83 research outputs found
Preventing Establishment: An Inventory of Introduced Plants in Puerto Villamil, Isabela Island, Galapagos
As part of an island-wide project to identify and eradicate potentially invasive plant species before they become established, a program of inventories is being carried out in the urban and agricultural zones of the four inhabited islands in Galapagos. This study reports the results of the inventory from Puerto Villamil, a coastal village representing the urban zone of Isabela Island. We visited all 1193 village properties to record the presence of the introduced plants. In addition, information was collected from half of the properties to determine evidence for potential invasiveness of the plant species. We recorded 261 vascular taxa, 13 of which were new records for Galapagos. Most of the species were intentionally grown (cultivated) (73.3%) and used principally as ornamentals. The most frequent taxa we encountered were Cocos nucifera (coconut tree) (22.1%) as a cultivated plant and Paspalum vaginatum (salt water couch) (13.2%) as a non cultivated plant. In addition 39 taxa were naturalized. On the basis of the invasiveness study, we recommend five species for eradication (Abutilon dianthum, Datura inoxia, Datura metel, Senna alata and Solanum capsicoides), one species for hybridization studies (Opuntia ficus-indica) and three species for control (Furcraea hexapetala, Leucaena leucocephala and Paspalum vaginatum)
Back from a Predicted Climatic Extinction of an Island Endemic: A Future for the Corsican Nuthatch
The Corsican Nuthatch (Sitta whiteheadi) is red-listed as vulnerable to extinction by the IUCN because of its endemism, reduced population size, and recent decline. A further cause is the fragmentation and loss of its spatially-restricted favourite habitat, the Corsican pine (Pinus nigra laricio) forest. In this study, we aimed at estimating the potential impact of climate change on the distribution of the Corsican Nuthatch using species distribution models. Because this species has a strong trophic association with the Corsican and Maritime pines (P. nigra laricio and P. pinaster), we first modelled the current and future potential distribution of both pine species in order to use them as habitat variables when modelling the nuthatch distribution. However, the Corsican pine has suffered large distribution losses in the past centuries due to the development of anthropogenic activities, and is now restricted to mountainous woodland. As a consequence, its realized niche is likely significantly smaller than its fundamental niche, so that a projection of the current distribution under future climatic conditions would produce misleading results. To obtain a predicted pine distribution at closest to the geographic projection of the fundamental niche, we used available information on the current pine distribution associated to information on the persistence of isolated natural pine coppices. While common thresholds (maximizing the sum of sensitivity and specificity) predicted a potential large loss of the Corsican Nuthatch distribution by 2100, the use of more appropriate thresholds aiming at getting closer to the fundamental distribution of the Corsican pine predicted that 98% of the current presence points should remain potentially suitable for the nuthatch and its range could be 10% larger in the future. The habitat of the endemic Corsican Nuthatch is therefore more likely threatened by an increasing frequency and intensity of wildfires or anthropogenic activities than by climate change
Influence of phenological barriers and habitat differentiation on the population genetic structure of the balearic endemic Rhamnus ludovici-salvatoris Chodat and R. alaternus L
