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      <Keyword>WMS</Keyword>
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        <AddressType/>
        <Address/>
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        <StateOrProvince/>
        <PostCode/>
        <Country>Portugal</Country>
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      <ContactVoiceTelephone/>
      <ContactFacsimileTelephone/>
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          <Abstract>A determinação da potencialidade florestal poderá fazer-se com recurso a modelos preditivos da composição, em termos das espécies ecologicamente dominantes, das florestas espontâneas. Estas correspondem àquelas que não só apresentam, por princípio, a melhor adaptação ecológica (climática, edáfica) que garante a maior qualidade ambiental do Território e que corresponde aos usos extensivos em sistemas de agricultura tradicionais, mas também a novas oportunidades de paisagens rurais funcionalmente salutares.
Os modelos fundamentais que exprimem os pressupostos ecológicos que foram utilizados no desenvolvimento da metodologia utilizada na determinação deste tipo de aptidão são de três tipos: i) Modelos de Distribuição de Espécies (SDM-Species Distribution Models); ii) Modelos geobotânicos de Vegetação Natural Potencial (VNP), em particular o de Capelo et al. (2007); e iii) Modelos tipológicos de geosséries ripícolas, estabelecidos especificamente no âmbito deste projeto, a partir de Aguiar et al., 1995 e Portela-Pereira, 2014.

&lt;br&gt;Cartografia de aptidão à instalação de povoamentos da espécie arbórea Alnus glutinosa. Modelo tipológico de geosséries ripícolas. Linhas de água e aluviões em todo o país excepto nos Superdistritos Alto Alentejano, Aracenense e Baixo Alentejano.&lt;br&gt;&lt;br&gt;

Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.

&lt;br&gt;&lt;br&gt;Bioclimatic Suitability to Tree Species&lt;br&gt;
The determination of forest potential can be made using the predictive models of the composition, in terms of ecologically dominant species of spontaneous forests. These correspond to those who not only have, in principle, the best ecological adaptation (climate, edaphic) that guarantees the highest environmental quality of the territory and which corresponds to extended use in traditional farming systems, but also to new opportunities for functionally salutary countryside .
The basic models that express the ecological assumptions that were used in the development of the methodology used in determining this type of suitability are of three types: i) Species Distribution Models (SDM-Species Distribution Models); ii)  Geobotanical Models of potential natural vegetation  (PNV), in particular Capelo et al. (2007); and iii) typological models of riparian geosséries established specifically in this project, based on Aguiar et al., 1995 and Portela-Pereira, 2014.&lt;br&gt;&lt;br&gt;

Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.
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          <Abstract>A Aptidão Edafo-Morfológica é uma aptidão parcial dependente das condições de solo, morfologia do terreno e declive. Esta aptidão foi determinada para a Agricultura de Sequeiro e de Regadio e para a Silvicultura e teve por objectivo restringir as Aptidões às Culturas Agrícolas e às Espécies Arbóreas/Pastagens às condições mais adequadas relativamente aos parâmetros referidos.
A Aptidão Edafo-morfológica à Agricultura de Regadio, foi obtida através da exclusão dos tipos de solo ou de ocupações que a impedem e não a partir de uma matriz, uma vez que o regadio alarga a potencialidade para a agricultura, ao reduzir a dependência dos factores climáticos. Os critérios de exclusão adoptados incidem sobre características do solo, difíceis de reverter: solos com espessura inferior a 25 cm, solos com fase pedregosa, solos hidro e halomórficos, solos orgânicos hidromóficos, afloramentos rochosos, massas de água, zonas húmidas e territórios artificializados.
&lt;br&gt;&lt;br&gt;Irrigated Agriculture&lt;br&gt;
The Soil and Morphological Suitability is a partial suitability dependent on soil, land morphology and slope conditions. This suitability was determined for the Rainfed and Irrigated Agriculture and the Silviculture and aimed to restrict the suitability to Agricultural Crops and Tree Species / Pastures to the most suitable conditions in respect of those parameters.
The Soil and Morphological Suitability to the Irrigated Agriculture was obtained by excluding the soil types or land uses that prevent it and not from an array, since the irrigation extends the potential for agriculture reducing its dependence on climatic factors. The adopted exclusion criteria focus on soil characteristics, difficult to reverse: soils with thickness less than 25 cm, soils with stony phase, saline soils, hydromorphic organic soils, rocky outcrops, water bodies, wetlands and artificialized territories.</Abstract>
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          <Abstract>A Aptidão Edafo-Morfológica à Agricultura de Sequeiro foi determinada a partir de uma matriz que integra o valor ecológico do solo com a morfologia do terreno e o declive.
				&lt;br&gt;&lt;br&gt;
				Soil and Morphological suitability - Dryland Agriculture&lt;br&gt;
The Soil and Morphological suitability for Dryland Agriculture was determined from a matrix that integrates the ecological value of the land with the land morphology and the slope.
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          <Abstract>A determinação da potencialidade florestal poderá fazer-se com recurso a modelos preditivos da composição, em termos das espécies ecologicamente dominantes, das florestas espontâneas. Estas correspondem àquelas que não só apresentam, por princípio, a melhor adaptação ecológica (climática, edáfica) que garante a maior qualidade ambiental do Território e que corresponde aos usos extensivos em sistemas de agricultura tradicionais, mas também a novas oportunidades de paisagens rurais funcionalmente salutares.
Os modelos fundamentais que exprimem os pressupostos ecológicos que foram utilizados no desenvolvimento da metodologia utilizada na determinação deste tipo de aptidão são de três tipos: i) Modelos de Distribuição de Espécies (SDM-Species Distribution Models); ii) Modelos geobotânicos de Vegetação Natural Potencial (VNP), em particular o de Capelo et al. (2007); e iii) Modelos tipológicos de geosséries ripícolas, estabelecidos especificamente no âmbito deste projeto, a partir de Aguiar et al., 1995 e Portela-Pereira, 2014.

&lt;br&gt;Cartografia da área de aptidão à instalação de povoamentos da espécie arbórea Acer monspessulanum.´Modelo VNP. Séries Arisaro clusi-Querco broteroi Sigmetum, Junipero lagunae-Querco suberis S. e mosaicos com Viburno tini-Querco rivas-martinezii S.
Não existem dados sistemáticos de ocorrência desta espécie, pelo que a cartografia da sua área de ocorrência só pode ser feita com recurso a modelos geobotânicos.
&lt;br&gt;&lt;br&gt;Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.

&lt;br&gt;&lt;br&gt;Bioclimatic Suitability to Tree Species&lt;br&gt;
The determination of forest potential can be made using the predictive models of the composition, in terms of ecologically dominant species of spontaneous forests. These correspond to those who not only have, in principle, the best ecological adaptation (climate, edaphic) that guarantees the highest environmental quality of the territory and which corresponds to extended use in traditional farming systems, but also to new opportunities for functionally salutary countryside .
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Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.
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          <Abstract>A determinação da potencialidade florestal poderá fazer-se com recurso a modelos preditivos da composição, em termos das espécies ecologicamente dominantes, das florestas espontâneas. Estas correspondem àquelas que não só apresentam, por princípio, a melhor adaptação ecológica (climática, edáfica) que garante a maior qualidade ambiental do Território e que corresponde aos usos extensivos em sistemas de agricultura tradicionais, mas também a novas oportunidades de paisagens rurais funcionalmente salutares.
Os modelos fundamentais que exprimem os pressupostos ecológicos que foram utilizados no desenvolvimento da metodologia utilizada na determinação deste tipo de aptidão são de três tipos: i) Modelos de Distribuição de Espécies (SDM-Species Distribution Models); ii) Modelos geobotânicos de Vegetação Natural Potencial (VNP), em particular o de Capelo et al. (2007); e iii) Modelos tipológicos de geosséries ripícolas, estabelecidos especificamente no âmbito deste projeto, a partir de Aguiar et al., 1995 e Portela-Pereira, 2014.

&lt;br&gt;Cartografia da área de aptidão à instalação de povoamentos da espécie arbórea Quercus rotundifolia. Modelo VNP. Séries Genisto histricis-Querco rotundifoliae Sigmetum, Rusco-Juniperetum lagunae S., Lonicero implexae-Querco rotundifoliae S., Myrto-Querco rotundifoliae S., Pyro bourgaeanae-Querco rotundifoliae S., Rhamno olioidis-Querco rotundifoliae S. e respetivos mosaicos. Os modelos de distribuição da azinheira obtidos apresentaram estatísticas muito boas (R = 0,75 para GLM). No entanto, os mapas produzidos com estes modelos revelaram-se pouco satisfatórios. Esta discrepância deve-se certamente ao facto de a azinheira ser excessivamente subestimada nos dados de distribuição actual, sobretudo pelo seu porte arbustivo em áreas muito secas ou sujeitas a incêndios recorrentes. A título de exemplo, a espécie quase não está representada no Maciço Calcário Estremenho e em Trás-os-Montes. Constatou-se também uma dificuldade em aderir o modelo à distribuição desta espécie na zona ao sul do Douro interior, até à serra da Estrela. A distribuição desta espécie parece obedecer, neste local, não apenas a factores climáticos ou litológicos, mas também a factores edáficos não expressos pela tipologia da Carta de Solos. Existem algumas evidências que micronutrientes, como o boro, possam eventualmente constituir factores limitantes a outras espécies de carvalho, sendo favoráveis à azinheira (Azevedo Gomes, com. pess.; Aguiar, com. pess.). Como tal, optou-se por cartografar esta espécie a partir do modelo de vegetação potencial existente, selecionando-se as séries onde a mesma está presente em abundância.&lt;br&gt;&lt;br&gt;Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.

&lt;br&gt;&lt;br&gt;Bioclimatic Suitability to Tree Species&lt;br&gt;
The determination of forest potential can be made using the predictive models of the composition, in terms of ecologically dominant species of spontaneous forests. These correspond to those who not only have, in principle, the best ecological adaptation (climate, edaphic) that guarantees the highest environmental quality of the territory and which corresponds to extended use in traditional farming systems, but also to new opportunities for functionally salutary countryside .
The basic models that express the ecological assumptions that were used in the development of the methodology used in determining this type of suitability are of three types: i) Species Distribution Models (SDM-Species Distribution Models); ii)  Geobotanical Models of potential natural vegetation  (PNV), in particular Capelo et al. (2007); and iii) typological models of riparian geosséries established specifically in this project, based on Aguiar et al., 1995 and Portela-Pereira, 2014.&lt;br&gt;&lt;br&gt;

Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.
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          <Abstract>A determinação da potencialidade florestal poderá fazer-se com recurso a modelos preditivos da composição, em termos das espécies ecologicamente dominantes, das florestas espontâneas. Estas correspondem àquelas que não só apresentam, por princípio, a melhor adaptação ecológica (climática, edáfica) que garante a maior qualidade ambiental do Território e que corresponde aos usos extensivos em sistemas de agricultura tradicionais, mas também a novas oportunidades de paisagens rurais funcionalmente salutares.
Os modelos fundamentais que exprimem os pressupostos ecológicos que foram utilizados no desenvolvimento da metodologia utilizada na determinação deste tipo de aptidão são de três tipos: i) Modelos de Distribuição de Espécies (SDM-Species Distribution Models); ii) Modelos geobotânicos de Vegetação Natural Potencial (VNP), em particular o de Capelo et al. (2007); e iii) Modelos tipológicos de geosséries ripícolas, estabelecidos especificamente no âmbito deste projeto, a partir de Aguiar et al., 1995 e Portela-Pereira, 2014.

&lt;br&gt;Cartografia da área de aptidão à instalação de povoamentos da espécie arbórea Betula pubescens. Modelo misto VNP e de geosséries ripícolas. Séries Saxifrago-Betuleto celtiberica Sigmetum e Lycopodio clavati-Junipero nani S. e linhas de água e aluviões na área da série Vaccinio-Querco roboris S.&lt;br&gt;&lt;br&gt;Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.

