Efecto De La Estructura Del Paisaje En La Polilla Del Olivo De “Prays Oleae (Lepidoptera: Praydidae)”

Total Page:16

File Type:pdf, Size:1020Kb

Efecto De La Estructura Del Paisaje En La Polilla Del Olivo De “Prays Oleae (Lepidoptera: Praydidae)” Efecto de la estructura del paisaje en la polilla del olivo de “Prays oleae (Lepidoptera: Praydidae)” Damián Mauricio Sáenz Posada Tutores: Susana Pascual Marta Ortega Javier Gutiérrez Puebla Máster en Tecnologías de la Información Geográfica Universidad Complutense de Madrid Junio 2013 Efecto de la estructura del paisaje en la polilla del olivo de “Prays oleae (Lepidoptera: Praydidae)” Damián Mauricio Sáenz Posada1 Tutores: Susana Pascual2 Marta Ortega3 Javier Gutiérrez Puebla4 Trabajo realizado en el Instituto Nacional de Investigación y Tecnología Agraria y Alimentaria (INIA) para optar al título de M.Sc. en Tecnologías de la Información Geográfica (TIG). Máster en Tecnologías de la Información Geográfica Universidad Complutense de Madrid Junio 2013 1 Ingeniero de Montes. M.Sc. Gestión Ambiental en la Empresa. (Estudiante de M.Sc. TIG) 2 Departamento de Protección Forestal. Instituto Nacional de Investigación y Tecnología Agraria y Alimentaria. 3 Departamento de Ecología. Facultad de Ciencias Biológicas. Universidad Complutense de Madrid. 4 Departamento de Geografía Humana. Facultad de Geografía en historia. Universidad Complutense de Madrid. Efecto de la estructura del paisaje en la población de “Prays oleae”. Tabla de contenido 1. INTRODUCCIÓN .......................................................................................................... 6 2. OBJETIVOS ................................................................................................................. 10 2.1. Objetivo General .................................................................................................................... 10 2.2. Objetivos específicos ........................................................................................................... 10 3. MATERIALES Y MÉTODOS ..................................................................................... 11 3.1. Área de estudio....................................................................................................................... 11 3.2. Material Cartográfico (SIOSE, PNOA, SIGPAC) ........................................................ 12 3.3. Información biológica (RAIF) .......................................................................................... 13 3.4. Caracterización de la estructura del paisaje en la zona de estudio .............. 16 3.4.1. Elaboración de la capa base .................................................................................... 16 3.4.2. Análisis espacial e índices de composición y configuración del paisaje 21 3.5. Análisis estadístico ............................................................................................................... 23 4. RESULTADOS ............................................................................................................. 26 4.1. Análisis de la curva de vuelo y daños de P. oleae. .................................................. 26 4.2. Análisis de correlación entre los índices de paisaje y los parámetros de población y daño del P. oleae. ....................................................................................................... 28 4.2.1. Índice de diversidad de Shannon (SDI) ............................................................. 28 4.2.2. Índice de forma (MSI) ................................................................................................ 32 4.2.3. Índice de borde (TE)................................................................................................... 36 5. DISCUSIÓN ................................................................................................................. 42 6. CONCLUSIONES Y FUTURAS LÍNEAS DE INVESTIGACIÓN .............................. 45 BIBLIOGRAFÍA .................................................................................................................. 47 ANEXOS .............................................................................................................................. 