[EN] Rhamnus ludovici-salvatoris, endemic to the Gymnesian Islands, coexists with the related and widespread R. alaternus in Mallorca and Menorca. In both species, the population genetic structure using RAPD, and flowering during a 3-year period to check for possible phenological barriers, were analyzed. Rhamnus ludovici-salvatoris showed lower genetic diversity and stronger population structure than R. alaternus, the Cabrera population being less diverse and the most differentiated. Rhamnus ludovici-salvatoris flowered one month later, although flowering of both species coincided sporadically. These congeners seem to have diverged through isolation by time and differentiation in habitat. The population genetic structure of R. ludovici-salvatoris could mainly be due to the existence of small populations on the one hand, and a gene flow caused by rare hybridization events on the other, which may also explain the presence of morphologically intermediate individuals in Menorca. The conservation of R. ludovici-salvatoris populations may include population reinforcements and other in situ interventions.Ferriol Molina, M.; Llorens García, L.; Gil, L.; Boira Tortajada, H. (2009). Influence of phenological barriers and habitat differentiation on the population genetic structure of the balearic endemic Rhamnus ludovici-salvatoris Chodat and R. alaternus L. Plant Systematics and Evolution. 277(1-2):105-116. doi:10.1007/s00606-008-0110-3S1051162771-2Affre L, Thompson JD, Debussche M (1997) Genetic structure of continental and island populations of the Mediterranean endemic Cyclamen balearicum (Primulaceae). Amer J Bot 84(4): 437–451BOIB (2005) Decreto 75/2005. BOIB 106: 29–32Bolmgren K, Oxelman B (2004) Generic limits in Rhamnus L. s.l. (Rhamnaceae) inferred from nuclear and chloroplast DNA sequence phylogenies. Taxon 53(2):383–390Bolòs O, Molinier R (1958) Recherches phytosociologiques dans l’île de Majorque. Collectanea Botanica 34:699–865Cardona MA (1979) Consideracions sobre l’endemisme i l’origen de la flora de las Illes Balears. Butlletí del Institut Catalá de Historia Natural 44 (Sec. Bot. 3):7–15Cardona MA, Contandriopoulos J (1979) Endemism and evolution in the islands of the Western Mediterranean. In: Bramwell D (ed) Plants and islands. Academic Press, London, pp 133–169Chodat L (1924) Contributions à la Géo-Botanique de Majorque. PhD Thesis, Université de Genève—Institut de Botanique, SwitzerlandCollins D, Mill RR, Moller M (2003) Species separation of Taxus baccata, T. canadensis, and T. cuspidata (Taxaceae) and origins of their reputed hybrids inferred from RAPD and cpDNA data. Amer J Bot 90(2):175–182Cronk QCB (1997) Islands: stability, diversity, conservation. Biodivers Conserv 6(3):477–493Doyle JJ, Doyle JL (1990) Isolation of plant DNA from fresh tissue. Focus 12:13–15Ducarme V, Wesselingh RA (2005) Detecting hybridization in mixed populations of Rhinanthus minor and Rhinanthus angustifolius. Folia Geobot 40(2/3):151–161Englishloeb GM, Karban R (1992) Consequences of variation in flowering phenology for seed head herbivory and reproductive success in Erigeron glaucus (Compositae). Oecologia 89:588–595Gautier F, Caluzon G, Suk JP, Violanti D (1994) Age et durée de la crise de salinité Messinienne. Comptes Rendus de l’Académie des Sciences de Paris 318:1103–1109Gerard PR, Fernandez-Manjarres JF, Frascaria-Lacoste N (2006) Temporal cline in a hybrid zone population between Fraxinus excelsior L. and Fraxinus angustifolia Vahl. Molec Ecol 15:3655–3667Gil L, Llorens L, Tébar FJ, Costa M (1995) La vegetación de la isla de Cabrera. In: Guía de la excursión geobotánica de las XV Jornadas de Fitosociología. Datos sobre la vegetación de Cabrera. Palma de Mallorca: Universitat de les Illes Balears, pp 51–77Gulías J, Flexas J, Abadía A, Medrano H (2002) Photosynthetic responses to water deficit in six Mediterranean sclerophyll species: possible factors explaining the declining distribution of Rhamnus ludovici-salvatoris, and endemic Balearic species. Tree Physiol 22:687–697Gulías J, Traveset A, Riera N, Mus M (2004) Critical stages in the recruitment process of Rhamnus alaternus L. Ann Bot 93:723–731Gustafsson S, Sjögren-Gulve P (2002) Genetic diversity in the rare orchid, Gymnadenia odoratissima and a comparison with the more common congener, G. conopsea. Conserv Genet 3:225–234Gustafsson S (2003) Population genetic analyses