&lt;br&gt;&lt;br&gt;Bioclimatic Suitability to Tree Species&lt;br&gt;
The determination of forest potential can be made using the predictive models of the composition, in terms of ecologically dominant species of spontaneous forests. These correspond to those who not only have, in principle, the best ecological adaptation (climate, edaphic) that guarantees the highest environmental quality of the territory and which corresponds to extended use in traditional farming systems, but also to new opportunities for functionally salutary countryside .
The basic models that express the ecological assumptions that were used in the development of the methodology used in determining this type of suitability are of three types: i) Species Distribution Models (SDM-Species Distribution Models); ii)  Geobotanical Models of potential natural vegetation  (PNV), in particular Capelo et al. (2007); and iii) typological models of riparian geosséries established specifically in this project, based on Aguiar et al., 1995 and Portela-Pereira, 2014.&lt;br&gt;&lt;br&gt;

Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.
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          <Abstract>A determinação da potencialidade florestal poderá fazer-se com recurso a modelos preditivos da composição, em termos das espécies ecologicamente dominantes, das florestas espontâneas. Estas correspondem àquelas que não só apresentam, por princípio, a melhor adaptação ecológica (climática, edáfica) que garante a maior qualidade ambiental do Território e que corresponde aos usos extensivos em sistemas de agricultura tradicionais, mas também a novas oportunidades de paisagens rurais funcionalmente salutares.
Os modelos fundamentais que exprimem os pressupostos ecológicos que foram utilizados no desenvolvimento da metodologia utilizada na determinação deste tipo de aptidão são de três tipos: i) Modelos de Distribuição de Espécies (SDM-Species Distribution Models); ii) Modelos geobotânicos de Vegetação Natural Potencial (VNP), em particular o de Capelo et al. (2007); e iii) Modelos tipológicos de geosséries ripícolas, estabelecidos especificamente no âmbito deste projeto, a partir de Aguiar et al., 1995 e Portela-Pereira, 2014.

&lt;br&gt;Cartografia da área de aptidão à instalação de povoamentos da espécie arbórea Celtis australis. Modelo tipológico de geosséries ripícolas. Linhas de água e aluviões nos Superdistritos da Terra Quente, Zezerense e Cacerense e no troço nordeste do rio Tejo no Superdistrito Ribatagano, a montante da foz do rio Zêzere.&lt;br&gt;&lt;br&gt;Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.

&lt;br&gt;&lt;br&gt;Bioclimatic Suitability to Tree Species&lt;br&gt;
The determination of forest potential can be made using the predictive models of the composition, in terms of ecologically dominant species of spontaneous forests. These correspond to those who not only have, in principle, the best ecological adaptation (climate, edaphic) that guarantees the highest environmental quality of the territory and which corresponds to extended use in traditional farming systems, but also to new opportunities for functionally salutary countryside .
The basic models that express the ecological assumptions that were used in the development of the methodology used in determining this type of suitability are of three types: i) Species Distribution Models (SDM-Species Distribution Models); ii)  Geobotanical Models of potential natural vegetation  (PNV), in particular Capelo et al. (2007); and iii) typological models of riparian geosséries established specifically in this project, based on Aguiar et al., 1995 and Portela-Pereira, 2014.&lt;br&gt;&lt;br&gt;

Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.
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          <Abstract>A determinação da potencialidade florestal poderá fazer-se com recurso a modelos preditivos da composição, em termos das espécies ecologicamente dominantes, das florestas espontâneas. Estas correspondem àquelas que não só apresentam, por princípio, a melhor adaptação ecológica (climática, edáfica) que garante a maior qualidade ambiental do Território e que corresponde aos usos extensivos em sistemas de agricultura tradicionais, mas também a novas oportunidades de paisagens rurais funcionalmente salutares.
Os modelos fundamentais que exprimem os pressupostos ecológicos que foram utilizados no desenvolvimento da metodologia utilizada na determinação deste tipo de aptidão são de três tipos: i) Modelos de Distribuição de Espécies (SDM-Species Distribution Models); ii) Modelos geobotânicos de Vegetação Natural Potencial (VNP), em particular o de Capelo et al. (2007); e iii) Modelos tipológicos de geosséries ripícolas, estabelecidos especificamente no âmbito deste projeto, a partir de Aguiar et al., 1995 e Portela-Pereira, 2014.

&lt;br&gt;Cartografia da área de aptidão à instalação de povoamentos da espécie arbórea Ceratonia siliqua. Modelo VNP. Séries Rhamno oleoidis-Querco rotundifoliae Sigmetum e Viburno tini-Oleo sylvestris S. A alfarrobeira, em termos da sua ocorrência em massas espontâneas, corresponde ao andar bioclimático termomediterrânico subhúmido em solos argilosos relativamente pesados. Admissivelmente, o seu cultivo poderá estender-se a outras regiões com menores aptidões, ou seja, a solos mais pobres e andares bioclimáticos com maiores intensidades de frio e mais secos, se forem garantidas condições culturais um pouco mais intensivas.&lt;br&gt;&lt;br&gt;Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.

&lt;br&gt;&lt;br&gt;Bioclimatic Suitability to Tree Species&lt;br&gt;
The determination of forest potential can be made using the predictive models of the composition, in terms of ecologically dominant species of spontaneous forests. These correspond to those who not only have, in principle, the best ecological adaptation (climate, edaphic) that guarantees the highest environmental quality of the territory and which corresponds to extended use in traditional farming systems, but also to new opportunities for functionally salutary countryside .
The basic models that express the ecological assumptions that were used in the development of the methodology used in determining this type of suitability are of three types: i) Species Distribution Models (SDM-Species Distribution Models); ii)  Geobotanical Models of potential natural vegetation  (PNV), in particular Capelo et al. (2007); and iii) typological models of riparian geosséries established specifically in this project, based on Aguiar et al., 1995 and Portela-Pereira, 2014.&lt;br&gt;&lt;br&gt;

Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.
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          <Abstract>A determinação da potencialidade florestal poderá fazer-se com recurso a modelos preditivos da composição, em termos das espécies ecologicamente dominantes, das florestas espontâneas. Estas correspondem àquelas que não só apresentam, por princípio, a melhor adaptação ecológica (climática, edáfica) que garante a maior qualidade ambiental do Território e que corresponde aos usos extensivos em sistemas de agricultura tradicionais, mas também a novas oportunidades de paisagens rurais funcionalmente salutares.
Os modelos fundamentais que exprimem os pressupostos ecológicos que foram utilizados no desenvolvimento da metodologia utilizada na determinação deste tipo de aptidão são de três tipos: i) Modelos de Distribuição de Espécies (SDM-Species Distribution Models); ii) Modelos geobotânicos de Vegetação Natural Potencial (VNP), em particular o de Capelo et al. (2007); e iii) Modelos tipológicos de geosséries ripícolas, estabelecidos especificamente no âmbito deste projeto, a partir de Aguiar et al., 1995 e Portela-Pereira, 2014.

&lt;br&gt;Cartografia da área de aptidão à instalação de povoamentos da espécie arbórea Castanea Sativa. Modelo composto por uma combinação de GLM e VNP. Con("VNP" == 9,0,Con("qr" == 1,1,Con("qp" == 1,1,0))). O castanheiro é uma espécie introduzida há muitos séculos (um arqueófito), que se encontra por vezes naturalizada, geralmente em bosques mistos com carvalho-alvarinho e carvalho-negral, pontualmente em formações extremes. Assim, os dados de presença desta espécie são frequentemente incompletos.
Optou-se assim por cartografar a aptidão a esta espécie com base na área de aptidão de carvalho-alvarinho e carvalho-negral, à qual foi retirada a área dos vales demasiado quentes e secos do Alto Douro e afluentes, que correspondem às séries de vegetação Junipero lagunae-Querco suberis Sigmetum e Rusco-Juniperetum lagunae S.&lt;br&gt;&lt;br&gt;Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.

&lt;br&gt;&lt;br&gt;Bioclimatic Suitability to Tree Species&lt;br&gt;
The determination of forest potential can be made using the predictive models of the composition, in terms of ecologically dominant species of spontaneous forests. These correspond to those who not only have, in principle, the best ecological adaptation (climate, edaphic) that guarantees the highest environmental quality of the territory and which corresponds to extended use in traditional farming systems, but also to new opportunities for functionally salutary countryside .
The basic models that express the ecological assumptions that were used in the development of the methodology used in determining this type of suitability are of three types: i) Species Distribution Models (SDM-Species Distribution Models); ii)  Geobotanical Models of potential natural vegetation  (PNV), in particular Capelo et al. (2007); and iii) typological models of riparian geosséries established specifically in this project, based on Aguiar et al., 1995 and Portela-Pereira, 2014.&lt;br&gt;&lt;br&gt;

Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.
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          <Abstract>Neste Projecto recorreu-se ao conceito de Aptidão Ecológica à Edificação que corresponde às áreas em que não existem contra-indicações de natureza ecológica à implantação de edificação e que, paralelamente são mais adequadas à edificação, do ponto de vista bioclimático, geotécnico, salvaguarda de riscos naturais e custos de construção (Magalhães et al., 2008).
Neste sentido, caracterizou-se a paisagem em termos da sua aptidão ecológica à edificação, considerando critérios de valor e sensibilidade ecológica (Estrutura Ecológica Nacional) e de adequação da implementação de edificação à morfologia do terreno (conforto bioclimático econdições geotécnicas).
&lt;br&gt;&lt;br&gt;
Magalhães, M. R., Cunha, N. S., Abreu, M., Lousã, M., Cortez, N., Costa, J. C., Cunha, N., Campo, S., Pena, S., Mesquita, S., Arsénio, P. e Mata, D. (2008). Plano Verde do Concelho de Sintra – 2ªFase. Coordenação e Concepção Geral, Centro de Estudos de Arquitectura Paisagista, Instituto Superior de Agronomia, UTL, Lisboa.
&lt;br&gt;&lt;br&gt;Soil and Top-climatic Suitability to Building&lt;br&gt;
In this project the concept of Ecological Soil to Building corresponds to the areas where there are no ecological nature constraints to the implementation of building.  In parallel these areas are more appropriate to the building, bioclimatic and geotechnical standpoint, safeguard natural hazards and construction costs (Magalhães et al., 2008). In this sense, the landscape was characterized  in terms of its ecological suitability for building, considering criteria of ecological value and sensitivity (National Ecological Network) and adequacy to the land morphology (bioclimatic comfort and geotechnical conditions).
&lt;br&gt;&lt;br&gt;
Magalhães, M. R., Cunha, N. S., Abreu, M., Lousã, M., Cortez, N., Costa, J. C., Cunha, N., Campo, S., Pena, S., Mesquita, S., Arsénio, P. e Mata, D. (2008). Plano Verde do Concelho de Sintra – 2ªFase. Coordenação e Concepção Geral, Centro de Estudos de Arquitectura Paisagista, Instituto Superior de Agronomia, UTL, Lisboa.</Abstract>
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          <Abstract>A determinação da potencialidade florestal poderá fazer-se com recurso a modelos preditivos da composição, em termos das espécies ecologicamente dominantes, das florestas espontâneas. Estas correspondem àquelas que não só apresentam, por princípio, a melhor adaptação ecológica (climática, edáfica) que garante a maior qualidade ambiental do Território e que corresponde aos usos extensivos em sistemas de agricultura tradicionais, mas também a novas oportunidades de paisagens rurais funcionalmente salutares.
Os modelos fundamentais que exprimem os pressupostos ecológicos que foram utilizados no desenvolvimento da metodologia utilizada na determinação deste tipo de aptidão são de três tipos: i) Modelos de Distribuição de Espécies (SDM-Species Distribution Models); ii) Modelos geobotânicos de Vegetação Natural Potencial (VNP), em particular o de Capelo et al. (2007); e iii) Modelos tipológicos de geosséries ripícolas, estabelecidos especificamente no âmbito deste projeto, a partir de Aguiar et al., 1995 e Portela-Pereira, 2014.