50 2 Efecto de la estructura del paisaje en la población de “Prays oleae”. Índice de Tablas y Figuras Tablas Tabla 1: Cantidad de puntos de control empleados según los distintos radios de influencia. .................................................................................................................................................... 16 Tabla 2: Número de muestras por variable que contuvieron un mínimo de 10 datos por semana. ................................................................................................................................... 26 Tabla 3: Correlación entre el índice de diversidad de Shannon (SDI) y la población de P. oleae (número de adultos capturados por trampa y día) a lo largo de los tres años de estudio. Los datos son el coeficiente de correlación de Pearson (r) y la significación estadística de la misma (p). .................................................................................... 29 Tabla 4: Correlación entre el índice de diversidad de Shannon (SDI) y los daños de la generación filófaga del P. oleae (hojas atacadas). Los datos son el coeficiente de correlación de Pearson (r) y la significación estadística de la misma (p). Se observan dos niveles de significación estadística, p=0,05 (resaltado en rojo) y p=0,1 (resaltado en violeta). Las siglas SDC significan que no se cumplió el criterio de mínimo 10 datos semanales. ....................................................................................................... 30 Tabla 5: Correlación entre el índice de diversidad de Shannon (SDI) y los daños de la generación antófaga del P. oleae (flores atacadas). Los datos son el coeficiente de correlación de Pearson (r) y la significación estadística de la misma (p). Se observan dos niveles de significación estadística, p=0,05 (resaltado en rojo) y p=0,1 (resaltado en violeta). Las siglas SDC significan que no se cumplió el criterio de mínimo 10 datos semanales. ....................................................................................................... 31 Tabla 6: Correlación entre el índice de diversidad de Shannon (SDI) y los daños causados por la generación carpófaga (frutos atacados). ) Los datos son el coeficiente de correlación de Pearson (r) y la significación estadística de la misma (p). Se presentaron dos niveles de significación estadística, p=0,05 (resaltado en rojo) y p=0,1 (resaltado en violeta). Las siglas SDC significan que no se cumplió el criterio de mínimo 10 datos semanales. ...................................................................................... 32 Tabla 7: Correlación entre el índice de forma media (MSI) y la población de P. oleae (número de adultos capturados por trampa y día) a lo largo de los tres años de estudio. Los datos son el coeficiente de correlación de Pearson (r) y la significación estadística de la misma (P). Se observan dos niveles de significación estadística, p=0,05 (resaltado en rojo) y p=0,1 (resaltado en violeta). Las siglas SDC significan que no se cumplió el criterio de mínimo 10 datos semanales. .................... 33 Tabla 8: Correlación entre el índice de forma media (MSI) y el daño de la generación filófaga. (Hojas atacadas). Los datos son el coeficiente de correlación de 3 Efecto de la estructura del paisaje en la población de “Prays oleae”. Pearson (r) y la significación estadística de la misma (p). Los niveles de significación estadística, p=0,05 (resaltado en rojo) y p=0,1 (resaltado en violeta). Las siglas SDC significan que no se cumplió el criterio de mínimo 10 datos semanales. ................................................................................................................................................... 35 Tabla 9: Correlación entre el índice de forma media (MSI) y los daños causados por la generación antófaga (flores atacadas). Los datos son el coeficiente de correlación de Pearson (r) y la significación estadística de la misma (p). Se ilustraron dos niveles de significación estadística, p=0,05 (resaltado en rojo) y p=0,1 (resaltado en violeta). Las siglas SDC significan que no se cumplió el criterio de mínimo 10 datos semanales. ....................................................................................................... 