Ficha de avaliação EICAT
Rubus ulmifolius
MO · Moderado
Avaliação histórica recuperada de registros do SIGEEI. A estrutura e os campos foram preservados; a confirmação permanece pendente.
Identificação e síntese
Nomenclatura e vinculação
O nome original da avaliação é preservado. O nome aceito e os sinônimos servem para localização e conciliação, sem sobrescrever o registro EICAT histórico.
Taxonomia registrada
Classificação canônica recuperada da integração com o GBIF. O sistema explicita os níveis que a própria resposta do GBIF não informa.
Avaliação de impactos
1. Redução no desempenho de indivíduos da biota nativa
Resposta: Sim
Mecanismos selecionados: (1) Competição,(3) Hibridização,(4) Transmissão de doenças para espécies nativas,(6) Envenenamento / toxicidade,(10) Impacto físico no ecossistema,(11) Impacto estrutural no ecossistema,(12) Impactos indiretos via interações com outras espécies
Evidências por mecanismo
Prevents germination and colonisation of native plant species, resulting in plots covered entirely by R. ulmifolius Excludes endemic species after establishment in canopy gaps Outcompetes native forest Replaces native plant species Decreases native species richness in grasslands Modifies the composition of adjacent herbaceous vegetation Outcompetes native seedlings and threatens forest community Decreases terrestrial biodiversity from Robinson Crusoe Island Outcompetes native species Decreases native oak recruitment Competes for water with native speices Attracts more bee species than some other native plant species
Hybridizes with native blackberry R. ursinus which facilitates increased invasiveness
Acts as a reserve for Pierce’s disease Serves as an inoculum of Xylella fastidiosa bacterium Hosts and transmits Xylella fastidiosa bacterium
Accumulates lead and transfers lead to red deer
Negatively affects population size of the Wood Mouse (Apodemus sylvaticus)
Can contribute to increased bank erosion, flooding, and fire hazards
Replaces native habitat with dense thickets, which can trap livestock and decreases grazing area Reduces nesting area for native bird species Decreases species richness of ground beetles Affects fitness of carpenter bees
Provides food and reproduction resources fo invasive Drosophila suzukii ; Hosts the non-native oak lace bug Corythucha arcuata
Referências: Competição: Mazzolari, A.C., Comparatore, V.M. and Bedmar, F., 2011. Control of elmleaf blackberry invasion in a natural reserve in Argentina. Journal for nature conservation, 19(3), pp.185-191. Arellano-Cataldo, G. and Smith-Ramírez, C., 2016. Establishment of invasive plant species in canopy gaps on Robinson Crusoe Island. Plant ecology, 217(3), pp.289-302. Dirnböck, T., Greimler, J., LOPEZ S, P.A.T.R.I.C.I.O. and Stuessy, T.F., 2003. Predicting future threats to the native vegetation of Robinson Crusoe Island, Juan Fernández archipelago, Chile. Conservation Biology, 17(6), pp.1650-1659. Gaire, R., Astley, C., Upadhyaya, M.K., Clements, D.R. and Bargen, M., 2015. The biology of Canadian weeds. 154. Himalayan blackberry. Canadian journal of plant science, 95(3), pp.557-570. Masson, S., Mesléard, F. and Dutoit, T., 2015. Using shrub clearing, draining, and herbivory to control bramble invasion in Mediterranean Dry Grasslands. Environmental management, 56(4), pp.933-945. Masson, S., Gauvain, M., Mesléard, F. and Dutoit, T., 2015. Impacts of water stress removal and disturbance regimes on Mediterranean dry grasslands diversity and succession. Plant ecology, 216(10), pp.1351-1369. Montaldo, N.H., 2000. Reproductive success of bird-dispersed plants in a subtropical forest relict in Argentina. Revista Chilena de Historia Natural, 73(3), pp.511-524. Smith-Ramírez, C., ARELLANO, G., HAGEN, E., VARGAS, R., CASTILLO, J. and