&lt;br&gt;Cartografia da área de aptidão à instalação de povoamentos da espécie arbórea Fraxinus angustifolia. Modelo tipológico de geosséries ripícolas.&lt;br&gt;&lt;br&gt;Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.

&lt;br&gt;&lt;br&gt;Bioclimatic Suitability to Tree Species&lt;br&gt;
The determination of forest potential can be made using the predictive models of the composition, in terms of ecologically dominant species of spontaneous forests. These correspond to those who not only have, in principle, the best ecological adaptation (climate, edaphic) that guarantees the highest environmental quality of the territory and which corresponds to extended use in traditional farming systems, but also to new opportunities for functionally salutary countryside .
The basic models that express the ecological assumptions that were used in the development of the methodology used in determining this type of suitability are of three types: i) Species Distribution Models (SDM-Species Distribution Models); ii)  Geobotanical Models of potential natural vegetation  (PNV), in particular Capelo et al. (2007); and iii) typological models of riparian geosséries established specifically in this project, based on Aguiar et al., 1995 and Portela-Pereira, 2014.&lt;br&gt;&lt;br&gt;

Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.
Linhas de água e aluviões em todo o país excepto no Superdistrito Aracenense.
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          <Abstract>A determinação da potencialidade florestal poderá fazer-se com recurso a modelos preditivos da composição, em termos das espécies ecologicamente dominantes, das florestas espontâneas. Estas correspondem àquelas que não só apresentam, por princípio, a melhor adaptação ecológica (climática, edáfica) que garante a maior qualidade ambiental do Território e que corresponde aos usos extensivos em sistemas de agricultura tradicionais, mas também a novas oportunidades de paisagens rurais funcionalmente salutares.
Os modelos fundamentais que exprimem os pressupostos ecológicos que foram utilizados no desenvolvimento da metodologia utilizada na determinação deste tipo de aptidão são de três tipos: i) Modelos de Distribuição de Espécies (SDM-Species Distribution Models); ii) Modelos geobotânicos de Vegetação Natural Potencial (VNP), em particular o de Capelo et al. (2007); e iii) Modelos tipológicos de geosséries ripícolas, estabelecidos especificamente no âmbito deste projeto, a partir de Aguiar et al., 1995 e Portela-Pereira, 2014.

&lt;br&gt;Cartografia da área de aptidão à instalação de povoamentos da espécie arbórea Juniperus oxycedrus. Modelo VNP. Séries Junipero lagunae-Querco suberis Sigmetum, Rusco-Juniperetum lagunae S. e Pistacio-Junipero badiae S.
Não existem dados sistemáticos de ocorrência desta espécie, pelo que a cartografia da sua área de ocorrência só pode ser feita com recurso a modelos geobotânicos.&lt;br&gt;&lt;br&gt;Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.

&lt;br&gt;&lt;br&gt;Bioclimatic Suitability to Tree Species&lt;br&gt;
The determination of forest potential can be made using the predictive models of the composition, in terms of ecologically dominant species of spontaneous forests. These correspond to those who not only have, in principle, the best ecological adaptation (climate, edaphic) that guarantees the highest environmental quality of the territory and which corresponds to extended use in traditional farming systems, but also to new opportunities for functionally salutary countryside .
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Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.
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          <Abstract>A determinação da potencialidade florestal poderá fazer-se com recurso a modelos preditivos da composição, em termos das espécies ecologicamente dominantes, das florestas espontâneas. Estas correspondem àquelas que não só apresentam, por princípio, a melhor adaptação ecológica (climática, edáfica) que garante a maior qualidade ambiental do Território e que corresponde aos usos extensivos em sistemas de agricultura tradicionais, mas também a novas oportunidades de paisagens rurais funcionalmente salutares.
Os modelos fundamentais que exprimem os pressupostos ecológicos que foram utilizados no desenvolvimento da metodologia utilizada na determinação deste tipo de aptidão são de três tipos: i) Modelos de Distribuição de Espécies (SDM-Species Distribution Models); ii) Modelos geobotânicos de Vegetação Natural Potencial (VNP), em particular o de Capelo et al. (2007); e iii) Modelos tipológicos de geosséries ripícolas, estabelecidos especificamente no âmbito deste projeto, a partir de Aguiar et al., 1995 e Portela-Pereira, 2014.

&lt;br&gt;Cartografia da área de aptidão à instalação de povoamentos da espécie arbórea Juniperus turbinata. Modelo VNP. Séries Osyrio quadripartitae-Junipero turbinatae Sigmetum, Querco-Junipero turbinatae S., Rhamno oleoidis-Querco rotundifoliae S., Viburno tini-Querco rivas-martinezii S., Phlomido-Junipero turbinatae S. e seus mosaicos. Não existem dados sistemáticos de ocorrência desta espécie, pelo que a cartografia da sua área de ocorrência só pode ser feita com recurso a modelos geobotânicos.&lt;br&gt;&lt;br&gt;Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.

&lt;br&gt;&lt;br&gt;Bioclimatic Suitability to Tree Species&lt;br&gt;
The determination of forest potential can be made using the predictive models of the composition, in terms of ecologically dominant species of spontaneous forests. These correspond to those who not only have, in principle, the best ecological adaptation (climate, edaphic) that guarantees the highest environmental quality of the territory and which corresponds to extended use in traditional farming systems, but also to new opportunities for functionally salutary countryside .
The basic models that express the ecological assumptions that were used in the development of the methodology used in determining this type of suitability are of three types: i) Species Distribution Models (SDM-Species Distribution Models); ii)  Geobotanical Models of potential natural vegetation  (PNV), in particular Capelo et al. (2007); and iii) typological models of riparian geosséries established specifically in this project, based on Aguiar et al., 1995 and Portela-Pereira, 2014.&lt;br&gt;&lt;br&gt;

Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.
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          <Abstract>A determinação da potencialidade florestal poderá fazer-se com recurso a modelos preditivos da composição, em termos das espécies ecologicamente dominantes, das florestas espontâneas. Estas correspondem àquelas que não só apresentam, por princípio, a melhor adaptação ecológica (climática, edáfica) que garante a maior qualidade ambiental do Território e que corresponde aos usos extensivos em sistemas de agricultura tradicionais, mas também a novas oportunidades de paisagens rurais funcionalmente salutares.
Os modelos fundamentais que exprimem os pressupostos ecológicos que foram utilizados no desenvolvimento da metodologia utilizada na determinação deste tipo de aptidão são de três tipos: i) Modelos de Distribuição de Espécies (SDM-Species Distribution Models); ii) Modelos geobotânicos de Vegetação Natural Potencial (VNP), em particular o de Capelo et al. (2007); e iii) Modelos tipológicos de geosséries ripícolas, estabelecidos especificamente no âmbito deste projeto, a partir de Aguiar et al., 1995 e Portela-Pereira, 2014.

&lt;br&gt;Cartografia da área de aptidão à instalação de povoamentos da espécie arbórea Populus alba. Modelo tipológico de geosséries ripícolas. Linhas de água e aluviões no Superdistrito Algárvico.&lt;br&gt;&lt;br&gt;Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.

&lt;br&gt;&lt;br&gt;Bioclimatic Suitability to Tree Species&lt;br&gt;
The determination of forest potential can be made using the predictive models of the composition, in terms of ecologically dominant species of spontaneous forests. These correspond to those who not only have, in principle, the best ecological adaptation (climate, edaphic) that guarantees the highest environmental quality of the territory and which corresponds to extended use in traditional farming systems, but also to new opportunities for functionally salutary countryside .
The basic models that express the ecological assumptions that were used in the development of the methodology used in determining this type of suitability are of three types: i) Species Distribution Models (SDM-Species Distribution Models); ii)  Geobotanical Models of potential natural vegetation  (PNV), in particular Capelo et al. (2007); and iii) typological models of riparian geosséries established specifically in this project, based on Aguiar et al., 1995 and Portela-Pereira, 2014.&lt;br&gt;&lt;br&gt;

Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.
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          <Abstract>Carta de aptidão ao pastoreio onde surgem delimitadas as áreas com potencialidade para a exploração de comunidades herbáceas anuais como pastagens.
Os prados espontâneos considerados, anuais ou vivazes, ocorrem tipicamente no sobcoberto de montado, em mosaicos com comunidades arbustivas ou em terrenos agrícolas em pousio, com menos frequência em áreas geridas especificamente com o objectivo de manter áreas de pasto.
&lt;br&gt;Elaboração de um mapa de aptidão ao pastoreio onde surgem delimitadas as áreas com potencialidade para a exploração de comunidades herbáceas anuais como pastagens. Os prados espontâneos considerados, anuais ou vivazes, ocorrem tipicamente no sobcoberto de montado, em mosaicos com comunidades arbustivas ou em terrenos agrícolas em pousio, com menos frequência em áreas geridas especificamente com o objectivo de manter áreas de pasto. A metodologia empregue consistiu no desenvolvimento de um conjunto de regras, definidas com base em conhecimento de especialista. Estas regras visam estabelecer a aptidão do território considerando uma escala de três valores — aptidão nula a baixa, aptidão média e aptidão elevada — a partir das características ecológicas consideradas mais influentes na definição da adequabilidade para a pastagem: bioclima e morfologia do terreno, cartografados anteriormente.
&lt;br&gt;&lt;br&gt;Bioclimatic Suitability to Spontaneous Pastures&lt;br&gt;
In the Spontaneous Pastures Suitability map are bounded areas with potential for the exploitation of annual grasslands as pastureland.
Spontaneous meadows considered, annual or perennial, typically occur in the understorey of “montado” in mosaics with shrubby communities or agricultural land fallow, less often in areas specifically managed in order to maintain grazing areas.
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          <Abstract>A determinação da potencialidade florestal poderá fazer-se com recurso a modelos preditivos da composição, em termos das espécies ecologicamente dominantes, das florestas espontâneas. Estas correspondem àquelas que não só apresentam, por princípio, a melhor adaptação ecológica (climática, edáfica) que garante a maior qualidade ambiental do Território e que corresponde aos usos extensivos em sistemas de agricultura tradicionais, mas também a novas oportunidades de paisagens rurais funcionalmente salutares.
Os modelos fundamentais que exprimem os pressupostos ecológicos que foram utilizados no desenvolvimento da metodologia utilizada na determinação deste tipo de aptidão são de três tipos: i) Modelos de Distribuição de Espécies (SDM-Species Distribution Models); ii) Modelos geobotânicos de Vegetação Natural Potencial (VNP), em particular o de Capelo et al. (2007); e iii) Modelos tipológicos de geosséries ripícolas, estabelecidos especificamente no âmbito deste projeto, a partir de Aguiar et al., 1995 e Portela-Pereira, 2014.

&lt;br&gt;Cartografia da área de aptidão à instalação de povoamentos da espécie arbórea Pinus pinaster. Modelo CART, alterado manualmente; R = 0,59. O modelo do pinheiro-bravo apresenta uma aderência razoável às localizações conhecidas, com um coeficiente de correlação de 0,59. No entanto, tratando-se de uma espécie exótica cuja distribuição actual é determinada unicamente pela sua plantação, considera-se o resultado obtido bastante aceitável.&lt;br&gt;&lt;br&gt;Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.