35 Tabla 10: Correlación entre el índice de forma media (MSI) y los daños causados por la generación carpófaga (frutos atacados). Los datos son el coeficiente de correlación de Pearson (r) y la significación estadística de la misma (p). Se presentan dos niveles de significación estadística, p=0,05 (resaltado en rojo) y p=0,1 (resaltado en violeta). Las siglas SDC significan que no se cumplió el criterio de mínimo 10 datos semanales. ....................................................................................................... 36 Tabla 11: Correlación el índice de longitud de borde (TE) y la población de P. oleae (número de adultos capturados por trampa y día) a lo largo de los tres años de estudio. Los datos son el coeficiente de correlación de Pearson (r) y la significación estadística de la misma (p). La tabla presenta dos niveles de significación estadística, p=0,05 (resaltado en rojo) y p=0,1 (resaltado en violeta). Las siglas SDC significan que no se cumplió el criterio de mínimo 10 datos semanales. .................... 38 Tabla 12: Correlación entre el índice de longitud de bordes (TE) y daños de la generación filófaga (hojas atacadas). Los datos son el coeficiente de correlación de Pearson (r) y la significación estadística de la misma (p). Se observó dos niveles de significación estadística,
Recommended publications
  • Hymenoptera Parasitoid Complex of Prays Oleae (Bernard) (Lepidoptera: Praydidae) in Portugal
    Turkish Journal of Zoology Turk J Zool (2017) 41: 502-512 http://journals.tubitak.gov.tr/zoology/ © TÜBİTAK Research Article doi:10.3906/zoo-1603-50 Hymenoptera parasitoid complex of Prays oleae (Bernard) (Lepidoptera: Praydidae) in Portugal 1, 1 2 3 4 1 Anabela NAVE *, Fátima GONÇALVES , Rita TEIXEIRA , Cristina AMARO COSTA , Mercedes CAMPOS , Laura TORRES 1 Centre for the Research and Technology of Agro-Environmental and Biological Sciences, University of Trás-os-Montes and Alto Douro, Vila Real, Portugal 2 Agrarian and Forestry Systems and Plant Health, National Institute of Agricultural and Veterinary Research, Oeiras, Portugal 3 Department of Ecology and Sustainable Agriculture, Agrarian School, Polytechnic Institute of Viseu, Viseu, Portugal 4 Department of Environmental Protection, Experimental Station Zaidín, Granada, Spain Received: 23.03.2016 Accepted/Published Online: 29.11.2016 Final Version: 23.05.2017 Abstract: The olive moth, Prays oleae (Bernard) (Lepidoptera: Praydidae), is one of the most important pests of olive trees throughout the Mediterranean region, the Black Sea, the Middle East, and the Canary Islands. Thus, it is particularly important to develop alternative strategies to control this pest. Over a 4-year period, a survey was done in order to acquire knowledge about the complex of parasitoids associated with this pest. Leaves, flowers, and fruit infested with larvae and pupae of P. oleae were collected from olive groves, conditioned in vials, and kept under laboratory conditions until the emergence of P. ol e ae adults or parasitoids. The abundance and richness of parasitoids as well as the rate of parasitism was estimated. Hymenoptera parasitoids were found to be responsible for 43% of the mean mortality of the sampled individuals.
    [Show full text]
  • Schutz Des Naturhaushaltes Vor Den Auswirkungen Der Anwendung Von Pflanzenschutzmitteln Aus Der Luft in Wäldern Und Im Weinbau
    TEXTE 21/2017 Umweltforschungsplan des Bundesministeriums für Umwelt, Naturschutz, Bau und Reaktorsicherheit Forschungskennzahl 3714 67 406 0 UBA-FB 002461 Schutz des Naturhaushaltes vor den Auswirkungen der Anwendung von Pflanzenschutzmitteln aus der Luft in Wäldern und im Weinbau von Dr. Ingo Brunk, Thomas Sobczyk, Dr. Jörg Lorenz Technische Universität Dresden, Fakultät für Umweltwissenschaften, Institut für Forstbotanik und Forstzoologie, Tharandt Im Auftrag des Umweltbundesamtes Impressum Herausgeber: Umweltbundesamt Wörlitzer Platz 1 06844 Dessau-Roßlau Tel: +49 340-2103-0 Fax: +49 340-2103-2285 [email protected] Internet: www.umweltbundesamt.de /umweltbundesamt.de /umweltbundesamt Durchführung der Studie: Technische Universität Dresden, Fakultät für Umweltwissenschaften, Institut für Forstbotanik und Forstzoologie, Professur für Forstzoologie, Prof. Dr. Mechthild Roth Pienner Straße 7 (Cotta-Bau), 01737 Tharandt Abschlussdatum: Januar 2017 Redaktion: Fachgebiet IV 1.3 Pflanzenschutz Dr. Mareike Güth, Dr. Daniela Felsmann Publikationen als pdf: http://www.umweltbundesamt.de/publikationen ISSN 1862-4359 Dessau-Roßlau, März 2017 Das diesem Bericht zu Grunde liegende Vorhaben wurde mit Mitteln des Bundesministeriums für Umwelt, Naturschutz, Bau und Reaktorsicherheit unter der Forschungskennzahl 3714 67 406 0 gefördert. Die Verantwortung für den Inhalt dieser Veröffentlichung liegt bei den Autorinnen und Autoren. UBA Texte Entwicklung geeigneter Risikominimierungsansätze für die Luftausbringung von PSM Kurzbeschreibung Die Bekämpfung
