7 research outputs found
Comparison of the vascular exotic flora in continental islands: Sardinia (Italy) and Balearic Islands (Spain)
[EN] This paper provides a comparison of the vascular exotic flora of Sardinia and that of the Balearic Islands, both territories belonging to the Western Mediterranean biogeographic subregion. The study has recorded 531 exotic taxa in Sardinia (18.8% of the total flora) while 360(19%) in the Balearic Islands; 10 are new to Sardinia (3 of which for Italy) and 29 to the Balearic Islands. The alien flora of Sardinia is included in 99 families; Fabaceae is the richest (49 taxa), followed by Poaceae (33) and Asteraceae (31) while in the Balearic Islands in 90 families, with a predominance of Fabaceae (32), Asteraceae (31) and Poaceae (27). The comparison of the biological spectra reveals that in Sardinia phanerophytes are the most represented in Sardinia and therophytes in the Balearic Islands. A detailed analysis shows that most of the exotic taxa (246) are shared by both territories with a clear dominance of neophytes rather than archaeophytes. A study of the geographical origin shows supremacy of the American element over the Mediterranean. The majority of introduced exotic taxa are a result of intentional human introductions (76% SA, 77% BL), mainly for ornamental use (43% SA, 45% BL). The most occupied habitats are the semi-natural, agricultural and synanthropic for both territories, but attending to invasive plants, coastal habitats in Sardinia and wetlands in the Balearic Islands are the most sensitive. A part of the work deals with the causes of fragility and low resilience of the different habitats.[ES] Se presenta un estudio comparativo de la flora vascular exótica
de Cerdeña y de las Baleares, dos sistemas insulares pertenecientes
a la subregión biogeográfica Mediterránea Occidental.
En Cerdeña se han contabilizado 531 táxones exóticos (18,8%
del total de su flora), mientras que en las Baleares 360 (19%),
siendo 10 citas nuevas para Cerdeña (3 de las cuales para Italia)
y 29 para Baleares. La flora exótica de Cerdeña está incluida en
99 familias, y Fabaceae es la más rica (49 táxones), seguida por
Poaceae (33) y Asteraceae (31), frente a 90 familias para las Baleares,
con predominio de Fabaceae (32), Asteraceae (31) y Poaceae
(27). Se han encontrado diferencias respecto a los tipos
biológicos, con un predominio de los fanerófitos en Cerdeña y
de los terófitos en las Baleares. Un análisis detallado muestra
que buena parte de estos táxones (246) son compartidos por
ambos territorios, así como una dominancia de los neófitos frente
a los arqueófitos. Respecto al origen geográfico, ambos territorios
presentan una preeminencia del elemento americano sobre
el mediterráneo. En referencia a las vías de introducción, la
mayor parte de los táxones ha sido introducida por parte del
hombre de forma intencionada (76% SA, 77% BL) en particular
para uso ornamental (43% SA, 45% BL). Los hábitats más afectados
son los seminaturales, agrícolas y sinantrópicos en ambos
territorios, aunque atendiendo a la flora invasora, son los litorales
los más sensibles en Cerdeña y los humedales en Baleares.