in the orchid genus Gymnadenia—a conservation genetic perspective. PhD Thesis, Uppsala University, SwedenGustafsson S, Lönn M (2003) Genetic differentiation and habitat preference of flowering-time variants within Gymnadenia conopsea. Heredity 91:284–292Harris W (1996) Genecological aspects of flowering patterns of populations of Kunzea ericoides and K. sinclairii (Myrtaceae). New Zealand J Bot 34:333–354Hendry AP, Dray T (2005) Population structure attributable to reproductive time: isolation by time and adaptation by time. Molec Ecol 14:901–916Hosokawa K, Minami M, Kawahara K, Nakamura I, Shibata T (2000) Discrimination among three species of medicinal Scutellaria plants using RAPD markers. Pl Med 66:270–272Huang Z, Liu L, Zhou T, Ju B (2005) Effects of environmental factors on the population genetic structure in chukar partridge (Alectoris chukar). J Arid Environ 62:427–434Juan A, Crespo MB, Cowan RS, Lexer C, Fay F (2004) Patterns of variability and gene flow in Medicago citrina, an endangered endemic of islands in the western Mediterranean, as revealed by amplified fragment length polymorphism (AFLP). Molec Ecol 13:2679–2690Krijgsman W, Hilgen FJ, Raffi I, Sierro FJ, Wilson DS (1999) Chronology, causes and progression of the Messinian salinity crisis. Nature 400:652–655Lamont BB, He T, Enright NJ, Krauss SL, Miller BP (2003) Anthropogenic disturbance promotes hybridization between Banksia species by altering their biology. J Evol Biol 16:551–557Lennartsson T (1997) Seasonal differentiation—a conservative reproductive barrier in two grassland Gentianella (Gentianaceae) species. Pl Syst Evol 208:45–69Martinez-Solis I, Iranzo J, Estrelles E, Ibars AM (1993) Leaf domatia in the section Alaternus (Miller) DC. of the genus Rhamnus (Rhamnaceae). Bot J Linn Soc 112:311–318McIntosh ME (2002) Flowering phenology and reproductive output in two sister species of Ferocactus (Cactaceae). Pl Ecol 159:1–13Nei M (1973) Analysis of gene diversity in subdivided populations. Proc Natl Acad Sci USA 70:3321–3323Nei M (1978) Estimation of average heterozigosity and genetic distance from a small number of individuals. Genetics 89:583–590Nei M, Li W (1979) Mathematical model for studying genetic variation in terms of restriction endonucleases. Proc Natl Acad Sci USA 79:5269–5273Nybom H, Bartish IV (2000) Effects of life history traits and sampling strategies on genetic diversity estimates obtained with RAPD markers in plants. Perspect Pl Ecol Evol Syst 3(2):93–114Oostermeijer JGB, Luijten SH, Ellis-Adam AC, den Nijs JCM (2002) Future prospects for the rare, late-flowering Gentianella germanica and Gentianopsis ciliata in Dutch nutrient-poor calcareous grasslands. Biol Conserv 104:339–350Pease CM, Lande R, Bull JJ (1989) A model of population growth, dispersal and evolution in a changing environment. Ecology 70(6):1657–1664Perron M, Gordon AG, Bousquet J (1995) Species-specific RAPD fingerprints for the closely related Picea mariana and P. rubens. Theor Appl Genet 91:142–149Pierce S, Ceriani RM, Villa M, Cerabolini B (2006) Quantifying relative extinction risks and targeting intervention for the orchid flora of a natural park in the European prealps. Conserv Biol 20(6):1804–1810Richardson JE, Fay MF, Cronk QCB, Bowman D, Chase MW (2000) A phylogenetic analysis of Rhamnaceae using rbcL and trnL-F plastid DNA sequences. Amer J Bot 87(9):1309–1324Roselló JA, Sáez L (2000) Index Balearicum: an annotated check-list of the vascular plants described from the Balearic Islands. Collect Bot 25(1):3–203Roselló JA, Cebrián MC, Mayol M (2002) Testing taxonomic and biogeographical relationships in a narrow mediterranean endemic complex (Hippocrepis balearica) using RAPD markers. Ann Bot 89:321–327Sales E, Nebauer SG, Mus M, Segura J (2001) Population genetic study in the Balearic plant species Digitalis minor (Scrophulariaceae) using RAPD markers. Amer J Bot 88(10):1750–1759Sherwin WB, Moritz C (2000) Managing and monitoring genetic erosion. In: Young AG, Clarke GM (eds) Genetics, demography and viability of fragmented populations. Cambridge