Ackerman, 2007. orcquideas invasivas

LANKESTERIANA 7(1-2): 19-21. 2007. INVASIVE ORCHIDS: WEEDS WE HATE TO LOVE? Department of Biology, University of Puerto Rico PO Box 23360 San Juan PR 00931-3360, U.S.A. JAMES D. ACKERMAN Rare species that show habitat specificity and an aversion to habitat disturbance may be common in the Orchidaceae (Tremblay et al. 1998; Bergman et al. 2006). Nonetheless, most orchids may not be in such a critical state and many are, quite frankly, weedy. We may learn much about rare sp
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  Rare species that show habitat specificity and anaversion to habitat disturbance may be common inthe Orchidaceae (Tremblay et al. 1998; Bergman etal. 2006). Nonetheless, most orchids may not be insuch a critical state and many are, quite frankly,weedy. We may learn much about rare species byasking what makes other orchids common andresilient or actually dependent on change. Mostorchids do occur in ephemeral or frequently dis-turbed habitats (Ackerman 1983; Catling 1996)whether they are pastures, roadsides, citrus groves,coffee and tea farms, or simply as epiphytes whosesubstrates, by definition, are temporary and run thegamut from durable tree trunks to short-lived twigs(Johansson 1974).Effective dispersal capabilities are essential for occupying ephemeral habitats. Certainly orchidseed morphology lends itself to the possibility of distance dispersal (Arditti & Ghani 2000; Murren &Ellison 1998). In the West Indies, nearly 60% of the orchid species occur on more than one islandand a floristic affinity analysis has indicated thatgeographical distance for these species is generallynot a barrier to dispersal (Trejo-Torres & Ackerman2001).The combination of mobility and widespread preference for ephemeral habitats appears to havegiven orchid populations a degree of resiliency thatis generally underappreciated. We all know thatdeforestation, or habitat destruction is a common problem not only in the tropics but elsewherethroughout the world. A prime example is PuertoRico where 95% of the forest cover was cut by theearly 1940’s (Brash 1987; Lugo et al. 1993 cited byFigueroa Colón 1996), yet the number of orchidspecies lost from the flora has been less than 5%.Since then, forest recovery has been substantial andsome orchid species have responded positively tothe re-growth, a few becoming quite abundant insecondary habitats (Ackerman & Galarza-Pérez1991).Orchids with rapidly expanding populationsinclude natives, but non-natives everywhere aremaking their appearance (Table 1). In fact, theglobal compendium of weeds ( lists over 90 orchid weeds! In PuertoRico, a number of non-native orchids have persistedfor a long time, but only recently have they becomeaggressive taking on weed-like characteristics.Such a demographic pattern is very typical of inva-sive species.What makes an orchid weedy and invasive?Many plants that are classified as weeds have asuite of characteristics associated with colonizationcapabilities, and some of these features characterizeorchids in general: abundant seed production(although in orchids effective population sizes may be small), distance dispersal, and weak competitivecapabilities. Rapid development, autogamy andapomixis are also common features of weeds, butthese are certainly not common features of orchids.From a sample of weedy orchids, we find a com- plete spectrum of breeding systems (e.g., Sun1997), from apomictic or autogamous to outcross-ing, and plants of the latter may be either self-com- patible or -incompatible.It is difficult to find a common thread among theinvasive orchids. Some are understory plants; per-haps most prefer grassy roadsides, while a few othersare epiphytes. Some are autogamous but othersattract local pollinators with nectar rewards or bydeceit, with pollination systems not unlike that of local species. Answers may rest not only with thedistribution of appropriate habitat, but also with the LANKESTERIANA  7(1-2): 19-21. 2007. INVASIVE ORCHIDS: WEEDS WE HATE TO LOVE? J AMES D. A CKERMANDepartment of Biology, University of Puerto RicoPO Box 23360San Juan PR 00931-3360, U.S.A.   players in the orchids’ symbiotic relationships: polli-nators and mycorrhizal fungi. Widespread specieseither specialize on widespread “partners” or arecatholic with whom they play or exploit (cf.Bascompte et al. 2003; Vázquez & Aizen 2004). Theasymmetrical relationship between plants and their  pollinators is well documented, but the relationship between orchids and their mycorrhizal symbionts isonly just beginning to be revealed (e.g., Otero et al. 2002, 2004; Taylor  et al. 2003). What do rare speciesdo? Again, we do not know this entirely but we can predict that constraints of specificity may have a role,whether it is the habitat, the pollinators, their mycor-rhizal associations, or some combination of the threeremains to be seen.Finally, we are faced with an orchidaceous dilem-ma: can non-native, marquee taxa be so bad? Dothey exclude native taxa or disrupt natural ecosys-tems or are they benign? Do we encourage, tolerateor fight such intrusions to our sovereign soil? L ITERATURE C ITED Ackerman, J.D . 