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Pristine Azorean forests have been deeply fragmented since human colonization. Fragmentation increases the length of edges and it therefore promotes edge habitats. Studying the impact of edge habitat on species assemblages is crucial to highlight the importance of forest connectivity and guide management strategies.This study explores the impact of forest edges on arthropod assemblages, and particularly investigates the differences of arthropod communities between three habitats, along a distance gradient from the forest edge near a pasture matrix to the core forest. We also compare patterns of arthropod communities with different biogeographic status (endemic, native non-endemic, and introduced species). We sampled in a pristine forest on Terceira island bordered by semi-natural pastures, using flight interception traps. Traps were established along the ecological gradient of three habitats: the forest edge, an intermediate habitat at 100 m from the border, and the core forest at 300 m deep from the border.We took a multi-taxon approach and used both univariate and multivariate techniques to understand the variation in arthropods species abundance, richness and composition between the three habitats in the native forest.Overall, endemic species dominated arthropod abundances whereas species richness and diversity were similar between the three biogeographic categories. We found evidence of a strong edge effect on arthropod assemblages, adjusted both by biogeographic categories and seasonality. Indigenous (endemic and native non-endemic) species abundances were higher in the forest interior than at the edges or intermediate habitats, suggesting that indigenous arthropod assemblages were sensitive to the distance from the edge, whereas introduced species abundances did no show an edge effect. Species diversity and richness did not differ between the three habitats either, regardless of the biogeographic categories. The composition of arthropods between the three habitats differed significantly when we considered all species or endemic species only, but not with native non-endemic or introduced species. However, the difference got obscured when seasonality was included in the analyses, suggesting that even though edges impact species composition, this impact varies seasonally and endemic species are particularly affected in early summer.Our results indicate that forest edges impact arthropods assemblages but endemic species are more likely to be constrained by the increase of edges than introduced species. Since most of these endemic species are of conservation concern, we urge to avoid forest management strategies that increase fragmentation and call for action to increase the size of native forest habitat.HighlightsEdge effects constraint the abundance and composition of endemic species but not of introduced onesBoth biogeographical categories and temporal dynamics play a role in forming assemblage patternsEndemics are the most abundant but richness is similar for all three biogeographic categoriesThe edge can affect the abundance of indigenous species up to100 m into the forest interior

[ES] Las abejas son un grupo extremadamente diverso con más de 1000 especies descritas en la península ibérica. Además, son excelentes polinizadores y aportan numerosos servicios ecosistémicos fundamentales para la mayoría de ecosistemas terrestres. Debido a los diversos cambios ambientales inducidos por el ser humano, existen evidencias del declive de algunas de sus poblaciones para ciertas especies. Sin embargo, conocemos muy poco del estado de conservación de la mayoría de especies y de muchas de ellas ignoramos cuál es su distribución en la península ibérica. En este trabajo presentamos un esfuerzo colaborativo para crear una base de datos de ocurrencias de abejas que abarca la península ibérica e islas Baleares que permitirá resolver cuestiones como la distribución de las diferentes especies, preferencia de hábitat, fenología o tendencias históricas. En su versión actual, esta base de datos contiene un total de 87 684 registros de 923 especies recolectados entre 1830 y 2022, de los cuales un 87% presentan información georreferenciada. Para cada registro se incluye información relativa a la localidad de muestreo (89%), identificador y colector de la especie (64%), fecha de captura (54%) y planta donde se recolectó (20%). Creemos que esta base de datos es el punto de partida para conocer y conservar mejor la biodiversidad de abejas en la península ibérica e Islas Baleares, [EN] Bees are a diverse group with more than 1000 species known from the Iberian Peninsula. They have increasingly received special attention due to their important role as pollinators and providers of ecosystem services. In addition, various rapid human-induced environmental changes are leading to the decline of some of its populations. However, we know very little about the conservation status of most species and for many species, we hardly know their true distributions across the Iberian Peninsula. Here, we present a collaborative effort to collate and curate a database of Iberian bee occurrences to answer questions about their distribution, habitat preference, phenology, or historical trends. In total we have accumulated 87 684 records from the Iberian Peninsula and the Balearic Islands of 923 different species with 87% of georeferenced records collected between 1830 and 2022. In addition, each record has associated information such as the sampling location (89%), collector and person who identified the species (64%), date of the capture (54%) and plant species where the bees were captured (20%). We believe that this database is the starting point to better understand and conserve bee biodiversity in the Iberian Peninsula., Esta base de datos se ha realizado con la ayuda de los proyectos EUCLIPO (Fundaçao para a Ciencia e a Tecnologia, LISBOA-01-0145- FEDER-028360/EUCLIPO) y SAFEGUARD (ref. 101003476 H2020-SFS-2019-2).