    [Show full text]
  • Biodiversity and Pest Management APRIL 2019
    biodiversity and pest management APRIL 2019 EIP-AGRI Focus Group ‘Pests and diseases of the olive tree’ Biodiversity and pest management AUTHORS: MARÍA TERESA MARTÍNEZ FERRER, TÂNIA NOBRE, VASILEIOS GKISAKIS, FRANÇOIS WARLOP, JUAN OLIVARES, SUSANA PASCUAL 1 biodiversity and pest management APRIL 2019 1. Introduction Maintaining biodiversity and the associated ecosystem services is an objective of the European Union, implemented through agri-environmental programmes. Biodiversity decline is occurring at a worldwide scale and has twofold implications. From a conservation point of view, the number of extinct and endangered species increases, and this impoverishment of natural ecosystems reduces their resilience. From an agronomical point of view, reduction of biodiversity affects processes that hamper crop productivity, such as pollination or pest management, being the consequence of this biodiversity decline a reduction in agroecosystem sustainability. But both, ecosystem resilience and agro ecosystem sustainability are not isolated. In the case of pest control, in many cases it is assumed that it depends on biodiversity. However, a positive relationship between biodiversity of natural enemies and pest suppression is not always the case. In fact, in some cases this relationship does not occur (Fig.1), and the success of biological control depends not on biodiversity, but on the presence of one or only few species of natural enemies. As an example, in the case of olive trees, a single species such as Anthocoris nemoralis or relatively simple predator assemblages are associated with better biological control than complex assemblages (Paredes et al., 2015). However, it seems that the general rule in different agroecosystems is that biodiversity rather than abundance of natural enemies is linked to pest control, although this has been proven mainly in annual crops and in non- mediterranean environmental conditions (Dainese et al., 2019).
    [Show full text]
  • 1 Fungal Diversity Associated to the Olive Moth, Prays Oleae Bernard: a Survey For
    View metadata, citation and similar papers at core.ac.uk brought to you by CORE provided by Universidade do Minho: RepositoriUM 1 Fungal diversity associated to the olive moth, Prays oleae Bernard: a survey for 2 potential entomopathogenic fungi 3 4 Ivo Oliveira1, José A. Pereira1; Teresa Lino-Neto2, Albino Bento1, Paula Baptista1* 5 6 1CIMO / School of Agriculture, Polytechnic Institute of Bragança, Campus de Santa 7 Apolónia, Apartado 1172, 5301-854 Bragança, Portugal. 8 2 Centre for Biodiversity Functional and Integrative Genomics (BioFIG), Plant 9 Functional Biology Centre, University of Minho, Campus de Gualtar, 4710-057 Braga, 10 Portugal. 11 12 13 Running title: Fungal associated to Prays oleae 14 Submission date: 28-05-2011 15 16 17 18 * Corresponding author. Tel.: + 351 273303332; Fax + 351 273 325405. 19 E-mail address: [email protected] (P. Baptista). 20 1 21 ABSTRACT 22 Olive production is one of the main agricultural activities in Portugal. In the region of 23 Trás-os-Montes this crop has been considerably affected by Prays oleae. In order to 24 evaluate the diversity of fungi on P. oleae population of Trás-os-Montes olive orchards, 25 larvae and pupae of the three annual generations (phyllophagous, antophagous and 26 carpophagous) were collected and evaluated for fungal growth on their surface. From 27 the 3828 larvae and pupae, a high percentage of individuals exhibited growth of a 28 fungal agent (40.6%), particularly those from the phyllophagous generation. From all 29 the moth generations, a total of 43 species from 24 genera were identified, but the 30 diversity and abundance of fungal species differed between the three generations.