Una parte del trabajo aborda las causas de la fragilidad y baja resiliencia
de los diferentes hábitats.Podda, L.; Fraga Arguimbau, P.; Mayoral García-Berlanga, O.; Mascia, F.; Bacchetta, G. (2010). Comparación de la flora exótica vascular en sistemas de islas continentales: Cerdeña (Italia) y Baleares (España). Anales del Jardín Botánico de Madrid. 67(2):157-176. doi:10.3989/ajbm.2251S157176672Mack, R. N., Simberloff, D., Mark Lonsdale, W., Evans, H., Clout, M., & Bazzaz, F. A. (2000). BIOTIC INVASIONS: CAUSES, EPIDEMIOLOGY, GLOBAL CONSEQUENCES, AND CONTROL. Ecological Applications, 10(3), 689-710. doi:10.1890/1051-0761(2000)010[0689:bicegc]2.0.co;2Madon*, O., & Médail, F. (1997). Plant Ecology, 129(2), 189-199. doi:10.1023/a:1009759730000Mansion, G., Rosenbaum, G., Schoenenberger, N., Bacchetta, G., Rosselló, J. A., & Conti, E. (2008). Phylogenetic Analysis Informed by Geological History Supports Multiple, Sequential Invasions of the Mediterranean Basin by the Angiosperm Family Araceae. Systematic Biology, 57(2), 269-285. doi:10.1080/10635150802044029MILBAU, A., & STOUT, J. C. (2008). Factors Associated with Alien Plants Transitioning from Casual, to Naturalized, to Invasive. Conservation Biology, 22(2), 308-317. doi:10.1111/j.1523-1739.2007.00877.xO’Dowd, D. J., Green, P. T., & Lake, P. S. (2003). Invasional «meltdown» on an oceanic island. Ecology Letters, 6(9), 812-817. doi:10.1046/j.1461-0248.2003.00512.xOlesen, J. M., Eskildsen, L. I., & Venkatasamy, S. (2002). Invasion of pollination networks on oceanic islands: importance of invader complexes and endemic super generalists. Diversity Distributions, 8(3), 181-192. doi:10.1046/j.1472-4642.2002.00148.xPauchard, A., Cavieres, L. A., & Bustamante, R. O. (2004). Comparing alien plant invasions among regions with similar climates: where to from here? Diversity and Distributions, 10(5-6), 371-375. doi:10.1111/j.1366-9516.2004.00116.xPyšek, P., Richardson, D. M., Rejmánek, M., Webster, G. L., Williamson, M., & Kirschner, J. (2004). Alien plants in checklists and floras: towards better communication between taxonomists and ecologists. TAXON, 53(1), 131-143. doi:10.2307/4135498Randall, J. M., Morse, L. E., Benton, N., Hiebert, R., Lu, S., & Killeffer, T. (2008). The Invasive Species Assessment Protocol: A Tool for Creating Regional and National Lists of Invasive Nonnative Plants that Negatively Impact Biodiversity. Invasive Plant Science and Management, 1(1), 36-49. doi:10.1614/ipsm-07-020.1REASER, J. K., MEYERSON, L. A., CRONK, Q., DE POORTER, M., ELDREGE, L. G., GREEN, E., … VAIUTU, L. (2007). Ecological and socioeconomic impacts of invasive alien species in island ecosystems. Environmental Conservation, 34(2), 98-111. doi:10.1017/s0376892907003815REICHARD, S. H., & WHITE, P. (2001). Horticulture as a Pathway of Invasive Plant Introductions in the United States. BioScience, 51(2), 103. doi:10.1641/0006-3568(2001)051[0103:haapoi]2.0.co;2Richardson, D. M., & Pyšek, P. (2006). Plant invasions: merging the concepts of species invasiveness and community invasibility. Progress in Physical Geography: Earth and Environment, 30(3), 409-431. doi:10.1191/0309133306pp490prRichardson, D. M., Pysek, P., Rejmanek, M., Barbour, M. G., Panetta, F. D., & West, C. J. (2000). Naturalization and invasion of alien plants: concepts and definitions. Diversity Distributions, 6(2), 93-107. doi:10.1046/j.1472-4642.2000.00083.xRosenbaum, G., Lister, G. S., & Duboz, C. (2002). Reconstruction of the tectonic evolution of the western Mediterranean since the Oligocene. Journal of the Virtual Explorer, 08. doi:10.3809/jvirtex.2002.00053Sanz-Elorza, M., Mateo, R. G., & Bernardo, F. G. (2008). The historical role of agriculture and gardening in the introduction of alien plants in the western Mediterranean. Plant Ecology, 202(2), 247-256. doi:10.1007/s11258-008-9474-2Schippers, P., van Groenendael, J. M., Vleeshouwers, L. M., & Hunt, R. (2001). Herbaceous plant strategies in disturbed habitats. Oikos, 95(2), 198-210. doi:10.1034/j.1600-0706.2001.950202.xSchnitzler, A., Hale, B. W., & Alsum, E. M. (2007). Examining native and exotic species