&lt;br&gt;&lt;br&gt;Bioclimatic Suitability to Tree Species&lt;br&gt;
The determination of forest potential can be made using the predictive models of the composition, in terms of ecologically dominant species of spontaneous forests. These correspond to those who not only have, in principle, the best ecological adaptation (climate, edaphic) that guarantees the highest environmental quality of the territory and which corresponds to extended use in traditional farming systems, but also to new opportunities for functionally salutary countryside .
The basic models that express the ecological assumptions that were used in the development of the methodology used in determining this type of suitability are of three types: i) Species Distribution Models (SDM-Species Distribution Models); ii)  Geobotanical Models of potential natural vegetation  (PNV), in particular Capelo et al. (2007); and iii) typological models of riparian geosséries established specifically in this project, based on Aguiar et al., 1995 and Portela-Pereira, 2014.&lt;br&gt;&lt;br&gt;

Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.
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          <Abstract>A determinação da potencialidade florestal poderá fazer-se com recurso a modelos preditivos da composição, em termos das espécies ecologicamente dominantes, das florestas espontâneas. Estas correspondem àquelas que não só apresentam, por princípio, a melhor adaptação ecológica (climática, edáfica) que garante a maior qualidade ambiental do Território e que corresponde aos usos extensivos em sistemas de agricultura tradicionais, mas também a novas oportunidades de paisagens rurais funcionalmente salutares.
Os modelos fundamentais que exprimem os pressupostos ecológicos que foram utilizados no desenvolvimento da metodologia utilizada na determinação deste tipo de aptidão são de três tipos: i) Modelos de Distribuição de Espécies (SDM-Species Distribution Models); ii) Modelos geobotânicos de Vegetação Natural Potencial (VNP), em particular o de Capelo et al. (2007); e iii) Modelos tipológicos de geosséries ripícolas, estabelecidos especificamente no âmbito deste projeto, a partir de Aguiar et al., 1995 e Portela-Pereira, 2014.

&lt;br&gt;Cartografia da área de aptidão à instalação de povoamentos da espécie arbórea Pinus pinea. Modelo VNP. Séries Asparago aphylli-Querco suberis Sigmetum, Oleo sylvestris-Querco suberis S. e respectivos mosaicos, Osyrio quadripartitae-Junipero turbinatae S., Teucrio baetici-Querco suberis S., mosaicos de Asparago aphylli-Querco suberis S. e Viburno tini-Querco roboris S. Nos últimos anos executaram-se inúmeras plantações de pinheiro-manso em áreas onde o mesmo não era habitualmente cultivado, nomeadamente no Baixo Alentejo, na bacia do rio Guadiana. Verifica-se, no entanto, que tais árvores apresentam um crescimento muito lento e começa a perceber-se que essa não é uma zona adequada à cultura de pinheiro-manso com objectivos de produção. No entanto, não é possível destrinçar, a priori, nos dados de ocorrência da espécie, quais os locais que correspondem a elevada aptidão a esta cultura e quais os que correspondem a aptidão muito marginal, de baixa produtividade. Como tal, os modelos produzidos a partir de dados de ocorrência da espécie revelaram-se muito pouco eficientes, por traduzirem os limites actuais de ocorrência desta espécie por excesso. Optou-se assim por realizar a cartografia das áreas de aptidão ao cultivo de pinheiro-manso com base em modelos de vegetação potencial.&lt;br&gt;&lt;br&gt;Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.

&lt;br&gt;&lt;br&gt;Bioclimatic Suitability to Tree Species&lt;br&gt;
The determination of forest potential can be made using the predictive models of the composition, in terms of ecologically dominant species of spontaneous forests. These correspond to those who not only have, in principle, the best ecological adaptation (climate, edaphic) that guarantees the highest environmental quality of the territory and which corresponds to extended use in traditional farming systems, but also to new opportunities for functionally salutary countryside .
The basic models that express the ecological assumptions that were used in the development of the methodology used in determining this type of suitability are of three types: i) Species Distribution Models (SDM-Species Distribution Models); ii)  Geobotanical Models of potential natural vegetation  (PNV), in particular Capelo et al. (2007); and iii) typological models of riparian geosséries established specifically in this project, based on Aguiar et al., 1995 and Portela-Pereira, 2014.&lt;br&gt;&lt;br&gt;

Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.
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          <Abstract>A determinação da potencialidade florestal poderá fazer-se com recurso a modelos preditivos da composição, em termos das espécies ecologicamente dominantes, das florestas espontâneas. Estas correspondem àquelas que não só apresentam, por princípio, a melhor adaptação ecológica (climática, edáfica) que garante a maior qualidade ambiental do Território e que corresponde aos usos extensivos em sistemas de agricultura tradicionais, mas também a novas oportunidades de paisagens rurais funcionalmente salutares.
Os modelos fundamentais que exprimem os pressupostos ecológicos que foram utilizados no desenvolvimento da metodologia utilizada na determinação deste tipo de aptidão são de três tipos: i) Modelos de Distribuição de Espécies (SDM-Species Distribution Models); ii) Modelos geobotânicos de Vegetação Natural Potencial (VNP), em particular o de Capelo et al. (2007); e iii) Modelos tipológicos de geosséries ripícolas, estabelecidos especificamente no âmbito deste projeto, a partir de Aguiar et al., 1995 e Portela-Pereira, 2014.

&lt;br&gt;Cartografia da área de aptidão à instalação de povoamentos da espécie arbórea Populus nigra. Modelo tipológico de geosséries ripícolas. Linhas de água e aluviões nos Sectores Galaico-Português, Salmantino, Lusitano-Duriense, Estrelense e Toledano-Tagano.&lt;br&gt;&lt;br&gt;Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.

&lt;br&gt;&lt;br&gt;Bioclimatic Suitability to Tree Species&lt;br&gt;
The determination of forest potential can be made using the predictive models of the composition, in terms of ecologically dominant species of spontaneous forests. These correspond to those who not only have, in principle, the best ecological adaptation (climate, edaphic) that guarantees the highest environmental quality of the territory and which corresponds to extended use in traditional farming systems, but also to new opportunities for functionally salutary countryside .
The basic models that express the ecological assumptions that were used in the development of the methodology used in determining this type of suitability are of three types: i) Species Distribution Models (SDM-Species Distribution Models); ii)  Geobotanical Models of potential natural vegetation  (PNV), in particular Capelo et al. (2007); and iii) typological models of riparian geosséries established specifically in this project, based on Aguiar et al., 1995 and Portela-Pereira, 2014.&lt;br&gt;&lt;br&gt;

Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.
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          <Abstract>A determinação da potencialidade florestal poderá fazer-se com recurso a modelos preditivos da composição, em termos das espécies ecologicamente dominantes, das florestas espontâneas. Estas correspondem àquelas que não só apresentam, por princípio, a melhor adaptação ecológica (climática, edáfica) que garante a maior qualidade ambiental do Território e que corresponde aos usos extensivos em sistemas de agricultura tradicionais, mas também a novas oportunidades de paisagens rurais funcionalmente salutares.
Os modelos fundamentais que exprimem os pressupostos ecológicos que foram utilizados no desenvolvimento da metodologia utilizada na determinação deste tipo de aptidão são de três tipos: i) Modelos de Distribuição de Espécies (SDM-Species Distribution Models); ii) Modelos geobotânicos de Vegetação Natural Potencial (VNP), em particular o de Capelo et al. (2007); e iii) Modelos tipológicos de geosséries ripícolas, estabelecidos especificamente no âmbito deste projeto, a partir de Aguiar et al., 1995 e Portela-Pereira, 2014.

&lt;br&gt;Cartografia da área de aptidão à instalação de povoamentos da espécie arbórea Pinus sylvestris. Modelo VNP. Séries Saxifrago-Betuleto celtiberica Sigmetum e Lycopodio clavati-Junipero nani S. Não existem dados sistemáticos de ocorrência desta espécie, pelo que a cartografia da sua área de ocorrência só pode ser feita com recurso a modelos geobotânicos.&lt;br&gt;&lt;br&gt;Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.

&lt;br&gt;&lt;br&gt;Bioclimatic Suitability to Tree Species&lt;br&gt;
The determination of forest potential can be made using the predictive models of the composition, in terms of ecologically dominant species of spontaneous forests. These correspond to those who not only have, in principle, the best ecological adaptation (climate, edaphic) that guarantees the highest environmental quality of the territory and which corresponds to extended use in traditional farming systems, but also to new opportunities for functionally salutary countryside .
The basic models that express the ecological assumptions that were used in the development of the methodology used in determining this type of suitability are of three types: i) Species Distribution Models (SDM-Species Distribution Models); ii)  Geobotanical Models of potential natural vegetation  (PNV), in particular Capelo et al. (2007); and iii) typological models of riparian geosséries established specifically in this project, based on Aguiar et al., 1995 and Portela-Pereira, 2014.&lt;br&gt;&lt;br&gt;

Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.
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          <Abstract>A determinação da potencialidade florestal poderá fazer-se com recurso a modelos preditivos da composição, em termos das espécies ecologicamente dominantes, das florestas espontâneas. Estas correspondem àquelas que não só apresentam, por princípio, a melhor adaptação ecológica (climática, edáfica) que garante a maior qualidade ambiental do Território e que corresponde aos usos extensivos em sistemas de agricultura tradicionais, mas também a novas oportunidades de paisagens rurais funcionalmente salutares.
Os modelos fundamentais que exprimem os pressupostos ecológicos que foram utilizados no desenvolvimento da metodologia utilizada na determinação deste tipo de aptidão são de três tipos: i) Modelos de Distribuição de Espécies (SDM-Species Distribution Models); ii) Modelos geobotânicos de Vegetação Natural Potencial (VNP), em particular o de Capelo et al. (2007); e iii) Modelos tipológicos de geosséries ripícolas, estabelecidos especificamente no âmbito deste projeto, a partir de Aguiar et al., 1995 e Portela-Pereira, 2014.

&lt;br&gt;Cartografia da área de aptidão à instalação de povoamentos da espécie arbórea Quercus coccifera. Modelo VNP. Séries Arisaro clusi-Querco broteroi Sigmetum, Asparago aphylli-Querco suberis S., Lonicero implexae-Querco rotundifoliae S., Osyrio quadripartitae-Junipero turbinatae S., Querco-Junipero turbinatae S., Rhamno olioidis-Querco rotundifoliae S. e mosaicos com Viburno tini-Querco rivas-martinezii S. Não existem dados sistemáticos de ocorrência desta espécie, pelo que a cartografia da sua área de ocorrência só pode ser feita com recurso a modelos geobotânicos.&lt;br&gt;&lt;br&gt;Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.

&lt;br&gt;&lt;br&gt;Bioclimatic Suitability to Tree Species&lt;br&gt;
The determination of forest potential can be made using the predictive models of the composition, in terms of ecologically dominant species of spontaneous forests. These correspond to those who not only have, in principle, the best ecological adaptation (climate, edaphic) that guarantees the highest environmental quality of the territory and which corresponds to extended use in traditional farming systems, but also to new opportunities for functionally salutary countryside .
The basic models that express the ecological assumptions that were used in the development of the methodology used in determining this type of suitability are of three types: i) Species Distribution Models (SDM-Species Distribution Models); ii)  Geobotanical Models of potential natural vegetation  (PNV), in particular Capelo et al. (2007); and iii) typological models of riparian geosséries established specifically in this project, based on Aguiar et al., 1995 and Portela-Pereira, 2014.&lt;br&gt;&lt;br&gt;

Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.
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          <Abstract>A determinação da potencialidade florestal poderá fazer-se com recurso a modelos preditivos da composição, em termos das espécies ecologicamente dominantes, das florestas espontâneas. Estas correspondem àquelas que não só apresentam, por princípio, a melhor adaptação ecológica (climática, edáfica) que garante a maior qualidade ambiental do Território e que corresponde aos usos extensivos em sistemas de agricultura tradicionais, mas também a novas oportunidades de paisagens rurais funcionalmente salutares.
Os modelos fundamentais que exprimem os pressupostos ecológicos que foram utilizados no desenvolvimento da metodologia utilizada na determinação deste tipo de aptidão são de três tipos: i) Modelos de Distribuição de Espécies (SDM-Species Distribution Models); ii) Modelos geobotânicos de Vegetação Natural Potencial (VNP), em particular o de Capelo et al. (2007); e iii) Modelos tipológicos de geosséries ripícolas, estabelecidos especificamente no âmbito deste projeto, a partir de Aguiar et al., 1995 e Portela-Pereira, 2014.