1983. On the evidence for a primitivelyepiphytic habit in orchids. Syst. Bot. 8: 474-477.Ackerman, J.D., J.C. Trejo Torres & Y. Crespo Chuy.In press. Orchids of the West Indies: predictability of diversity and endemism. J. Biogeography.Ackerman, J.D. & M. Galarza-Pérez. 1991. Patterns andmaintenance of extraordinary variation in theCaribbean orchid, Tolumnia ( Oncidium ) variegata. Syst. Bot. 16: 182-194.Arditti, J. & A.K.A. Ghani. 2000. Numerical and physi-cal properties of orchid seeds and their biological Species  Arundina graminifolia Dendrobium crumenatum Epidendrum radicansOeceoclades maculata Phaius tancarvilleaeSpathoglottis plicataVanilla planifoliaVanilla pompona Zeuxine strautematica Native India, Nepal, China, SEAsia to IndonesiaIndia, Bangladesh,China, Burma, Thailand,Vietnam, Indonesia,Malaysia, Philippines,AustraliaMexico, CentralAmerica, ColombiaAfricaIndia, Nepal, China, SEAsia to Phillipines, SouthPacific IslandsIndia, SE Asia NewGuinea, New Caledoniato PhillipinesMexico, CentralAmerica?Mexico, CentralAmerica, South AmericaSri Lanka, India, SEAsia, Java, Phillipines,Taiwan, Japan Non-native Hawaii, Puerto Rico,GuadeloupePuerto Rico,GuadeloupeCuba, Puerto RicoSouth America,Central America,West Indies, FloridaHawaii, Cuba,Jamaica, Puerto RicoHawaii, Cuba, PuertoRico, Virgin Islands,Lesser AntillesPuerto Rico, WestIndies, Central &South AmericaPuerto Rico, Lesser Antilles?Southern USA,Bahamas, Cuba,Jamaica, Puerto Rico Breeding systemOutcrossingDeceptionOutcrossing rewardOutcrossingdeceptionAutogamousOutcrossing?DeceptionAutogamousOutcrossing deception*Outcrossing deception*Apomictic Habitat Open disturbedOpenOpen disturbedShadyOpen to shady disturbedOpen, disturbed groundForest disturbed habitatsForest disturbed habitatsOpen disturbed *The two vanillas may be reward plants at least for the male euglossine bee pollinators in Central America . T ABLE 1. Orchid species naturalized in Puerto Rico. 3 RD IOCC PROCEEDINGS 20 LANKESTERIANA  7(1-2), marzo 2007  . ©Universidad de Costa Rica, 2007  .  implications. New Phytol. 145: 367-421.Bascompte, J., P. Jordano, C.J. Melián & J.M. Olesen.2003. The nested assembly of plant-animal mutualisticnetworks. Proc. Nat. Acad. Sc. (USA) 100: 9383-9387.Bergman, E., J.D. Ackerman, J. Thompson & J.K.Zimmerman. 2006. Land use history affects the dis-tribution of the saprophytic orchid Wullschlaegeliacalcarata in Puerto Rico. Biotropica 38: 492-499.Brash, A. 1987. The history of avian extinction and forestconversion on Puerto Rico. Biol. Conserv. 39: 97-111.Catling, P.M. 1996. Conservation strategy. Pages 11-23 in : IUCN/SSC Orchid Specialist Group, Orchids— status survey and conservation action plan. IUCNGland, Switzerland and Cambridge, UK.Figueroa Colón, J.C. 1996. Phytogeographical trends, centersof high species richness and endemism, and the questionof extinctions in the native flora of Puerto Rico. Ann. NewYork Acad. Sc. 776: 89-102.Johansson, D. 1974. Ecology of West African epiphytes.Acta Phytogeog. Suec. 59: 1-129.IUCN/SSC Orchid Specialist Group. 1996. Orchids— status survey and conservation action plan. IUCNGland, Switzerland and Cambridge, UK.Lugo, A., J. Parrotta & S. Brown. 1993. Loss in speciescaused by deforestation and their recovery throughmanagement. Ambio 22(2-3): 106-109.Murren, J.C. & A.M. Ellison. 1998. Seed dispersal char-acteristics of   Brassavola nodosa (Orchidaceae).Amer. J. Bot. 85: 675-680.Otero J.T., J.D. Ackerman& P. Bayman. 2002.Diversity and host specificity of endophytic  Rhizoctonia -like fungi from tropical orchids. Amer. J.Bot. 89: 1852-1858.Otero J.T., J. D. Ackerman & P. Bayman. 2004.Differences in mycorrhizal preferences between twotropical orchids. Molec. Ecol.13: 2393–2404.Sun, M. 1997. Genetic diversity in three colonizingorchids with contrasting mating systems. Amer. J.Bot. 84: 224-232.Taylor, D.L., T.D. Bruns, T.M. Szaro & S.A. Hodges.2003. Divergence in mycorrhizal specialization within  Hexalectris spicata (Orchidaceae), a nonphotosynthet-ic desert orchid. Amer. J. Bot. 90: 1168-1179.Trejo-Torres, J.C. & J.D. Ackerman. 2001.Biogeographic affinities of Caribbean Orchidaceae based on parsimony analyses of shared species. J.Biogeogr. 28: 775-794.Tremblay, R.L., J.K. Zimmerman, L. Lebrón, P.Bayman, I. Sastre, F. Axelrod & J. Alers-García.1998. Host specificity and low reproductive successin the rare endemic Puerto Rican orchid  Lepanthescaritensis (Orchidaceae). Biol. Conserv. 85: 297-304.Vázquez, D.P. & M.A. Aizen. 2004. Asymmetric spe-cialization: a pervasive feature of plant-pollinator interactions. Ecology 85: 1251-1257. A CKERMAN - Invasive orchids21 James D. Ackerman is Professor of the University of Puerto Rico at Río Piedras. He is a biologist with broad interests, but focuses on the ecology, systematics and evolution of Orchidaceae. His present interests include studies on the rela-tionship between land use history and orchid distributions, orchid biogeography, invasive orchids, and their mycor-rhizal relationships. LANKESTERIANA  7(1-2), marzo 2007  . ©Universidad de Costa Rica, 2007  .

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