    [Show full text]
  • Stones on the Ground in Olive Groves Promote the Presence of Spiders (Araneae)
    EUROPEAN JOURNAL OF ENTOMOLOGYENTOMOLOGY ISSN (online): 1802-8829 Eur. J. Entomol. 115: 372–379, 2018 http://www.eje.cz doi: 10.14411/eje.2018.037 ORIGINAL ARTICLE Stones on the ground in olive groves promote the presence of spiders (Araneae) JACINTO BENHADI-MARÍN 1, 2, JOSÉ A. PEREIRA1, JOSÉ A. BARRIENTOS 3, JOSÉ P. SOUSA2 and SÓNIA A.P. SANTOS 4, 5 1 Centro de Investigação de Montanha (CIMO), ESA, Instituto Politécnico de Bragança, Campus de Santa Apolónia, 5300-253 Bragança, Portugal; e-mails: [email protected], [email protected] 2 Centre for Functional Ecology, Department of Life Sciences, University of Coimbra, Calçada Martim de Freitas, 3000-456 Coimbra, Portugal; e-mail: [email protected] 3 Department of Animal Biology, Plant Biology and Ecology, Faculty of Biosciences, Autonomous University of Barcelona, 08193 Bellaterra, Barcelona, Spain; e-mail: [email protected] 4 CIQuiBio, Barreiro School of Technology, Polytechnic Institute of Setúbal, Rua Américo da Silva Marinho, 2839-001 Lavradio, Portugal; e-mail: [email protected] 5 LEAF, Instituto Superior de Agronomia, Tapada da Ajuda, 1349-017 Lisboa, Portugal Key words. Araneae, biological control, ground hunter, predator, abundance, diversity, shelter Abstract. Spiders are generalist predators that contribute to the control of pests in agroecosystems. Land use management determines habitats including refuges for hibernation and aestivation. The availability of shelters on the ground can be crucial for maintaining populations of spider within crops. We studied the effect of the number of stones on the surface of the soil on the spi- der community in selected olive groves in Trás-os-Montes (northeastern Portugal).
    [Show full text]
  • EIP-AGRI Focus Group 'Pests and Diseases of the Olive Tree'
    EIP-AGRI Focus Group ‘Pests and diseases of the olive tree’ Biological and Biotechnical methods for olive pest control Marion Canale, Umberto Bernardo, Panagiotis Milonas, Sónia Santos [email protected] [email protected] [email protected] [email protected] 1 Biological and Biotechnical methods for olive pests control 18/04/2019 1. Introduction and description of the main problem related to the topic The olive tree (Olea europaea L.) is a typical and emblematic tree in the Mediterranean countries where it has great relevance from economic to social and landscape aspects (Loumou & Giourga, 2003). The olive tree is susceptible to the attack of different insect pests causing a decline of the olive production. Phytosanitary threats are the major cause of harvesting losses in olive groves. Each year, 15% of the production is damaged by insect pests (Bueno & Jones, 2002). Usually, olive growers use a range of pesticides to control pests that can have several negative impacts (e.g., loss of biodiversity, insecticide resistance and residues on olives) (Kombargi et al., 1998; Pereira-Castro et al., 2015). Notwithstanding, the European Union (EU) has established the adoption of environmentally-friendly farming practices through the agri-environment schemes and through the Directive 2009/128/EC for the sustainable use of pesticides. These measures bring the need to develop sustainable production systems where the application of biological and biotechnical methods can be promoted. Biologically based methods for pest management use natural enemies of pests to reduce the population of the target-pest. Biotechnical methods are highly specific since they influence either the behaviour or the development of the target pest and do not have direct biocide activity.