University Press, Cambridge, pp 9–34Sneath PHA, Sokal RR (1973) Numerical taxonomy. Freeman and Co., San FranciscoTraveset A, Gulías J, Riera N, Mus M (2003) Transition probabilities from pollination to establishment in a rare dioecious shrub species (Rhamnus ludovici-salvatoris) in two habitats. J Ecol 91:427–437Tutin TG, Heywood VH, Burges NA, Valentine DH, Walters SM, Webb DA (eds) (2001) Flora Europaea, vol 2. Rosaceae to Umbelliferae. Cambridge University Press, CambridgeWright S (1931) Evolution in Mendelian populations. Genetics 16:97–159Zimmerman M (1980a) Reproduction in Polemonium: pre-dispersal seed predation. Ecology 61:502–506Zimmerman M (1980b) Reproduction in Polemonium: competition for pollinators. Ecology 61:497–50
A Battle Lost? Report on Two Centuries of Invasion and Management of Lantana camara L. in Australia, India and South Africa
Recent discussion on invasive species has invigorated the debate on strategies to manage these species. Lantana camara L., a shrub native to the American tropics, has become one of the worst weeds in recorded history. In Australia, India and South Africa, Lantana has become very widespread occupying millions of hectares of land. Here, we examine historical records to reconstruct invasion and management of Lantana over two centuries and ask: Can we fight the spread of invasive species or do we need to develop strategies for their adaptive management? We carried out extensive research of historical records constituting over 75% of records on invasion and management of this species in the three countries. The records indicate that governments in Australia, India and South Africa have taken aggressive measures to eradicate Lantana over the last two centuries, but these efforts have been largely unsuccessful. We found that despite control measures, the invasion trajectory of Lantana has continued upwards and that post-war land-use change might have been a possible trigger for this spread. A large majority of studies on invasive species address timescales of less than one year; and even fewer address timescales of >10 years. An understanding of species invasions over long time-scales is of paramount importance. While archival records may give only a partial picture of the spread and management of invasive species, in the absence of any other long-term dataset on the ecology of Lantana, our study provides an important insight into its invasion, spread and management over two centuries and across three continents. While the established paradigm is to expend available resources on attempting to eradicate invasive species, our findings suggest that in the future, conservationists will need to develop strategies for their adaptive management rather than fighting a losing battle
Globally distributed Xyleborus species reveal recurrent intercontinental dispersal in a landscape of ancient worldwide distributions
Critical Invasion Science: Weeds, Pests, and Aliens
The study of invasive plants and animals calls strongly for a critical approach due to the deeply social nature of invasion landscapes, the power relations affecting the science of invasions, and the differential impacts of weed or pest control on lives and landscapes. I first explore what a “critical” invasion science means. Then I investigate several aspects of invasion science ripe for critical analysis: the history of the science (to understand what the science is doing and why), the terminology and categories of analysis, and the highly contested social, political, and ethical context within which invasion management takes place. I conclude with four proposals for further work in critical invasion science and examples of the types of questions it might ask
What Is the Meaning of Extreme Phylogenetic Diversity? The Case of Phylogenetic Relict Species
Genetic structure of dioecious and trioecious Salix myrsinifolia populations at the border of geographic range
Aspects of sexual failure in the reproductive process of a rare bulbiliferous plant in subtropical Asia, Titanotrichum oldhamii (Gesneriaceae).
- …