&lt;br&gt;Cartografia da área de aptidão à instalação de povoamentos da espécie arbórea Quercus faginea. Modelo VNP. Séries Arisaro clusi-Querco broteroi Sigmetum, Asparago aphylli-Querco suberis S., Junipero lagunae-Querco suberis S., Lonicero implexae-Querco rotundifoliae S., Sanguisorbo agrimonioidis-Q. suberis S., Teucrio baetici-Querco suberis S. e Viburno tini-Querco rivas-martinezii. S e respectivos mosaicos. Tal como no caso da azinheira, o melhor modelo GLM elaborado para o carvalho-cerquinho teve uma boa aderência aos dados, com um coeficiente de correlação de 0,72, mas revelou-se pouco adequado quando implementado em SIG. Isto decorre do facto de esta espécie ocorrer geralmente em bosques mistos com as restantes espécies do género Quercus, sendo frequentemente co-dominante, pelo que é preterida no que respeita à informação de ocorrência de espécies arbóreas. Optou-se assim por produzir cartografia com base em VNP. A área de ocorrência actual de carvalho-cerquinho estimada pelo modelo contém importantes áreas disjuntas, com expressão taxonómica ao nível subespecífico (subsp. faginea, subsp. broteroi e subsp. alpestris).&lt;br&gt;&lt;br&gt;Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.

&lt;br&gt;&lt;br&gt;Bioclimatic Suitability to Tree Species&lt;br&gt;
The determination of forest potential can be made using the predictive models of the composition, in terms of ecologically dominant species of spontaneous forests. These correspond to those who not only have, in principle, the best ecological adaptation (climate, edaphic) that guarantees the highest environmental quality of the territory and which corresponds to extended use in traditional farming systems, but also to new opportunities for functionally salutary countryside .
The basic models that express the ecological assumptions that were used in the development of the methodology used in determining this type of suitability are of three types: i) Species Distribution Models (SDM-Species Distribution Models); ii)  Geobotanical Models of potential natural vegetation  (PNV), in particular Capelo et al. (2007); and iii) typological models of riparian geosséries established specifically in this project, based on Aguiar et al., 1995 and Portela-Pereira, 2014.&lt;br&gt;&lt;br&gt;

Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.
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          <Abstract>A determinação da potencialidade florestal poderá fazer-se com recurso a modelos preditivos da composição, em termos das espécies ecologicamente dominantes, das florestas espontâneas. Estas correspondem àquelas que não só apresentam, por princípio, a melhor adaptação ecológica (climática, edáfica) que garante a maior qualidade ambiental do Território e que corresponde aos usos extensivos em sistemas de agricultura tradicionais, mas também a novas oportunidades de paisagens rurais funcionalmente salutares.
Os modelos fundamentais que exprimem os pressupostos ecológicos que foram utilizados no desenvolvimento da metodologia utilizada na determinação deste tipo de aptidão são de três tipos: i) Modelos de Distribuição de Espécies (SDM-Species Distribution Models); ii) Modelos geobotânicos de Vegetação Natural Potencial (VNP), em particular o de Capelo et al. (2007); e iii) Modelos tipológicos de geosséries ripícolas, estabelecidos especificamente no âmbito deste projeto, a partir de Aguiar et al., 1995 e Portela-Pereira, 2014.

&lt;br&gt;Cartografia da área de aptidão à instalação de povoamentos da espécie arbórea Quercus pyrenaica. Modelo GLM; R = 0,95. O modelo do carvalho-negral, apesar da relativa raridade de pontos de ocorrência que lhe correspondem, tem uma aderência muito boa (R=0,95). Corresponde também aos limites aproximados das séries de vegetação (VNP) admitidos teoricamente pelos modelos geobotânicos como dominados por esta espécie (Capelo et al., op. cit.).&lt;br&gt;&lt;br&gt;Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.

&lt;br&gt;&lt;br&gt;Bioclimatic Suitability to Tree Species&lt;br&gt;
The determination of forest potential can be made using the predictive models of the composition, in terms of ecologically dominant species of spontaneous forests. These correspond to those who not only have, in principle, the best ecological adaptation (climate, edaphic) that guarantees the highest environmental quality of the territory and which corresponds to extended use in traditional farming systems, but also to new opportunities for functionally salutary countryside .
The basic models that express the ecological assumptions that were used in the development of the methodology used in determining this type of suitability are of three types: i) Species Distribution Models (SDM-Species Distribution Models); ii)  Geobotanical Models of potential natural vegetation  (PNV), in particular Capelo et al. (2007); and iii) typological models of riparian geosséries established specifically in this project, based on Aguiar et al., 1995 and Portela-Pereira, 2014.&lt;br&gt;&lt;br&gt;

Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.
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          <Abstract>A determinação da potencialidade florestal poderá fazer-se com recurso a modelos preditivos da composição, em termos das espécies ecologicamente dominantes, das florestas espontâneas. Estas correspondem àquelas que não só apresentam, por princípio, a melhor adaptação ecológica (climática, edáfica) que garante a maior qualidade ambiental do Território e que corresponde aos usos extensivos em sistemas de agricultura tradicionais, mas também a novas oportunidades de paisagens rurais funcionalmente salutares.
Os modelos fundamentais que exprimem os pressupostos ecológicos que foram utilizados no desenvolvimento da metodologia utilizada na determinação deste tipo de aptidão são de três tipos: i) Modelos de Distribuição de Espécies (SDM-Species Distribution Models); ii) Modelos geobotânicos de Vegetação Natural Potencial (VNP), em particular o de Capelo et al. (2007); e iii) Modelos tipológicos de geosséries ripícolas, estabelecidos especificamente no âmbito deste projeto, a partir de Aguiar et al., 1995 e Portela-Pereira, 2014.

&lt;br&gt;Modelo GLM; R = 0,95. Os dados de localização dos carvalhos de Portugal referem apenas a presença de 'carvalho', não discriminando qual das espécies está presente. Deste modo, para produzir um conjunto de treino para cada uma das três espécies a modelar, cruzou-se a informação de localização de ‘carvalhos’ com a carta de VNP, separando-se assim esta grande categoria em três grupos (parcialmente sobrepostos). Verifica-se uma aderência muito grande do mapa produzido aos limites admitidos teoricamente (R=0,95), correspondentes à área no Noroeste de Portugal com défices hídricos estivais reduzidos (Iosc4 elevado). Isto é, aproximadamente à área temperada submediterrânica de Portugal continental. A área de distribuição actual prevista é muito consistente também com o conhecimento de campo dos autores. A distribuição estimada de Quercus robur corresponde também ao mapa de distribuição potencial de Corylus avellana (aveleira) e Prunus avium (cerejeira); pode ser considerado também para Acer pseudoplatanus (bordo) e Quercus rubra (carvalho-americano), mas apenas em contexto ornamental urbano, uma vez que são espécies exóticas. Cartografia da área de aptidão à instalação de povoamentos da espécie arbórea Quercus robur.&lt;br&gt;&lt;br&gt;Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.

&lt;br&gt;&lt;br&gt;Bioclimatic Suitability to Tree Species&lt;br&gt;
The determination of forest potential can be made using the predictive models of the composition, in terms of ecologically dominant species of spontaneous forests. These correspond to those who not only have, in principle, the best ecological adaptation (climate, edaphic) that guarantees the highest environmental quality of the territory and which corresponds to extended use in traditional farming systems, but also to new opportunities for functionally salutary countryside .
The basic models that express the ecological assumptions that were used in the development of the methodology used in determining this type of suitability are of three types: i) Species Distribution Models (SDM-Species Distribution Models); ii)  Geobotanical Models of potential natural vegetation  (PNV), in particular Capelo et al. (2007); and iii) typological models of riparian geosséries established specifically in this project, based on Aguiar et al., 1995 and Portela-Pereira, 2014.&lt;br&gt;&lt;br&gt;

Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.
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          <Abstract>A determinação da potencialidade florestal poderá fazer-se com recurso a modelos preditivos da composição, em termos das espécies ecologicamente dominantes, das florestas espontâneas. Estas correspondem àquelas que não só apresentam, por princípio, a melhor adaptação ecológica (climática, edáfica) que garante a maior qualidade ambiental do Território e que corresponde aos usos extensivos em sistemas de agricultura tradicionais, mas também a novas oportunidades de paisagens rurais funcionalmente salutares.
Os modelos fundamentais que exprimem os pressupostos ecológicos que foram utilizados no desenvolvimento da metodologia utilizada na determinação deste tipo de aptidão são de três tipos: i) Modelos de Distribuição de Espécies (SDM-Species Distribution Models); ii) Modelos geobotânicos de Vegetação Natural Potencial (VNP), em particular o de Capelo et al. (2007); e iii) Modelos tipológicos de geosséries ripícolas, estabelecidos especificamente no âmbito deste projeto, a partir de Aguiar et al., 1995 e Portela-Pereira, 2014.

&lt;br&gt;Cartografia da área de aptidão à instalação de povoamentos da espécie arbórea Quercus rivasmartinezii. Modelo VNP. Séries Myrico fayaeo-Arbuto unedonis Sigmetum, Teucrio baetici-Querco suberis S., Arisaro clusi-Querco broteroi S. e mosaicos desta série com Asparago aphylli-Querco suberis S., mosaicos com Viburno tini-Querco rivas-martinezii S. Não existem dados sistemáticos de ocorrência desta espécie, pelo que a cartografia da sua área de ocorrência só pode ser feita com recurso a modelos geobotânicos.&lt;br&gt;&lt;br&gt;Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.

&lt;br&gt;&lt;br&gt;Bioclimatic Suitability to Tree Species&lt;br&gt;
The determination of forest potential can be made using the predictive models of the composition, in terms of ecologically dominant species of spontaneous forests. These correspond to those who not only have, in principle, the best ecological adaptation (climate, edaphic) that guarantees the highest environmental quality of the territory and which corresponds to extended use in traditional farming systems, but also to new opportunities for functionally salutary countryside .
The basic models that express the ecological assumptions that were used in the development of the methodology used in determining this type of suitability are of three types: i) Species Distribution Models (SDM-Species Distribution Models); ii)  Geobotanical Models of potential natural vegetation  (PNV), in particular Capelo et al. (2007); and iii) typological models of riparian geosséries established specifically in this project, based on Aguiar et al., 1995 and Portela-Pereira, 2014.&lt;br&gt;&lt;br&gt;

Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.
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          <Abstract>A determinação da potencialidade florestal poderá fazer-se com recurso a modelos preditivos da composição, em termos das espécies ecologicamente dominantes, das florestas espontâneas. Estas correspondem àquelas que não só apresentam, por princípio, a melhor adaptação ecológica (climática, edáfica) que garante a maior qualidade ambiental do Território e que corresponde aos usos extensivos em sistemas de agricultura tradicionais, mas também a novas oportunidades de paisagens rurais funcionalmente salutares.
Os modelos fundamentais que exprimem os pressupostos ecológicos que foram utilizados no desenvolvimento da metodologia utilizada na determinação deste tipo de aptidão são de três tipos: i) Modelos de Distribuição de Espécies (SDM-Species Distribution Models); ii) Modelos geobotânicos de Vegetação Natural Potencial (VNP), em particular o de Capelo et al. (2007); e iii) Modelos tipológicos de geosséries ripícolas, estabelecidos especificamente no âmbito deste projeto, a partir de Aguiar et al., 1995 e Portela-Pereira, 2014.

&lt;br&gt;Cartografia da área de aptidão à instalação de povoamentos das espécies arbóreas ribeirinhas. Modelos tipológicos de geosséries ripícolas, estabelecidos especificamente no âmbito deste projeto, a partir de Aguiar et al., 1995 e Portela-Pereira, 2014. Não existem dados sistemáticos de ocorrência destas espécies, pelo que a cartografia da sua área de ocorrência só pode ser feita com recurso a modelos geobotânicos. Ag: Alnus glutinosa (amieiro); Bp: Betula pubescens (vidoeiro); Ca: Celtis australis (lodão-bastardo); Fa: Fraxinus angustifolia (freixo); Pa: Populus alba (choupo-branco); Pn: Populus nigra (choupo); Sa: Salix atrocinerea (borrazeira-preta); Sal: Salix alba (salgueiro-branco); Sn: Salix neotricha (vimeiro); Ss: Salix salviifolia (borrazeira-branca)&lt;br&gt;&lt;br&gt;Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.