    [Show full text]
  • Hidden Genetic Variability, Can the Olive Moth Prays Oleae (Lepidoptera: Yponomeutidae Or Praydidae?) Be a Species’ Complex?
    insects Article Hidden Genetic Variability, Can the Olive Moth Prays oleae (Lepidoptera: Yponomeutidae or Praydidae?) be a Species’ Complex? Marlon Pazian 1 ,Tânia Nobre 1,* , Imen Blibech 2 and Fernando T Rei 1 1 MED—Mediterranean Institute for Agriculture, Environment and Development, Instituto de Investigação e Formação Avançada, Universidade de Évora, Pólo da Mitra, Ap. 94, 7006-554 Évora, Portugal; [email protected] (M.P.); [email protected] (F.T.R.) 2 Laboratory of research LR: Genetic Resources of the Olive Tree: Characterization, Promotion and Protection, Olive Tree Institute, Sousse 4061, Tunisia; [email protected] * Correspondence: [email protected]; Tel.: +351-266-760-885 Received: 28 February 2020; Accepted: 16 March 2020; Published: 26 March 2020 Abstract: Prays oleae is the second most important pest in Mediterranean olive groves, causing substantial damage on olive production. We used mitochondrial [cytochrome c oxidase subunit I(COI), and NADH dehydrogenase subunit 5 (nad5)] and nuclear [ribosomal protein S5 (RpS5)] amplicons to assess the population variability in five main olive producing regions from Tunisia, to support or dismiss the existence of two non-monophyletic groups within the species, as found within Portugal. Our phylogenetic analysis with cytochrome c oxidase subunit I (COI) indeed displayed two distinct and well-supported clades of P. oleae, which were corroborated by the haplotype network reconstructed with both mitochondrial and nuclear amplicons. We were also able to dismiss the hypothesis that one of the clades would not develop on olive fruits. No correlation was observed between clades differentiation and geographic distribution. The existence of cryptic species can impact on the management of agroecosystems and on the perception of how these moths responds to environmental changes.
    [Show full text]
  • Ichneumonidae (Hymenoptera) As Biological Control Agents of Pests
    Ichneumonidae (Hymenoptera) As Biological Control Agents Of Pests A Bibliography Hassan Ghahari Department of Entomology, Islamic Azad University, Science & Research Campus, P. O. Box 14515/775, Tehran – Iran; [email protected] Preface The Ichneumonidae is one of the most species rich families of all organisms with an estimated 60000 species in the world (Townes, 1969). Even so, many authorities regard this figure as an underestimate! (Gauld, 1991). An estimated 12100 species of Ichneumonidae occur in the Afrotropical region (Africa south of the Sahara and including Madagascar) (Townes & Townes, 1973), of which only 1927 have been described (Yu, 1998). This means that roughly 16% of the afrotropical ichneumonids are known to science! These species comprise 338 genera. The family Ichneumonidae is currently split into 37 subfamilies (including, Acaenitinae; Adelognathinae; Agriotypinae; Alomyinae; Anomaloninae; Banchinae; Brachycyrtinae; Campopleginae; Collyrinae; Cremastinae; Cryptinae; Ctenopelmatinae; 1 Diplazontinae; Eucerotinae; Ichneumoninae; Labeninae; Lycorininae; Mesochorinae; Metopiinae; Microleptinae; Neorhacodinae; Ophioninae; Orthopelmatinae; Orthocentrinae; Oxytorinae; Paxylomatinae; Phrudinae; Phygadeuontinae; Pimplinae; Rhyssinae; Stilbopinae; Tersilochinae; Tryphoninae; Xoridinae) (Yu, 1998). The Ichneumonidae, along with other groups of parasitic Hymenoptera, are supposedly no more species rich in the tropics than in the Northern Hemisphere temperate regions (Owen & Owen, 1974; Janzen, 1981; Janzen & Pond, 1975), although
    [Show full text]
  • Yellow Or Transparent? Comparison of Sticky Traps for Monitoring Functional Arthropod Diversity in an Olive Agroecosystem
