hybrids in 20
genera have been recorded in Guatemala (Table 1,
Figs. 1-8). The genera and number of species are:
Lepanthes (70 species and four hybrids), Stelis (47),
Specklinia (22), Platystele (15), Trichosalpinx (13),
Acianthera (12), Pleurothallis (11), Lankesteriana (6),
Restrepia (6), Anathallis (5), Masdevallia (5),
Dryadella (3), Myoxanthus (3), Octomeria (3),
Dresslerella (2), Lepanthopsis (2), Barbosella (1),
Draculla (1), Kraenzlinella (1), Restrepiella (1),
Scaphosepalum (1) (Fig. 9). Of these taxa, 53 species
and four natural hybrids are known only from a few
localities and are most possibly endemic to Guatemala.
Other 29 species are restricted to southeast Mexico and
Guatemala.
Ornamental potential and illegal trade of
Pleurothallidinae species-Need for sustainable
alternative
The ornamental potential of this subtribe is associated
with the wide diversity of habits, size and shape of the
plants and flowers, the length of the inflorescence and
the number of flowers, coloring patterns of the leaves of
plants and flowers; and their rare floral architecture
(Figs. 1-8). Of the 215 taxa recorded in Guatemala, 78%
(168) are sold as ornamental plants illegally in markets
and nurseries plants (Table 1); mostly in the local
markets of Cobán (Alta Verapaz), Guatemala
(Guatemala), San Marcos (San Marcos). In general, the
Pleurothallidinae species are sold between US$ 5-35
(Table 1). The species of the Lepanthes are most
commonly sold in local markets (67 sold of 70 species)
(Fig. 12); because it is the genus with the highest number
of species and in the pieces of moss that they give off to
sell orchids, several species of Lepanthes grow of
Several of these species usually grow in wet forests and
in the subtropical lower montane rainforests at
elevations of 1100-2600 m (Fig. 10). However, none of
these recently described species from a few collections
or endemic to Guatemala have been evaluated before
for their conservation status, considering that habitats
where it commonly grow have been seriously
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Fig.1: Pleurothallidinae species from Guatemala. A. Acianthera angustifolia. B. A. angustisepala. C. A. circumplexa.
D. A. herrerae. E. A. javieri. F. A. johnsonii. G. A. pubescens. H. A. tikalensis. I. A. violacea. J. Anathallis platystylis.
K. Dracula pusilla. L. Dryadella greenwoodiana. M. Kraenzlinella erinacea. N. Lankesteriana abbreviata.
O. Lepanthes acuminata. P. L. almolongae.
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Fig 2: Pleurothallidinae species from Guatemala. A. Lepanthes any. B. L. appendiculata. C. L. archilae. D. L.
breedlovei. E. L. denticulata. F. L. disticha. G. L. enca-barcenae. H. L. excedens. I. L. fratercula. J. L. geniculata.
K. L. gibberosa. L. L. guatemalensis. M. L. gustavo-romeroi. N. L. hondurensis. O. L. ibanezii. P. L. inaequalis.
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Fig 3: Pleurothallidinae species from Guatemala. A. Lepanthes javieri. B. L. johnsonii. C. L. lenticularis. D. L.
matudana. E. L. migueliana. F. L. mittelstaedtii. G. L. motozintlensis. H. L. oreocharis. I. L. oroscoi. J. L. ordonezii.
K. L. purulhaensis. L. L. quetzalensis. M. L. scopula. N. L. stenophylla. O. L. tecpanica. P. L. williamsii.
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Fig 4 : Pleurothallidinae species from Guatemala. A. Lepanthes yunckeri. B. L. × fonacytii. C. L. × mendietae. D. L. ×
stenosepala. E. Lepanthopsis floripecten. F. Masdevallia chontalensis. G. M. floribunda. H. M. tuerckheimii.
I. Platystele minimiflora. J. P. minimiflora. K. P. narvalis. L. P. oxyglossa. M. P. pedicellaris. N. P. repens. O. P.
sancristobalensis. P. P. stenostachya.
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75
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Diversity of Pleurothallidinae in Guatemala.....
JANUARY-JUNE 2017
Fig 5: Pleurothallidinae species from Guatemala. A. Pleurothallis antonensis. B. P. cardiothallis.
C. P. cardiothallis. D. P. correllii. E. P. correllii. F. P. leucantha. G. P. matudana. H. P. matudana.
I. P. pansamalae. J. P. saccatilabia. K. P. sanchoi. L. P. sanchoi.
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Fig 6: Pleurothallidinae species from Guatemala. A. Specklinia fuegii. B. S. glandulosa. C. S. juddii. D. S. marginata.