A agricultura intensiva é uma das actividades que mais influencia a estrutura da paisagem, levando frequentemente à destruição e à perda de biodiversidade local. Por exemplo, a intensidade e gestão das actividades agrícolas pode influenciar dramaticamente a composição e abundância das comunidades de artrópodes que habitam nos agroecosistemas. Alguns artrópodes fitófagos podem causar danos aos pomares ao consumirem parte da planta ou fruto. No entanto, muitos outros podem fornecer serviços benéficos, como a polinização, o controlo de pragas e a decomposição. Os carochos, formigas e aranhas são predadores generalistas importantes para ajudar a controlar pragas de insectos, e, inclusive, reduzir a quantidade de ervas daninhas ao consumir as suas sementes. Quer os ecólogos quer os agrónomos acreditam que a simplicidade dos modernos campos agrícolas, especialmente os extensos campos em monoculturas que recebem frequentes aplicações de pesticidas, contribuem para os surtos de pragas, bastante típicos desses tipos de sistema. Os agroecossistemas mais simples podem ser ambientes relativamente hostis para os inimigos naturais, conduzindo à depauperação das comunidades de predadores e parasitóides. Os ecossistemas agrícolas mais diversificados, por outro lado, tendem a recrutar espécies ruderais, as quais, em geral, são mais resistentes à perturbação destes ambientes agrícolas. O declínio da biodiversidade dos inimigos naturais geralmente enfraquece o controlo biológico. Uma das razões por trás disso é que as comunidades mais ricas podem reunir espécies de inimigos naturais que atacam pragas usando diferentes estratégias ou nichos espaciais e temporais, de modo que a mortalidade total infligida sobre as pragas é maximizada apenas quando várias espécies inimigas ocorrem simultaneamente. O desafio que se coloca aos ecólogos e agrónomos é entender de que forma a biodiversidade dos inimigos naturais pode fortalecer o controlo biológico. Este livro contribui para a identificação e proteção dos artrópodes predadores, que são muito úteis para a agricultura e por isso benéficos para toda a sociedade. [da Nota Introdutória] FINANCIAMENTO: Este livro é um produto do projecto AGRO-ECOSERVICES (ACORES-01-0145-FEDER-000073), financiado pelo FEDER em 85% e por fundos regionais em 15%, através do Programa Operacional Açores 2020. info:eu-repo/semantics/publishedVersion

Proceedings of the 9th Meeting at Lisboa (Portugal) 26-29 October, 2021. The olive tree culture in Terceira Island occupies a strip in Porto Martins area whose fruit is very sought, mainly by tourists and restaurants. The olive tree is very affected by pests, such as the olive fly, which causes high losses and a drastic loss of production. Therefore, large quantities of pesticides are applied whose applications have a great impact, in particular, on beneficial organisms. In this work, the beneficial fauna present in olive groves was identified through the technique of beatings. The impact of the application of pesticides on these beneficial insects present in olive trees with different levels of treatments was also evaluated. For this, orchards with intensive applications, with less intensive applications and one organic orchard were selected to studied and monitoring. It was verified that in the olive groves with intensive and semi-intensive pesticide applications the abundance of beneficial insects was unbalanced, with a low abundance of predatory insects and still high population densities of the olive cottonweed pest. The results obtained point to the fact that chemical treatments do not destroy the target pests and worst contribute to a reduction in auxiliary organisms. In the organic orchard was observed the highest abundance of predatory insects and the lowest abundance of herbivorous insects. These results showed that this type of orchard is in a natural balance and that this is the way to follow in preserving the presence of beneficial insects in the olive parcels because these are very important to keep low pest populations and permit its better control. The conclusions of this study point to the fact that producers can further increase their yield by taking the biological option in their daily practices that will have a lower impact on the beneficial fauna present in the olive groves. At the same time will also permit to preserve the environment and the health of the applicators, producers and of the consumer by obtaining a product without any pesticide residues. To the producers involved in this study. To the agricultural development service of Terceira island (SDAT) and the regional secretary of agriculture and rural development /SRADR) for the logistic support to all the work. To the Cuarentagri project (www.cuarentagri.com) that allowed the execution of this work. info:eu-repo/semantics/publishedVersion