MIRANDA, A., 2013. El rol de Turdusfalcklandii (Aves: Passeriforme) como dispersor de plantas invasoras en el archipiélago de Juan Fernández. Revista chilena de historia natural, 86(1), pp.33-48. Smith-Ramírez, C., Vargas, R., Castillo, J., Mora, J.P. and Arellano-Cataldo, G., 2017. Woody plant invasions and restoration in forests of island ecosystems: lessons from Robinson Crusoe Island, Chile. Biodiversity and Conservation, 26(7), pp.1507-1524. Williams, K., Westrick, L.J. and Williams, B.J., 2006. Effects of blackberry (Rubus discolor) invasion on oak population dynamics in a California savanna. Forest ecology and management, 228(1-3), pp.187-196. Caplan, J.S. and Yeakley, J.A., 2010. Water relations advantages for invasive Rubusáarmeniacus over two native ruderal congeners. Plant ecology, 210(1), pp.169-179. Interação com outras spp: Arnó, J., Solà, M., Riudavets, J. and Gabarra, R., 2016. Population dynamics, non-crop hosts, and fruit susceptibility of Drosophila suzukii in Northeast Spain. Journal of pest science, 89(3), pp.713-723. Bernardinelli, I., 2006. Potential host plants of Corythucha arcuata (Het., Tingidae) in Europe: a laboratory study. Journal of applied entomology, 130(9‐10), pp.480-484. Hibridização: Gaire, R., Astley, C., Upadhyaya, M.K., Clements, D.R. and Bargen, M., 2015. The biology of Canadian weeds. 154. Himalayan blackberry. Canadian journal of plant science, 95(3), pp.557-570. Impacto fisico: Gaire, R., Astley, C., Upadhyaya, M.K., Clements, D.R. and Bargen, M., 2015. The biology of Canadian weeds. 154. Himalayan blackberry. Canadian journal of plant science, 95(3), pp.557-570. Impacto estrutural Gaire, R., Astley, C., Upadhyaya, M.K., Clements, D.R. and Bargen, M., 2015. The biology of Canadian weeds. 154. Himalayan blackberry. Canadian journal of plant science, 95(3), pp.557-570. Porrini, D.P., Castro, A.V. and Cicchino, A.C., 2014. Los carábidos (Coleoptera: Carabidae) asociados a los remanentes de bosque nativo en la Reserva Natural Municipal Laguna de los Padres, Buenos Aires. Revista de la Sociedad Entomológica Argentina, 73(1-2), pp.35-48. Flores‐Prado, L., Pinto, C.F., Rojas, A. and Fontúrbel, F.E., 2014. Strong selection on mandible and nest features in a carpenter bee that nests in two sympatric host plants. Ecology and evolution, 4(10), pp.1820-1827. Envenenamento/toxicidade: Reglero, M.M., Monsalve-González, L., Taggart, M.A. and Mateo, R., 2008. Transfer of metals to plants and red deer in an old lead mining area in Spain. Science of the Total Environment, 406(1-2), pp.287-297. Transmissão de doenças: Gaire, R., Astley, C., Upadhyaya, M.K., Clements, D.R. and Bargen, M., 2015. The biology of Canadian weeds. 154. Himalayan blackberry. Canadian journal of plant science, 95(3), pp.557-570. Hill, B.L. and Purcell, A.H., 1995. Multiplication and movement of Xylella fastidiosa within grapevine and four other plants. Phytopathology, 85(11), pp.1368-1372. Hill, B.L. and Purcell, A.H., 1997. Populations of Xylella fastidiosa in plants required for transmission by an efficient vector. Phytopathology, 87(12), pp.1197-1201.
2. Declínio no tamanho populacional de espécie nativa
Resposta: Sim
Mecanismos selecionados: (9) Impacto químico no ecossistema
Evidências por mecanismo
Negatively affects population size of the Wood Mouse (Apodemus sylvaticus)
Referências: Amori, G., Luiselli, L., Milana, G. and Casula, P., 2015. Small scale factors affect population size of the wood mouse (Apodemus sylvaticus) in a Mediterranean island (Sardinia). Revue d’Ecologie (Terre et Vie), 70(1), pp.58-69.
3. Extinção local de população nativa
Resposta: Não
4. Reversibilidade da extinção local após remoção do táxon
Resposta: Nenhuma extinção registrada