E. S. pisinna. F. S. segregatifolia. G. S. spectabilis. H. S. tribuloides. I. Stelis aeolica. J. S. annedamoniae.
K. S. ciliaris. L. S. emarginata. M. S. gracilis. N. S. hymenantha. O. S. immersa. P. S. kellogi.
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JANUARY-JUNE 2017
Fig 7: Pleurothallidinae species from Guatemala. A. Stelis kellogi. B. S. lamprophylla. C. S. microchila. D. S. ornata.
E. S. ovatilabia. F. S. pachyglossa. G. S. parvula. H. S. platystilis. I. S. purpurascens. J. S. quadrifida. K. S. rubens.
L. S. segoviensis. M. S. segoviensis. N. S. tacanensis. O. S. tenebrosa. P. S. megachlamys.
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Fig 8: Pleurothallidinae species from Guatemala. A. Trichosalpinx blaisdellii. B. T. ciliaris. C. T. cortezi.
D. T. greenwoodiana. E. T. pringlei. F. T. pringlei.
Fig. 9 : Number of species of Pleurothallidinae per genera.
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Diversity of Pleurothallidinae in Guatemala.....
JANUARY-JUNE 2017
Fig 10: Habitats of species of Pleurothallidinae in Guatemala. A-B. Cloud forest in Santa María Cahabón, Alta
Verapaz. C-D. Pine-oak forests burned in Caquipec, Alta Verapaz. E-F. Motagua and Chixoy-Polochic faults with
cloud forest in Alta Verapaz, Guatemala.
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Fig 11: Anthropogenic factors and threats for the habitats of Pleurothallidinae species in Guatemala. A-B.
Deforestation of vegetation in Northern Transversal Strip (part of limit between Huehuetenango, Quiché,
Alta Verapaz and Izabal deparments). C. Unmonitored forest fires. D. Changes in land use due to extensive
cattle ranching. E. Firewood.
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Diversity of Pleurothallidinae in Guatemala.....
Fig 12 : Number of species sold in Guatemalan markets.
Fig 13 : Cultivation in vitro of species of Pleurothallidinae.
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EDGAR MÓ et al.,
83
literature, it was observed to be selling in the local
markets and exchanged by different nursery growers.
Unfortunately, the Pleurothallidinae biodiversity in
Guatemala has been seriously jeopardized by different
anthropogenic factors and threats due to their huge
economic and horticultural potentials. According to
Guatemalan law, one way to produce and
commercialize these plants is third generation plant
production. A more viable and sustainable approach
will be to allow the introduction of well monitored in
vitro orchid germination programs as well organic
cultivation of the high value local orchid crops of
Pleurothallidinae species by local inhabitants,
collectors, nursery workers and remote rural
communities including forest fringe residents and
related communities after proper training and
education. Climate change and global warming have
been causing widespread impact on the survival of
several plant species including orchids and their
primary and secondary pollinators (Hegland et al.
2009). In addition, the excessive anthropogenic stress
in the region could have severe long-term impacts on
the survival and natural propagation of the orchid
species of this vulnerable region (Cetzal-Ix et al. 2014;
Cash et al. 2016).
sympatric form with species of diverse genera. Followed
by Stelis (23 of 47), Specklinia (18 of 22); the other
genera registered in Guatemala have fewer species,
however, almost all are commercially sold in local
markets. Surprisingly, for the case of endemic species to
Guatemala, 49 species are sold in the markets between
US$ 10-35, considering that these were recently
described (2001 and 2014) of a few populations in the
department of Alta Verapaz. In this department are
distributed the greater diversity of species of
Pleurothallidinae in Guatemala (82%, 177 of 215)
(Table 1).
Most species of Pleurothallidinae in Guatemala are
extremely vulnerable to exploitation by collectors and
nurserymen. The harvesting of the species by local
populations for illegal nursery trade could result in
serious depletion of several species in the long term if
careful attention is not paid immediately (Cetzal-Ix et
al. 2014). Coupled with the lack of monitoring and
increased encroachments in the forested areas over the
decades by local populations; cattle and livestock
grazing in sensitive habitats; collection of food, fuel,
fiber, fodder and fertilizer resources from the adjacent
forests are regularly building significant and
detrimental anthropogenic pressures within the
sensitive and extremely fragile ecosystem due to
absence of any form legal restrictions, lack of any
credible monitoring and surveillance by the local
conservation agencies and extremely poor forest
management practices (Cetzal-Ix et al. 2014; AlvarezMora et al. 2016). For all the above factors, we
sincerely believe endemic species to Guatemala or
those restricted to Mexico and Guatemala should be
immediately considered and/or recognized as
Vulnerable (VU) species under the current IUCN
directives.