    Animal Biodiversity and Conservation 43.1 (2020) 159 Yellow or transparent? Comparison of sticky traps for monitoring functional arthropod diversity in an olive agroecosystem A. Dimitrova, M. Milošević, T. Spanos, I. Livieratos, V. D. Gkisakis Dimitrova, A., Milošević, M., Spanos, T., Livieratos, I., Gkisakis, V. D., 2020. Yellow or transparent? Comparison of sticky traps for monitoring functional arthropod diversity in an olive agroecosystem. Animal Biodiversity and Consevation, 43.1: 159–167, Doi: https://doi.org/10.32800/abc.2020.43.0159 Abstract Yellow or transparent? Comparison of sticky traps for monitoring functional arthropod diversity in an olive agroecosystem. A diverse and balanced arthropod community is known to play an important role in the olive canopy but monitoring methods are not always well defined. We monitored canopy arthropods in an olive or- chard over two years, comparing the performance of yellow sticky traps and transparent sticky traps. Data used to compare the two types of traps were arthropod abundance, richness, diversity indices, species abundance distribution and aggregation of taxa in functional groups based on prioritized agroecosystem services. The total abundance of arthropods caught in the yellow traps was higher than that in the transparent traps but diversity in both traps was similar. Transparent traps may therefore be a valid option to assess biodiversity in an olive agrosystem as besides being less labor demanding than yellow traps, they are low cost and replicable, and do not damage the overall arthropod. Key words: Olive, Canopy, Agrobiodiversity, Trapping, Agroecology Resumen ¿Amarillas o transparentes? Comparación de trampas adhesivas para estudiar la diversidad funcional de los artrópodos en el ecosistema de los olivares.
    [Show full text]
  • Effect of Non-Crop Vegetation Types on Conservation Biological Control Of
    EVect of non-crop vegetation types on conservation biological control of pests in olive groves Daniel Paredes1, Luis Cayuela2, GeoV M. Gurr3 and Mercedes Campos1 1 Grupo de Proteccion´ Vegetal, Departamento de Proteccion´ Ambiental, Estacion´ Experimental de Zaid´ın, CSIC, Granada, Spain 2 Area´ de Biodiversidad y Conservacion,´ Departamento de Biolog´ıa y Geolog´ıa, Universidad Rey Juan Carlos I, Mostoles,´ Spain 3 EH Graham Centre for Agricultural Innovation (Primary Industries, NSW and Charles Sturt University), Orange, NSW, Australia ABSTRACT Conservation biological control (CBC) is an environmentally sound potential al- ternative to the use of chemical insecticides. It involves modifications of the envi- ronment to promote natural enemy activity on pests. Despite many CBC studies increasing abundance of natural enemies, there are far fewer demonstrations of reduced pest density and very little work has been conducted in olive crops. In this study we investigated the eVects of four forms of non-crop vegetation on the abundance of two important pests: the olive psyllid (Euphyllura olivina) and the olive moth (Prays oleae). Areas of herbaceous vegetation and areas of woody vegeta- tion near olive crops, and smaller patches of woody vegetation within olive groves, decreased pest abundance in the crop. Inter-row ground covers that are known to increase the abundance of some predators and parasitoids had no eVect on the pests, possibly as a result of lack of synchrony between pests and natural enemies, lack of specificity or intra-guild predation. This study identifies examples of the right types of diversity for use in conservation biological control in olive production systems.
    [Show full text]
  • Hidden Genetic Variability, Can the Olive Moth Prays Oleae (Lepidoptera: Yponomeutidae Or Praydidae?) Be a ‘Species’ Complex?