diversity in European riparian forests. Biological Conservation, 138(1-2), 146-156. doi:10.1016/j.biocon.2007.04.010Speranza, F., Villa, I. M., Sagnotti, L., Florindo, F., Cosentino, D., Cipollari, P., & Mattei, M. (2002). Age of the Corsica–Sardinia rotation and Liguro–Provençal Basin spreading: new paleomagnetic and Ar/Ar evidence. Tectonophysics, 347(4), 231-251. doi:10.1016/s0040-1951(02)00031-8Suehs, C. M., Affre, L., & Médail, F. (2003). Invasion dynamics of two alien Carpobrotus (Aizoaceae) taxa on a Mediterranean island: I. Genetic diversity and introgression. Heredity, 92(1), 31-40. doi:10.1038/sj.hdy.6800374Towns, D. R., & Ballantine, W. J. (1993). Conservation and restoration of New Zealand Island ecosystems. Trends in Ecology & Evolution, 8(12), 452-457. doi:10.1016/0169-5347(93)90009-eVila, M., Tessier, M., Suehs, C. M., Brundu, G., Carta, L., Galanidis, A., … Hulme, P. E. (2006). Local and regional assessments of the impacts of plant invaders on vegetation structure and soil properties of Mediterranean islands. Journal of Biogeography, 33(5), 853-861. doi:10.1111/j.1365-2699.2005.01430.xVITOUSEK, P. M., WALKER, L. R., WHITEAKER, L. D., MUELLER-DOMBOIS, D., & MATSON, P. A. (1987). Biological Invasion by Myrica faya Alters Ecosystem Development in Hawaii. Science, 238(4828), 802-804. doi:10.1126/science.238.4828.802Wittenberg, R., & Cock, M. J. W. (Eds.). (2001). Invasive alien species: a toolkit of best prevention and management practices. doi:10.1079/9780851995694.000
The natural radioactivity map of Umbria (Italy): a multipurpose tool for environmental understanding
We present the first map of the terrestrial natural radioactivity, with relative uncertainties, of the Umbria Region (Italy). The total specific activity is derived from the abundances of natural radionuclides (40K, 238U, 232Th) measured in 283 rock and 14 soil samples using a high-purity germanium (HPGe) γ-ray spectrometer while an area accounting for ∼20% of the territory was investigated through large-volume NaI detectors mounted on an ultralight aircraft. A multivariate estimation method (Collocated CoKriging) for interpolating sparse γ-ray data considering the well-known geological information as ancillary was applied. This regional radioactivity map is a powerful tool for a number of different applications: (i) for the identification of distinctive lithological characteristics on the basis of radioactive content; (ii) for the definition of the natural baseline of outdoor effective dose rate in the event of a radiological contamination; (iii) for Green Building indoor air quality certifications, through the estimation of the radon flux derived from uranium content in the site location; (iv) for the stone industry, through the radiological characterization of building materials extracted from quarries in the investigated area, following the export regulations of the international market. Finally, the geo-environmental data presented are also available on an open access platform, supporting the general public understanding and the local authorities decision making
Hyperon signatures in the PANDA experiment at FAIR
We present a detailed simulation study of the signatures from the sequential decays of the triple-strange pbar p -> Ω+Ω- -> K+ΛbarK- Λ -> K+pbarπ+K-pπ- process in the PANDA central tracking system with focus on hit patterns and precise time measurement. We present a systematic approach for studying physics channels at the detector level and develop input criteria for tracking algorithms and trigger lines. Finally, we study the beam momentum dependence on the reconstruction efficiency for the PANDA detector
A multi-element psychosocial intervention for early psychosis (GET UP PIANO TRIAL) conducted in a catchment area of 10 million inhabitants: study protocol for a pragmatic cluster randomized controlled trial
Multi-element interventions for first-episode psychosis (FEP) are promising, but have mostly been conducted in non-epidemiologically representative samples, thereby raising the risk of underestimating the complexities involved in treating FEP in 'real-world' services