Such a long term sustainable approach can genuinely
improve the local economy, reduce their severe
dependence on the highly vulnerable and scanty forest
resources; and also prevent illegal and non-judicious
force harvesting as well as trafficking of rare and
endemic wild orchid species. This model approach as
suggested by us at one hand can provide some
significant economic opportunities for the
impoverished local communities; and on the other
reduce the anthropogenic pressures on the local forests
for daily sustenance. Our proposed model if followed
sincerely and with proper planning and resources can
help in the conservation of the local, rare, endemic and
vulnerable orchid species from detrimental
anthropogenic pressures.
For example, Stelis anagraciae Archila & Szlach. has
been very recently described by Archila and
Szlachetko (2013) from a population of Alta Verapaz,
Guatemala. According to the authors, it is a litophytic
or epiphytic, rare species. The following year, this
species was discovered by Solano-Gómez (2014) in
Chiapas, Mexico and described as Stelis kaiae Solano
& C. Dietz. We consider the later as a new synonym
and that the distribution of this species extends
approximately to about 200 km. Although this species
is considered rare and is little known in scientific
Cultivation in vitro of species of Pleurothallidinae
There is a great diversity of conditions and means used
in the in vitro cultivation of orchids. However, the
culture medium (liquid or solid) depends on the
species with which it is being worked (Téllez-Velasco
2011). For example, in a liquid medium the
proliferation of protocorms is greater and faster; in
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Diversity of Pleurothallidinae in Guatemala.....
JANUARY-JUNE 2017
seeds; but too strong for preserving fragile seeds. The
product must be less powerful than that of the green
method or more diluted. Using hydrogen peroxide or
calcium hypochlorite and a reduced soaking times
approximately 10 minutes is quite useful. Next, under
the hood, several successive rinses are carried out with
sterile distilled water. Using sterile removable filter that
are specifically adapted to the syringe; seeds should be
washed using the chosen product and repeatedly rinsed
with sterile distilled water, filtered and then scraped with
sterile tool from surface of the filter and finally deposited
in the culture medium.
contrast the solid media favors differentiation. Next,
when the germination process is initiated, it is
advisable to try different media at total or partial
concentrations. For in vitro germination a large
number of plants can be grown in a relatively short
period of time. In addition, the life cycle of the species
should also be seriously considered. The growth in
Pleurothallidinae species to reach adult phase takes
about one to two years; while in orchids of other
subtribes this adult phase can take between 6 to 8 years
to have the final product for successful
commercialization. For this reason, in vitro
reproduction is a viable option for this group of plants,
considering the great global demand. For example,
species of the genus Masdevallia are considered as a
group that requires a specific culture medium on which
to develop (Téllez-Velasco 2011). Here we present an
in vitro culture technique for Lepanthes species, which
is one of the genera with the highest number of species
in the Pleurothallidinae subtribe and best represented
in Guatemala.
The culture media used is the widely used commercial
Phytamax P6668 at ½ concentration; and
supplemented with raw sugar, agar (gelling agent) and
sterile distilled water. The warm solution is poured into
small bottles and sterilized for 15 minutes in the
autoclave at 120°C. Overheating of the medium must
be avoided to retain nutritional qualities. The seeded
flasks are grown at room temperature under artificial
fluorescent light set at 12H by 24H.
For in vitro culture of Lepanthes, the harvested
capsules should be first stored in a paper bag and
correctly labelled. If a plastic tube or bag is used then it
will avoid moisture loss from the capsules and lead to
unfortunate rotting of the seeds. On the contrary; in a
paper bag, the capsule will dry better and open entirely
to release the fine seeds inside the envelope avoiding
any unintended losses. It is challenging to conduct in
vitro operations due to the need for stringent aseptic
environment to avoid frequent contaminations.
However, unlike a Cattleya pod with several million
seeds; there are only few seeds in a Lepanthes pod.
Either of the two methods can be used (Fig. 13):
The first contamination occurs after 3-4 days, due to
poor handling under the laminar hood, in improperly
decontaminated seeds or due to poorly sterilized
medium. Contaminations spread fast and completely
infect the culture media as well as the cultured seeds.
After 15 days, the seeds turn green and begin to grow
and they take on the appearance of small green balls.