&lt;br&gt;&lt;br&gt;Bioclimatic Suitability to Tree Species&lt;br&gt;
The determination of forest potential can be made using the predictive models of the composition, in terms of ecologically dominant species of spontaneous forests. These correspond to those who not only have, in principle, the best ecological adaptation (climate, edaphic) that guarantees the highest environmental quality of the territory and which corresponds to extended use in traditional farming systems, but also to new opportunities for functionally salutary countryside .
The basic models that express the ecological assumptions that were used in the development of the methodology used in determining this type of suitability are of three types: i) Species Distribution Models (SDM-Species Distribution Models); ii)  Geobotanical Models of potential natural vegetation  (PNV), in particular Capelo et al. (2007); and iii) typological models of riparian geosséries established specifically in this project, based on Aguiar et al., 1995 and Portela-Pereira, 2014.&lt;br&gt;&lt;br&gt;

Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.
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          <Abstract>A determinação da potencialidade florestal poderá fazer-se com recurso a modelos preditivos da composição, em termos das espécies ecologicamente dominantes, das florestas espontâneas. Estas correspondem àquelas que não só apresentam, por princípio, a melhor adaptação ecológica (climática, edáfica) que garante a maior qualidade ambiental do Território e que corresponde aos usos extensivos em sistemas de agricultura tradicionais, mas também a novas oportunidades de paisagens rurais funcionalmente salutares.
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&lt;br&gt;Cartografia da área de aptidão à instalação de povoamentos da espécie arbórea Salix atrocinerea. Modelo tipológico de geosséries ripícolas. Linhas de água e aluviões em todo o país.&lt;br&gt;&lt;br&gt;Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.

&lt;br&gt;&lt;br&gt;Bioclimatic Suitability to Tree Species&lt;br&gt;
The determination of forest potential can be made using the predictive models of the composition, in terms of ecologically dominant species of spontaneous forests. These correspond to those who not only have, in principle, the best ecological adaptation (climate, edaphic) that guarantees the highest environmental quality of the territory and which corresponds to extended use in traditional farming systems, but also to new opportunities for functionally salutary countryside .
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Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.
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          <Abstract>A determinação da potencialidade florestal poderá fazer-se com recurso a modelos preditivos da composição, em termos das espécies ecologicamente dominantes, das florestas espontâneas. Estas correspondem àquelas que não só apresentam, por princípio, a melhor adaptação ecológica (climática, edáfica) que garante a maior qualidade ambiental do Território e que corresponde aos usos extensivos em sistemas de agricultura tradicionais, mas também a novas oportunidades de paisagens rurais funcionalmente salutares.
Os modelos fundamentais que exprimem os pressupostos ecológicos que foram utilizados no desenvolvimento da metodologia utilizada na determinação deste tipo de aptidão são de três tipos: i) Modelos de Distribuição de Espécies (SDM-Species Distribution Models); ii) Modelos geobotânicos de Vegetação Natural Potencial (VNP), em particular o de Capelo et al. (2007); e iii) Modelos tipológicos de geosséries ripícolas, estabelecidos especificamente no âmbito deste projeto, a partir de Aguiar et al., 1995 e Portela-Pereira, 2014.

&lt;br&gt;Cartografia da área de aptidão à instalação de povoamentos da espécie arbórea Salix atrocinerea. Modelo tipológico de geosséries ripícolas. Linhas de água e aluviões em todo o país.&lt;br&gt;&lt;br&gt;Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.

&lt;br&gt;&lt;br&gt;Bioclimatic Suitability to Tree Species&lt;br&gt;
The determination of forest potential can be made using the predictive models of the composition, in terms of ecologically dominant species of spontaneous forests. These correspond to those who not only have, in principle, the best ecological adaptation (climate, edaphic) that guarantees the highest environmental quality of the territory and which corresponds to extended use in traditional farming systems, but also to new opportunities for functionally salutary countryside .
The basic models that express the ecological assumptions that were used in the development of the methodology used in determining this type of suitability are of three types: i) Species Distribution Models (SDM-Species Distribution Models); ii)  Geobotanical Models of potential natural vegetation  (PNV), in particular Capelo et al. (2007); and iii) typological models of riparian geosséries established specifically in this project, based on Aguiar et al., 1995 and Portela-Pereira, 2014.&lt;br&gt;&lt;br&gt;

Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.
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          <Abstract>A determinação da potencialidade florestal poderá fazer-se com recurso a modelos preditivos da composição, em termos das espécies ecologicamente dominantes, das florestas espontâneas. Estas correspondem àquelas que não só apresentam, por princípio, a melhor adaptação ecológica (climática, edáfica) que garante a maior qualidade ambiental do Território e que corresponde aos usos extensivos em sistemas de agricultura tradicionais, mas também a novas oportunidades de paisagens rurais funcionalmente salutares.
Os modelos fundamentais que exprimem os pressupostos ecológicos que foram utilizados no desenvolvimento da metodologia utilizada na determinação deste tipo de aptidão são de três tipos: i) Modelos de Distribuição de Espécies (SDM-Species Distribution Models); ii) Modelos geobotânicos de Vegetação Natural Potencial (VNP), em particular o de Capelo et al. (2007); e iii) Modelos tipológicos de geosséries ripícolas, estabelecidos especificamente no âmbito deste projeto, a partir de Aguiar et al., 1995 e Portela-Pereira, 2014.

&lt;br&gt;Cartografia da área de aptidão à instalação de povoamentos da espécie arbórea Quercus suber. Modelo CART, alterado manualmente; R = 0,61. A distribuição prevista corresponde a um modelo CART com R=0,61 e expressa genericamente os intervalos que correspondem a situação de óptimo climático do sobreiro. As observações externas à área prevista correspondem maioritariamente a observações climaticamente marginais em situações mistas com outras espécies (azinheira, carvalhos). Os principais factores que parecem controlar a distribuição do sobreiro são a secura (expressa pelo índice ombrotérmico), que determina o limite inferior da existência da Quercus suber para valores elevados e ainda a quantidade de frio invernal (expressa por baixos Itc), maior em altitude e na metade interior do país. Esta espécie tende a rarear em solos de origem calcária (cuja cartografia, no entanto, é pouco precisa, sobretudo pela pequena dimensão das áreas calcárias quando em estratos alternados com outros tipos de litologias).&lt;br&gt;&lt;br&gt;Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.

&lt;br&gt;&lt;br&gt;Bioclimatic Suitability to Tree Species&lt;br&gt;
The determination of forest potential can be made using the predictive models of the composition, in terms of ecologically dominant species of spontaneous forests. These correspond to those who not only have, in principle, the best ecological adaptation (climate, edaphic) that guarantees the highest environmental quality of the territory and which corresponds to extended use in traditional farming systems, but also to new opportunities for functionally salutary countryside .
The basic models that express the ecological assumptions that were used in the development of the methodology used in determining this type of suitability are of three types: i) Species Distribution Models (SDM-Species Distribution Models); ii)  Geobotanical Models of potential natural vegetation  (PNV), in particular Capelo et al. (2007); and iii) typological models of riparian geosséries established specifically in this project, based on Aguiar et al., 1995 and Portela-Pereira, 2014.&lt;br&gt;&lt;br&gt;

Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.
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          <Abstract>A Aptidão Edafo-Morfológica é uma aptidão parcial dependente das condições de solo, morfologia do terreno e declive. Esta aptidão foi determinada para a Agricultura de Sequeiro e de Regadio e para a Silvicultura e teve por objectivo restringir as Aptidões às Culturas Agrícolas e às Espécies Arbóreas/Pastagens às condições mais adequadas relativamente aos parâmetros referidos.
A Aptidão Edafo-Morfológica à Agricultura de Sequeiro foi determinada a partir de uma matriz que integra o valor ecológico do solo com a morfologia do terreno e o declive.
&lt;br&gt;&lt;br&gt;
Silviculture&lt;br&gt;
The Soil and Morphological Suitability is a partial suitability dependent on soil, land morphology and slope conditions. This suitability was determined for the Rainfed and Irrigated Agriculture and the Silviculture and aimed to restrict the suitability to Agricultural Crops and Tree Species / Pastures to the most suitable conditions in respect of those parameters.
The Soil and Morphological Suitability for Rainfed Agriculture was determined from an array that integrates the ecological value of the soil with the land morphology and the slope.</Abstract>
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          <Abstract>A determinação da potencialidade florestal poderá fazer-se com recurso a modelos preditivos da composição, em termos das espécies ecologicamente dominantes, das florestas espontâneas. Estas correspondem àquelas que não só apresentam, por princípio, a melhor adaptação ecológica (climática, edáfica) que garante a maior qualidade ambiental do Território e que corresponde aos usos extensivos em sistemas de agricultura tradicionais, mas também a novas oportunidades de paisagens rurais funcionalmente salutares.
Os modelos fundamentais que exprimem os pressupostos ecológicos que foram utilizados no desenvolvimento da metodologia utilizada na determinação deste tipo de aptidão são de três tipos: i) Modelos de Distribuição de Espécies (SDM-Species Distribution Models); ii) Modelos geobotânicos de Vegetação Natural Potencial (VNP), em particular o de Capelo et al. (2007); e iii) Modelos tipológicos de geosséries ripícolas, estabelecidos especificamente no âmbito deste projeto, a partir de Aguiar et al., 1995 e Portela-Pereira, 2014.

&lt;br&gt;Cartografia da área de aptidão à instalação de povoamentos da espécie arbórea Salix neotricha. Modelo tipológico de geosséries ripícolas. Linhas de água e aluviões de toda a Província Carpetano-Ibérico-Leonesa e do Superdistrito Ribatagano.&lt;br&gt;&lt;br&gt;Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.

&lt;br&gt;&lt;br&gt;Bioclimatic Suitability to Tree Species&lt;br&gt;
The determination of forest potential can be made using the predictive models of the composition, in terms of ecologically dominant species of spontaneous forests. These correspond to those who not only have, in principle, the best ecological adaptation (climate, edaphic) that guarantees the highest environmental quality of the territory and which corresponds to extended use in traditional farming systems, but also to new opportunities for functionally salutary countryside .
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Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.
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          <Abstract>A determinação da potencialidade florestal poderá fazer-se com recurso a modelos preditivos da composição, em termos das espécies ecologicamente dominantes, das florestas espontâneas. Estas correspondem àquelas que não só apresentam, por princípio, a melhor adaptação ecológica (climática, edáfica) que garante a maior qualidade ambiental do Território e que corresponde aos usos extensivos em sistemas de agricultura tradicionais, mas também a novas oportunidades de paisagens rurais funcionalmente salutares.
Os modelos fundamentais que exprimem os pressupostos ecológicos que foram utilizados no desenvolvimento da metodologia utilizada na determinação deste tipo de aptidão são de três tipos: i) Modelos de Distribuição de Espécies (SDM-Species Distribution Models); ii) Modelos geobotânicos de Vegetação Natural Potencial (VNP), em particular o de Capelo et al. (2007); e iii) Modelos tipológicos de geosséries ripícolas, estabelecidos especificamente no âmbito deste projeto, a partir de Aguiar et al., 1995 e Portela-Pereira, 2014.

&lt;br&gt;Cartografia da área de aptidão à instalação de povoamentos da espécie arbórea Salix salviifolia. Modelo tipológico de geosséries ripícolas. Linhas de água e aluviões em todo o país.&lt;br&gt;&lt;br&gt;Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.