O Guia Prático da Flora Nativa dos Açores / Field Guide of Azorean Native Flora facilita não só o conhecimento das principais espécies da flora açoriana, como permite uma fácil e rápida identificação das endémicas, seja das mais comuns, seja das mais raras. Contempla quase três centenas de espécies, incluindo fichas de líquenes, musgos, hepáticas, antocerotas, fetos e licófitas, gimnospérmicas e angiospérmicas, e inclui a localização onde podem ser avistadas, juntamente com um conjunto de aspetos de natureza científica, divulgando o património natural da Região, bem como a sua rica biodiversidade. FINANCIAMENTO: Secretaria Regional do Ambiente e Alterações Climáticas, Governo Regional dos Açores. Projecto FCT “GUIA DE CAMPO: Ferramentas Móveis lnterativas para a Aprendizagem Baseada no Local” (PTDC/CED-EDG/31182/2017); Projecto FCT “MULTI-YEAR PROJECT 2020-2023” (cE3c/GBA UIDB/00329/2020); Projecto LIFE, “PRIBES - Estratégia Regional para a Prevenção e Controlo de Espécies Exóticas Invasoras” (LIFE IP AZORES NATURA, LIFE17 IPE/PT/000010). info:eu-repo/semantics/publishedVersion

Research in Macaronesia has led to substantial advances in ecology, evolution and conservation biology. We review the scientific developments achieved in this region, and outline promising research avenues enhancing conservation. Some of these discoveries indicate that the Macaronesian flora and fauna are composed of rather young lineages, not Tertiary relicts, predominantly of European origin. Macaronesia also seems to be an important source region for back-colonisation of continental fringe regions on both sides of the Atlantic. This group of archipelagos (Azores, Madeira, Selvagens, Canary Islands, and Cabo Verde) has been crucial to learn about the particularities of macroecological patterns and interaction networks on islands, providing evidence for the development of the General Dynamic Model of oceanic island biogeography and subsequent updates. However, in addition to exceptionally high richness of endemic species, Macaronesia is also home to a growing number of threatened species, along with invasive alien plants and animals. Several innovative conservation and management actions are in place to protect its biodiversity from these and other drivers of global change. The Macaronesian Islands are a well-suited field of study for island ecology and evolution research, mostly due to its special geological layout with 40 islands grouped within five archipelagos differing in geological age, climate and isolation. A large amount of data is now available for several groups of organisms on and around many of these islands. However, continued efforts should be made toward compiling new information on their biodiversity, to pursue various fruitful research avenues and develop appropriate conservation management tools. The Island Biology Interest Group (IBIG, http://www.ibigbiology.com) is grateful to the organisers of the 2016 Island Biology Conference held in the Azores for promoting the symposium that led to this manuscript. We thank Joaquin Hortal for useful comments on an early version of the manuscript, and also Guido Jones for his language editing funded by the Cabildo de Tenerife, under the TFinnova Programme supported by MEDI and FDCAN funds. We are grateful to Salvador de la Cruz and Elena Morales for extracting updated information from the Biodiversity Data Bank of the Canary Islands. We also thank Ricardo Ramalho (Cardiff University) for fruitful discussions on the geological age of the Cabo Verde islands. This manuscript is a contribution by the INCT in Ecology, Evolution and Biodiversity Conservation funded by MCTIC/CNPq/FAPEG (grant 465610/2014-5).