When the first leaves and small roots appear, it is time
to transplant the seedlings on to a culture medium
identical and/or supplemented with mashed banana or
fruit juice (30 GR/Litre). All the operations must be
conducted under stringent aseptic conditions. If a
contamination occurs, it is possible to save part of the
plant by quickly and aseptically transplanting healthy
part of the seedling into an unused sterile bottle.
Finally after two years of cultivation; the adult plants
are ready to be transferred into the soil from the tissue
culture media.
Green method: It is the simplest. The fine kernels are
fragile and sensitive to common cleaning chemicals.
The immature pod is harvested before opening i.e.
between 60-90 days (depending on the species). The
pod is washed with sodium hypochlorite, brushed with
a small brush and finally rinsed under the laminar flow
hood with 70 % alcohol. The dried pod is then opened
in the hood with a sterilized scalpel and the seeds are
spread on the surface of the sterile agar medium.
CONCLUSIONS
The ornamental potential and associated prices of the
Pleurothallidinae species vary according to the size of
the flower, number of plants and flowers, and if these
are associated with orchids of other genera. The illegal
sale of these species in Guatemalan in markets and
Dry method: It is more delicate as it is necessary to find
a good cleaning product. It must be strong enough to
destroy the fungi, bacteria and their spores present in the
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EDGAR MÓ et al.,
85
Archila FL, Slachetko DL (2013) Stelis anagraciae
(Orchidaceae), a new pleurothallid species from
Guatemala. Biodiversity: Research and Conservation
29: 31–34
nurseries also depends on whether they are species of
endemic (to Guatemala) or restricted (to Guatemala
and Mexico) distribution, because they become
attractive for being scarce and because they are new
discoveries for the country. We believe that if the local
administration and the forest department do not adopt
proper measures several species of Pleurothallidinae
present in Guatemala will soon by threatened with
extinction.
Cash N, Cetzal-Ix W, Mó E, Vega H, Basu SK (2016)
First record of Lepanthes appendiculata (Orchidaceae,
Pleurothallidinae) from Nicaragua with comments on
the morphological variations, geographical
distribution and conservation status. Check List 12(4):
1–7
A sustainable approach to minimize the local
anthropogenic impacts and to take advantage of
ornamental/horticultural potential of this group of
orchids is to obtain permits for their reproduction
under controlled conditions. Hence, they should be
registered in the National Council of Protected Areas
to allow them to reproduce target orchid species at an
industrial scale (in vitro germination program and
organic cultivation); and at the same time minimize the
impact on endangered wild populations. Since we
consider orchids to be flagship plant species
highlighting rich local biodiversity, the loss of the
orchids from Guatemala will accelerate indirect loss of
several other key species from this highly sensitive and
fragile natural ecosystem. Hence, it is important to
save the local orchid species from extinction and our
proposed model could be a viable alternative for both
ecology and economy; if applied judiciously and
sincerely.
Cetzal-Ix W, Alvarez-Mora R, Basu SK, CosmePérez J, Noguera-Savelli E (2014) Orchid fruit
diversity at Puebla Mexico: A new insight into the
biodiversity of a fragmented ecosystem with need for
conservation and potential for horticultural
exploitations in future. In: Nandwani D (ed.),
Sustainable Horticultural Systems, Sustainable
Development and Biodiversity 2. pp. 207–220.
Springer International Publishing Switzerland. DOI
10.1007/978-3-319-06904-3_9
Endres Júnior D, Hisayuki Sasamori1 M, Droste A
(2014) In vitro propagation of Anathallis adenochila
(Loefgr.) F. Barros (Orchidaceae), a species endemic
to southern and southeastern Brazil. Acta Botanica
Brasilica 28(4): 489–494
Hegland SJ, Nielsen A, Lázaro A, Bjerknes AL,
Totland Ø (2009) How does climate warming affect
plant-pollinator interactions? Ecology Letters 12:
184–195. DOI: 10.1111/j.1461-0248.2008.01269.x
ACKNOWLEDGEMENTS
Higgins WE (2009) Pleurothallidinae: how many
genera? In: Sauleda RP, Sandow LA (eds.)
Proceedings of the 19th World Orchid Conference.
American Printing Arts, Miami, Florida, pp. 425–430
The authors gratefully acknowledge the kind
assistance provided by Rodolfo Hernández, José
Monzón Sierra, Rodolfo Hernández, Sergio Romero,
Carlos Bianchi, German Padilla, Mario Velásquez with
the photographs taken in the field.
Luer CA (2005) Icones Pleurothallidinarum XXVII.
Dryadella and Acronia section MacrophyllaeFasciculatae. Monographs in Systematic Botany from
the Missouri Botanical Garden 103: 1–307
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