&lt;br&gt;&lt;br&gt;Bioclimatic Suitability to Tree Species&lt;br&gt;
The determination of forest potential can be made using the predictive models of the composition, in terms of ecologically dominant species of spontaneous forests. These correspond to those who not only have, in principle, the best ecological adaptation (climate, edaphic) that guarantees the highest environmental quality of the territory and which corresponds to extended use in traditional farming systems, but also to new opportunities for functionally salutary countryside .
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Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.
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          <Abstract>A determinação da potencialidade florestal poderá fazer-se com recurso a modelos preditivos da composição, em termos das espécies ecologicamente dominantes, das florestas espontâneas. Estas correspondem àquelas que não só apresentam, por princípio, a melhor adaptação ecológica (climática, edáfica) que garante a maior qualidade ambiental do Território e que corresponde aos usos extensivos em sistemas de agricultura tradicionais, mas também a novas oportunidades de paisagens rurais funcionalmente salutares.
Os modelos fundamentais que exprimem os pressupostos ecológicos que foram utilizados no desenvolvimento da metodologia utilizada na determinação deste tipo de aptidão são de três tipos: i) Modelos de Distribuição de Espécies (SDM-Species Distribution Models); ii) Modelos geobotânicos de Vegetação Natural Potencial (VNP), em particular o de Capelo et al. (2007); e iii) Modelos tipológicos de geosséries ripícolas, estabelecidos especificamente no âmbito deste projeto, a partir de Aguiar et al., 1995 e Portela-Pereira, 2014.

&lt;br&gt;Cartografia da área de aptidão à instalação de povoamentos da espécie arbórea Taxus baccata. Modelo VNP. Séries Saxifrago-Betuleto celtiberica Sigmetum, Vaccinio-Querco roboris S. e Lycopodio clavati-Junipero nani S. O teixo espontâneo é raro em Portugal, e a localização dos poucos exemplares existentes é conhecida, estando praticamente restrita às serras do Gerês e da Estrela, sendo relativamente frequente na primeira e bastante raro na segunda. Estas localizações não são suficientes para gerar um modelo estatístico, pelo que o mesmo foi aproximado com recurso a modelos geobotânicos.&lt;br&gt;&lt;br&gt;Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.

&lt;br&gt;&lt;br&gt;Bioclimatic Suitability to Tree Species&lt;br&gt;
The determination of forest potential can be made using the predictive models of the composition, in terms of ecologically dominant species of spontaneous forests. These correspond to those who not only have, in principle, the best ecological adaptation (climate, edaphic) that guarantees the highest environmental quality of the territory and which corresponds to extended use in traditional farming systems, but also to new opportunities for functionally salutary countryside .
The basic models that express the ecological assumptions that were used in the development of the methodology used in determining this type of suitability are of three types: i) Species Distribution Models (SDM-Species Distribution Models); ii)  Geobotanical Models of potential natural vegetation  (PNV), in particular Capelo et al. (2007); and iii) typological models of riparian geosséries established specifically in this project, based on Aguiar et al., 1995 and Portela-Pereira, 2014.&lt;br&gt;&lt;br&gt;

Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.
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          <Abstract>A determinação da potencialidade florestal poderá fazer-se com recurso a modelos preditivos da composição, em termos das espécies ecologicamente dominantes, das florestas espontâneas. Estas correspondem àquelas que não só apresentam, por princípio, a melhor adaptação ecológica (climática, edáfica) que garante a maior qualidade ambiental do Território e que corresponde aos usos extensivos em sistemas de agricultura tradicionais, mas também a novas oportunidades de paisagens rurais funcionalmente salutares.
Os modelos fundamentais que exprimem os pressupostos ecológicos que foram utilizados no desenvolvimento da metodologia utilizada na determinação deste tipo de aptidão são de três tipos: i) Modelos de Distribuição de Espécies (SDM-Species Distribution Models); ii) Modelos geobotânicos de Vegetação Natural Potencial (VNP), em particular o de Capelo et al. (2007); e iii) Modelos tipológicos de geosséries ripícolas, estabelecidos especificamente no âmbito deste projeto, a partir de Aguiar et al., 1995 e Portela-Pereira, 2014.

&lt;br&gt;Cartografia da área de aptidão à instalação de povoamentos da espécie arbórea Olea europaea subsp. sylvestris. Modelo VNP. Séries Arbuto unedonis-Querco pyrenaicae Sigmetum, Arisaro clusi-Querco broteroi S., Asparago aphylli-Querco suberis S., Genisto falcatae-Querco pyrenaicae S., Genisto histricis-Querco rotundifoliae S., Junipero lagunae-Querco suberis S. , Rusco-Juniperetum lagunae S., Lonicero implexae-Querco rotundifoliae S., Myrto-Querco rotundifoliae S., Oleo sylvestris-Querco suberis S., Physospermo cornubiensis-Querco suberis S., Pyro bourgaeanae-Querco rotundifoliae S., Rhamno oleoidis-Querco rotundifoliae S. , Sanguisorbo agrimonioidis-Q. suberis S., Teucrio baetici-Querco suberis S., Viburno tini-Oleo sylvestris S., Viburno tini-Querco rivas-martinezii S., Phlomido-Junipero turbinatae S., Smilaco-Querco suberis S. e Pistacio-Junipero badiae S., assim como mosaicos que combinem duas destas séries. As incertezas de natureza taxonómica relativamente aos ‘zambujeiros’ (Olea europaea subsp. sylvestris) traduzem-se na inclusão, sob este nome, de árvores espontâneas e indivíduos de oliveira doméstica assilvestrados e ainda de retrocruzamentos genéticos reticulados e difíceis de destrinçar. Por isso mesmo, a modelação utilizada é, talvez, demasiado genérica e baseia-se na ocorrência indiferente de oliveiras ou zambujeiros nas referidas séries de vegetação. Sendo indiferente edáfica, a Olea europaea tem aptidão por macrobioclima mediterrânico, i.e., com mais de dois meses de secura estival, ou seja, ocorre na maioria do território, excepto nas cotas mais altas das serras. Os zambujeiros arbóreos parecem ter a maior aptidão como espécie dominante, por vezes em bosques mistos com alfarrobeiras, nos territórios de poucas geadas (termomediterrânicos) e em solos argilosos.&lt;br&gt;&lt;br&gt;Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.

&lt;br&gt;&lt;br&gt;Bioclimatic Suitability to Tree Species&lt;br&gt;
The determination of forest potential can be made using the predictive models of the composition, in terms of ecologically dominant species of spontaneous forests. These correspond to those who not only have, in principle, the best ecological adaptation (climate, edaphic) that guarantees the highest environmental quality of the territory and which corresponds to extended use in traditional farming systems, but also to new opportunities for functionally salutary countryside .
The basic models that express the ecological assumptions that were used in the development of the methodology used in determining this type of suitability are of three types: i) Species Distribution Models (SDM-Species Distribution Models); ii)  Geobotanical Models of potential natural vegetation  (PNV), in particular Capelo et al. (2007); and iii) typological models of riparian geosséries established specifically in this project, based on Aguiar et al., 1995 and Portela-Pereira, 2014.&lt;br&gt;&lt;br&gt;