    Hidden genetic variability, can the olive moth Prays oleae (Lepidoptera: Yponomeutidae or Praydidae?) be a ‘species’ complex? Pazian, M; Nobre, T.*; Blibech, I; Rei, F.T. MED – Mediterranean Institute for Agriculture, Environment and Development, Instituto de Investigação e Formação Avançada, Universidade de Évora, Pólo da Mitra, Ap. 94, 7006-554 Évora, Portugal. *Corresponding author: [email protected] Key words: Prays oleae, olive moth, cryptic species, phylogenetic, population structure Table S1. Data on the specimen and sampling coordinates of Prays oleae collected in Tunisia and Greece. GenBank accession numbers are given per sample. N/S = no sampled amplicon. COI Genbank Lab Locality phylogeny accession number Coordinates voucher (Fig.2) COI nad5 RpS5 B12 Bouficha clade 2 MT096260 MT106246 MT096181 36°15'36.0"N 10°26'24.0"E B13 Bouficha clade 1 MT096261 MT106247 MT096182 36°15'36.0"N 10°26'24.0"E B14 Bouficha clade 1 MT096262 MT106248 MT096183 36°15'36.0"N 10°26'24.0"E B16 Bouficha clade 1 MT096263 MT106249 MT096184 36°15'36.0"N 10°26'24.0"E B21 Bouficha clade 1 MT096264 MT106250 MT096185 36°15'36.0"N 10°26'24.0"E B22 Bouficha clade 1 MT096265 MT106251 MT096186 36°15'36.0"N 10°26'24.0"E B23 Bouficha clade 1 MT096266 MT106252 MT096187 36°15'36.0"N 10°26'24.0"E B24 Bouficha clade 1 MT096267 MT106253 MT096188 36°15'36.0"N 10°26'24.0"E B25 Bouficha clade 1 MT096268 MT106254 MT096189 36°15'36.0"N 10°26'24.0"E B31 Bouficha clade 2 MT096269 MT106255 MT096190 36°15'36.0"N 10°26'24.0"E B32 Bouficha clade 1 MT096270 MT106256 MT096191 36°15'36.0"N
    [Show full text]
  • Methodological Considerations in Discriminating Olive-Orchard Management Type Using Olive-Canopy Arthropod Fauna at the Level of Order
    Spanish Journal of Agricultural Research 13(4), e0304, 14 pages (2015) eISSN: 2171-9292 http://dx.doi.org/10.5424/sjar/2015134-6588 Instituto Nacional de Investigación y Tecnología Agraria y Alimentaria (INIA) RESEARCH ARTICLE OPEN ACCESS Methodological considerations in discriminating olive-orchard management type using olive-canopy arthropod fauna at the level of order Carlos Jerez-Valle1, Pedro A. García-López2, Mercedes Campos3 and Felipe Pascual1 1 Universidad de Granada, Departamento de Zoología. Campus de Fuentenueva s/n, 18071 Granada, Spain. 2 Universidad de Granada, Departamento de Estadística e Investigación Operativa. Campus de Fuentenueva s/n, 18071 Granada, Spain. 3 EEZ (CSIC), Departamento de Protección Ambiental. Profesor Albareda 1, 18008 Granada, Spain. Abstract The cultivation of the olive tree (Olea europaea L.) has great importance in the entire Mediterranean basin, so that the implementation of organic practices in their management directly affects the sustainability of the agricultural system. Bioindication with arthropods can help to detect the different agricultural practices. In this work, we analyse the most appropriate methodology for discriminating between management using arthropods at the taxonomic level of order, with the novelty of taking into account the weather conditions to select the sampling dates. Between 12 and 15 sampling stations (depending on the year) were selected from olive orchards belong- ing to organic, conventional non-tillage, and strict conventional management, being sampled by beating the canopy fortnightly in the spring-summer period of 2007, 2008 and 2009. Organic management was more abundant and richer than the rest for the three years. Most groups with significant differences in terms of relative abundance were more abundant in organic orchard, except Neuroptera.
    [Show full text]