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Invasive Alien Plants in the Azorean Protected Areas: Invasion Status and Mitigation Actions

Authors:
  • Direção-Geral do Território
  • Sociedade Portuguesa para o Estudo das Aves

Abstract

This chapter addresses plant invasions in the protected areas of the Azores (Northern Atlantic), whose flora encompasses a considerable proportion of alien species (about 70 %). The chapter includes (i) a general characterization of the Azores, with particular reference to their Island Natural Parks covering 24 % of the inland surface; (ii) an assessment of the plant invasion status of the Island Natural Parks (based on distribution data and expert evaluation of potential impacts and possibility of control of invasive alien plants); and (iii) a report about on-going and recent management initiatives embracing the control of invasive alien plants. The results show that the Island Natural Parks of Santa Maria Island is potentially the most threatened by invasive alien plants, followed in decreasing order by the Island Natural Parks of the islands of Graciosa, São Jorge, Corvo, Faial, São Miguel, Terceira, Flores and Pico. Some of the most threatening species are highlighted. Due to the innovative assessment methodology, the results do not fully corroborate previous studies, showing that just species listing may not provide a full understanding of the potential effects of invasive alien plants on native biodiversity, thus bringing new insights that may assist management initiatives. Several invasive alien plants management projects run by the Azorean Government and the Portuguese Society for the Study of Birds are described, with reference to those supported by the LIFE programme and PRECEFIAS (an Azorean project devoted to control of invasive alien plants in protected areas). Finally, a holistic discussion is provided stressing strengths and weaknesses of all topics covered in the chapter so that more effective invasive alien plant management strategies can be achieved in the future.
... In the Azores, the South African species Drosera aliciae and D. capensis have been introduced deliberately from cultivated material and since naturalized at some seepage habitats (Borges et al. 2010;Costa et al. 2013). In Brazil, plantings of D. capensis and D. binata into pristine CP habitats have fortunately been detected in time and could be removed completely (P. ...
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... distribution remains nowadays [5]. In addition to further habitat destruction [6] and climate change [7], the current main threat to Laurel Forest, especially in the Azores, is invasive species that outcompete native Laurel Forest plant species, completely transforming the habitat and thus leading to the extinction of endemic species of different taxa [8][9][10]. ...
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... However, changes in land use have led to a drastic reduction in natural forest cover and the expansion of exotic woodland and production forest [45,46]. Besides land cover change, invasive species, including a large number of plant taxa that are recognized as problematic invaders worldwide, constitute a major threat to the preservation of the remaining natural plant communities in the Azores [47,48]. ...
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... Furthermore, the Canary Islands, Madeira and Selvagens have provided examples of successful eradication and control schemes for rabbits, cats, mice, and plants (e.g., Bell, 2001;Olivera et al., 2010). In the Azores, a regional programme to control invasive alien plants in sensitive areas has revealed the importance of maintenance to prevent alien regrowth (Costa et al., 2013). ...
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Recent studies have shown that Macaronesia has considerable problems with exotic species, particularly those considered as invasive. For instance, in the Azores more than 60% of the vascular plant flora consists of non-indigenous species (Silva & Smith 2004, 2006). Several plants are presently considered to be serious threats not only to the conservation of the Azorean endemic flora and native plant communities, but also to the conservation of bird species, namely the Azores bullfinch (Pyrrhula murina) and of arthropods (Borges et al. 2006). In Madeira Archipelago, species like the black rat (Rattus rattus) and the domestic cat (Felis silvestris catus) are known to have a strong negative impact on populations of native birds. In the Canaries, about 11% of the terrestrial biota corresponds to alien species, and some recent introductions originated some social alarm, namely the recent naturalization of a species of snake (Lampropeltis getula) in Gran Canaria. However, of the considerable number of introduced species, how many are considered as really invasive (i.e. they are not only naturalized but are presently causing a negative impact on the Macaronesian biota)? Among those species, which are amenable to control or eradication? Which species should be considered priorities for control actions and other measures because they are causing impact but are still possible to control or eradicate? For instance, in Canaries the Barbary ground squirrel (Atlantoxerus getulus) is considered an emblematic invasive alien species (IAS), but is it the top-ranking invader in Macaronesia? French Hydrangea (Hydrangea macrophylla) is a touristic icon in the Azores, but is now also considered as an invasive alien species. What is the real impact of the different species of alien rodents in Macaronesia? Although negative impacts have been a concern, should positive impacts also be considered? For example, several alien species still have and will most probably continue to have an important role in the islands’ economy or as game species. This book aims to answer some of these questions. It is a first attempt to present information regarding alien species in the European region of Macaronesia in a systematic way. Undoubtedly, this is a difficult task, due to differences regarding legislation but also to the differences in the general treatment given to IAS in the different archipelagos. A standard set of criteria was designed and applied to those species considered as naturalized and occupying natural and semi-natural habitats. A first set of criteria was used to score the effect on biodiversity values, in terms of species and habitats, which are being affected by the invasive species. A second set of criteria was used to score the feasibility of control or eradication of the invasive species. In this second set of criteria we also included items reflecting the social importance of the species concerned. The application of both sets of criteria has allowed identification of the most noxious IAS in Macaronesia and also the ranking of those species according to a management priority. This is of considerable importance, since, due to the large scale of the IAS problem not only in Macaronesia but globally, it is not possible to control every introduced species. Resources will have to be allocated to those species that are still possible to control or eradicate with sustainable costs. Although the criteria were applied by experts from each archipelago, a global Macaronesian approach was possible after a thorough analysis and careful treatment of the data from each archipelago, this being the main objective of the book. This book is also intended to serve as a tool to raise awareness of the problem of IAS. In fact, island ecosystems have been considered as more susceptible to IAS than continental systems, largely due to the small scale of the islands and to peculiarities of island biota which make them more susceptible to foreign competitors, predators and pathogens. However, islands, particularly European islands, are important hotspots for biodiversity, and the preservation of this natural heritage is currently also dependent on the implementation of effective measures to contain IAS
Article
1. The Azores bullfinch (or Priolo), Pyrrhula murina, is largely confined to native forest in the east of the island of S. Miguel (Azores). This paper assesses the impact of a recent large-scale invasion of the native forest by exotic flora on the population and distribution of this species. It examines the population size and importance of vegetation characteristics to explain the seasonal distribution of this bird. The conservation of this population, including the planning of forest management practices is addressed. 2. Point-counts and capture-recapture indicate a population of 60-200 pairs. The bird occurred all year round in the largest fragment of native vegetation to the east of the range and was recorded in a smaller patch to the west only in autumn. 3. The Azores bullfinch's monthly density was much higher in laurel forest than in exotic forests (Cryptomeria japonica and Pittosporum undulatum). There were peaks in the density of birds in exotic forests in summer and autumn. The edge of the native forest was important from May to December and the interior from January to April. The degree and intensity of the selection of habitat structure varied seasonally. More habitats were selected over summer than over winter. Native forest and Clethra arborea were highly preferred at all seasons. Bare ground and short vegetation were selected in summer and avoided in winter. 4. The Azores bullfinch was sedentary but ranged widely locally. They appeared more mobile over summer than over winter. Larger-scale altitudinal movements were carried out in May. 5. Monthly habitat selection may be interpreted as preference for habitats where feeding resources are more abundant. A large home range is needed in summer because birds feed in openings that are separated by unsuitable tall vegetation. 6. Both demographic and environmental stochasticity are important factors in the conservation of the small population of Azores bulfinch. The first factor may not be the major one because the population may have increased recently due to the introduction of C. arborea and also because recruitment seems to compensate annual adult mortality. The invasion of the native forest by aggressive exotic flora seems to be the most important environmental stochasticity factor affecting this population. Present exotic forests are too dense but they could be valuable habitats in summer if they were more scattered. Improvement of the habitat quality of the existing native forest and expansion of its area are important nature conservation strategies for this population.