Aguiar C., Capelo J., Costa J.C., Espírito-Santo M.D., Lousã M., 1995. Tipologia das Geosséries Ripícolas Mediterrânicas de Portugal Continental. Actas do V Congresso de Áreas Protegidas. ICN. Lisboa.
&lt;br&gt;Portela-Pereira, E., 2014. Análise Geobotânica dos Bosques e Galerias Ripícolas da Bacia Hidrográfica do Tejo em Portugal. PhD em Geografia Física, IGOT-UL, Lisboa.
&lt;br&gt;Capelo, J., Mesquita, S., Costa, J.C., Ribeiro, S., Arsénio, P., Neto, C., Monteiro, T., Aguiar, C., Honrado J., Espírito-Santo, M.D., Lousã, M., 2007. A methodological approach to potential vegetation modeling using GIS techniques and phytosociological expert-knowledge: application to mainland Portugal. Phytocoenologia 37(3-4): 399-415.
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          <Abstract>A Aptidão Integrada às Espécies Arbóreas resulta da integração entre a  Carta de Aptidão Edafo-morfológica à Silvicultura e as Cartas de Aptidão Bioclimática a cada uma das Espécies Arbóreas e às Pastagens. Esta integração obtém, para cada uma das Espécies Arbóreas, uma localização mais rigorosa, dependendo do valor ecológico do solo, da morfologia do terreno e do declive.
				&lt;br&gt;&lt;br&gt;
Integrated Suitability for Tree Species&lt;br&gt;
Integrated Suitability for Tree Species results from the integration of the Soil and Morphological Suitability to Silviculture map and the Bioclimatic Suitability to each of Tree Species and Pastures map. This integration obtains, for each tree species, a more accurate location, depending on the ecological value of soil, the land morphology and the slope.</Abstract>
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          <Abstract>A Aptidão Integrada às Culturas Agrícolas em Sequeiro resulta da integração entre a  Aptidão Edafo-morfológica à Agricultura de Sequeiro (classes 3, 4, e 5) e as Cartas de Aptidão a cada uma das Culturas Agrícolas em sequeiro. Esta integração obtém, para cada uma das Culturas Agrícolas em Sequeiro, uma localização mais rigorosa, dependendo do valor ecológico do solo, da morfologia do terreno e do declive.
				&lt;br&gt;&lt;br&gt;
				Integrated Suitability for Rainfed Agricultural Crops&lt;br&gt;
Integrated Suitability for Rainfed Agricultural Crops results from the integration of Soil and Morphological Suitability for Rainfed Agriculture map (classes 3, 4, and 5) and the Suitability to each of the rainfed agricultural crops maps. This integration gets, for each of Rainfed Agricultural Crops, a more stringent location, depending on the ecological value of the soil, the terrain morphology and slope.</Abstract>
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          <Abstract>A Aptidão Integrada às Espécies Arbóreas resulta da integração entre a  Carta de Aptidão Edafo-morfológica à Silvicultura e as Cartas de Aptidão Bioclimática a cada uma das Espécies Arbóreas e às Pastagens. Esta integração obtém, para cada uma das Espécies Arbóreas, uma localização mais rigorosa, dependendo do valor ecológico do solo, da morfologia do terreno e do declive.
				&lt;br&gt;&lt;br&gt;
Integrated Suitability for Tree Species&lt;br&gt;
Integrated Suitability for Tree Species results from the integration of the Soil and Morphological Suitability to Silviculture map and the Bioclimatic Suitability to each of Tree Species and Pastures map. This integration obtains, for each tree species, a more accurate location, depending on the ecological value of soil, the land morphology and the slope.</Abstract>
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				&lt;br&gt;&lt;br&gt;
Integrated Suitability for Tree Species&lt;br&gt;
Integrated Suitability for Tree Species results from the integration of the Soil and Morphological Suitability to Silviculture map and the Bioclimatic Suitability to each of Tree Species and Pastures map. This integration obtains, for each tree species, a more accurate location, depending on the ecological value of soil, the land morphology and the slope.</Abstract>
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				&lt;br&gt;&lt;br&gt;
Integrated Suitability for Tree Species&lt;br&gt;
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				&lt;br&gt;&lt;br&gt;
				Integrated Suitability for Rainfed Agricultural Crops&lt;br&gt;
Integrated Suitability for Rainfed Agricultural Crops results from the integration of Soil and Morphological Suitability for Rainfed Agriculture map (classes 3, 4, and 5) and the Suitability to each of the rainfed agricultural crops maps. This integration gets, for each of Rainfed Agricultural Crops, a more stringent location, depending on the ecological value of the soil, the terrain morphology and slope.</Abstract>
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				&lt;br&gt;&lt;br&gt;
Integrated Suitability for Tree Species&lt;br&gt;
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				&lt;br&gt;&lt;br&gt;
Integrated Suitability for Tree Species&lt;br&gt;
Integrated Suitability for Tree Species results from the integration of the Soil and Morphological Suitability to Silviculture map and the Bioclimatic Suitability to each of Tree Species and Pastures map. This integration obtains, for each tree species, a more accurate location, depending on the ecological value of soil, the land morphology and the slope.</Abstract>
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          <Abstract>A Aptidão Integrada às Culturas Agrícolas em Sequeiro resulta da integração entre a  Aptidão Edafo-morfológica à Agricultura de Sequeiro (classes 3, 4, e 5) e as Cartas de Aptidão a cada uma das Culturas Agrícolas em sequeiro. Esta integração obtém, para cada uma das Culturas Agrícolas em Sequeiro, uma localização mais rigorosa, dependendo do valor ecológico do solo, da morfologia do terreno e do declive.
				&lt;br&gt;&lt;br&gt;
				Integrated Suitability for Rainfed Agricultural Crops&lt;br&gt;
Integrated Suitability for Rainfed Agricultural Crops results from the integration of Soil and Morphological Suitability for Rainfed Agriculture map (classes 3, 4, and 5) and the Suitability to each of the rainfed agricultural crops maps. This integration gets, for each of Rainfed Agricultural Crops, a more stringent location, depending on the ecological value of the soil, the terrain morphology and slope.</Abstract>
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				&lt;br&gt;&lt;br&gt;
Integrated Suitability for Tree Species&lt;br&gt;
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          <Abstract>A Aptidão Integrada às Espécies Arbóreas resulta da integração entre a  Carta de Aptidão Edafo-morfológica à Silvicultura e as Cartas de Aptidão Bioclimática a cada uma das Espécies Arbóreas e às Pastagens. Esta integração obtém, para cada uma das Espécies Arbóreas, uma localização mais rigorosa, dependendo do valor ecológico do solo, da morfologia do terreno e do declive.
				&lt;br&gt;&lt;br&gt;
Integrated Suitability for Tree Species&lt;br&gt;
Integrated Suitability for Tree Species results from the integration of the Soil and Morphological Suitability to Silviculture map and the Bioclimatic Suitability to each of Tree Species and Pastures map. This integration obtains, for each tree species, a more accurate location, depending on the ecological value of soil, the land morphology and the slope.</Abstract>
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          <Abstract>A Aptidão Integrada às Culturas Agrícolas em Sequeiro resulta da integração entre a  Aptidão Edafo-morfológica à Agricultura de Sequeiro (classes 3, 4, e 5) e as Cartas de Aptidão a cada uma das Culturas Agrícolas em sequeiro. Esta integração obtém, para cada uma das Culturas Agrícolas em Sequeiro, uma localização mais rigorosa, dependendo do valor ecológico do solo, da morfologia do terreno e do declive.
				&lt;br&gt;&lt;br&gt;
				Integrated Suitability for Rainfed Agricultural Crops&lt;br&gt;
Integrated Suitability for Rainfed Agricultural Crops results from the integration of Soil and Morphological Suitability for Rainfed Agriculture map (classes 3, 4, and 5) and the Suitability to each of the rainfed agricultural crops maps. This integration gets, for each of Rainfed Agricultural Crops, a more stringent location, depending on the ecological value of the soil, the terrain morphology and slope.</Abstract>
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          <Abstract>A Aptidão Integrada às Culturas Agrícolas em Sequeiro resulta da integração entre a  Aptidão Edafo-morfológica à Agricultura de Sequeiro (classes 3, 4, e 5) e as Cartas de Aptidão a cada uma das Culturas Agrícolas em sequeiro. Esta integração obtém, para cada uma das Culturas Agrícolas em Sequeiro, uma localização mais rigorosa, dependendo do valor ecológico do solo, da morfologia do terreno e do declive.
				&lt;br&gt;&lt;br&gt;
				Integrated Suitability for Rainfed Agricultural Crops&lt;br&gt;
Integrated Suitability for Rainfed Agricultural Crops results from the integration of Soil and Morphological Suitability for Rainfed Agriculture map (classes 3, 4, and 5) and the Suitability to each of the rainfed agricultural crops maps. This integration gets, for each of Rainfed Agricultural Crops, a more stringent location, depending on the ecological value of the soil, the terrain morphology and slope.
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          <Title>Aptidão Integrada às Pastagens Espontâneas</Title>
          <Abstract>A determinação deste tipo de Aptidão resultou da integração entre a Carta de Aptidão Edafo-morfológica à Silvicultura  e a Carta de Aptidão Bioclimática às Pastagens Espontâneas&lt;br&gt;&lt;br&gt;
Integrated Suitability to Spontaneous Pastures&lt;br&gt;
The determination of this type of suitability resulted from the integration of map of Soil and Morphological Suitability to Silviculture and the map of Bioclimatic Suitability to Spontaneous Pastures.</Abstract>
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          <Abstract>A Aptidão Integrada às Espécies Arbóreas resulta da integração entre a  Carta de Aptidão Edafo-morfológica à Silvicultura e as Cartas de Aptidão Bioclimática a cada uma das Espécies Arbóreas e às Pastagens. Esta integração obtém, para cada uma das Espécies Arbóreas, uma localização mais rigorosa, dependendo do valor ecológico do solo, da morfologia do terreno e do declive.
				&lt;br&gt;&lt;br&gt;
Integrated Suitability for Tree Species&lt;br&gt;
Integrated Suitability for Tree Species results from the integration of the Soil and Morphological Suitability to Silviculture map and the Bioclimatic Suitability to each of Tree Species and Pastures map. This integration obtains, for each tree species, a more accurate location, depending on the ecological value of soil, the land morphology and the slope.</Abstract>
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				&lt;br&gt;&lt;br&gt;
Integrated Suitability for Tree Species&lt;br&gt;
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				&lt;br&gt;&lt;br&gt;
Integrated Suitability for Tree Species&lt;br&gt;
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Integrated Suitability for Tree Species&lt;br&gt;
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				&lt;br&gt;&lt;br&gt;
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				&lt;br&gt;&lt;br&gt;
Integrated Suitability for Tree Species&lt;br&gt;
Integrated Suitability for Tree Species results from the integration of the Soil and Morphological Suitability to Silviculture map and the Bioclimatic Suitability to each of Tree Species and Pastures map. This integration obtains, for each tree species, a more accurate location, depending on the ecological value of soil, the land morphology and the slope.</Abstract>
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				&lt;br&gt;&lt;br&gt;
				Integrated Suitability for Rainfed Agricultural Crops&lt;br&gt;
Integrated Suitability for Rainfed Agricultural Crops results from the integration of Soil and Morphological Suitability for Rainfed Agriculture map (classes 3, 4, and 5) and the Suitability to each of the rainfed agricultural crops maps. This integration gets, for each of Rainfed Agricultural Crops, a more stringent location, depending on the ecological value of the soil, the terrain morphology and slope.</Abstract>
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				&lt;br&gt;&lt;br&gt;
Integrated Suitability for Tree Species&lt;br&gt;
Integrated Suitability for Tree Species results from the integration of the Soil and Morphological Suitability to Silviculture map and the Bioclimatic Suitability to each of Tree Species and Pastures map. This integration obtains, for each tree species, a more accurate location, depending on the ecological value of soil, the land morphology and the slope.</Abstract>
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          <Abstract>A Aptidão Integrada às Culturas Agrícolas em Sequeiro resulta da integração entre a  Aptidão Edafo-morfológica à Agricultura de Sequeiro (classes 3, 4, e 5) e as Cartas de Aptidão a cada uma das Culturas Agrícolas em sequeiro. Esta integração obtém, para cada uma das Culturas Agrícolas em Sequeiro, uma localização mais rigorosa, dependendo do valor ecológico do solo, da morfologia do terreno e do declive.
				&lt;br&gt;&lt;br&gt;
				Integrated Suitability for Rainfed Agricultural Crops&lt;br&gt;
Integrated Suitability for Rainfed Agricultural Crops results from the integration of Soil and Morphological Suitability for Rainfed Agriculture map (classes 3, 4, and 5) and the Suitability to each of the rainfed agricultural crops maps. This integration gets, for each of Rainfed Agricultural Crops, a more stringent location, depending on the ecological value of the soil, the terrain morphology and slope.</Abstract>
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          <Abstract>A Aptidão Integrada às Espécies Arbóreas resulta da integração entre a  Carta de Aptidão Edafo-morfológica à Silvicultura e as Cartas de Aptidão Bioclimática a cada uma das Espécies Arbóreas e às Pastagens. Esta integração obtém, para cada uma das Espécies Arbóreas, uma localização mais rigorosa, dependendo do valor ecológico do solo, da morfologia do terreno e do declive.
				&lt;br&gt;&lt;br&gt;
Integrated Suitability for Tree Species&lt;br&gt;
Integrated Suitability for Tree Species results from the integration of the Soil and Morphological Suitability to Silviculture map and the Bioclimatic Suitability to each of Tree Species and Pastures map. This integration obtains, for each tree species, a more accurate location, depending on the ecological value of soil, the land morphology and the slope.</Abstract>
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Integrated Suitability Assessment for the existing Land-use (2007)&lt;br&gt;
Tree species&lt;br&gt;
Evaluation of Integrated Suitability to Tree Species to each per se with respect to existing Land-use (COS 2007) results from the comparison between the two and was limited by the existence of corresponding classes in COS.</Abstract>
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          <Abstract>Com a aplicação das diferentes metodologias de aptidão apresentadas obtêm-se modelos ideais de ocupação do solo. Com a Avaliação pretende-se comparar as diferentes aptidões  com o uso actual do solo. Esta avaliação permite encontrar áreas onde o uso actual do solo é adequado, bem como aquelas áreas onde a alteração de uso do solo deveria ser programada e planeada. As comparações foram efectuadas com recurso à Carta de Ocupação do Solo de 2007 (IGP, 2007).
A Avaliação da Aptidão Edafo-Morfológica à Agricultura de Sequeiro foi obtida pela comparação entre esta carta e a COS2007 (Classe do nível 1 “Áreas Agrícolas e Agro-Florestais”).&lt;br&gt; &lt;br&gt;
Existing Land-use Assessment (2007) regarding the Soil and Morphological Suitability&lt;br&gt;

Rainfed Agriculture&lt;br&gt;

With the application of the different methodologies of suitability presented are obtained ideal models of land use. With the evaluation is intended to compare the different suitabilities with the current land use. This review allows you to find areas where the current land use is appropriate, as well as those areas where land use change should be scheduled and planned. Comparisons were made with Land-use map 2007 (IGP 2007).
Assessment of Soil and Morphological Suitability for Rainfed Agriculture was obtained by comparing its map and COS2007 (level Class 1 "Agricultural Areas and Agro-Forest")
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          <Abstract>Com a aplicação das diferentes metodologias de aptidão apresentadas obtêm-se modelos ideais de ocupação do solo. Com a Avaliação pretende-se comparar as diferentes aptidões  com o uso actual do solo. Esta avaliação permite encontrar áreas onde o uso actual do solo é adequado, bem como aquelas áreas onde a alteração de uso do solo deveria ser programada e planeada. As comparações foram efectuadas com recurso à Carta de Ocupação do Solo de 2007 (IGP, 2007).
A Avaliação da Aptidão Edafo-Morfológica à Agricultura de Sequeiro foi obtida pela comparação entre esta carta e a COS2007 (Classe do nível 1 “Florestas”) (especificar se há alguma exclusão) e também com os sistemas agro-florestais (SAF).&lt;br&gt; &lt;br&gt;

Silviculture&lt;br&gt;

With the application of the different methodologies of suitability presented are obtained ideal models of land use. With the evaluation is intended to compare the different suitabilities with the current land use. This review allows finding areas where the current land use is appropriate, as well as those areas where land use change should be scheduled and planned.
Comparisons were made with Land-use map 2007 (IGP 2007).
Assessment of Soil and Morphological Fitness for Rainfed Agriculture was obtained by comparing its map and COS2007 (Class Level 1 "Forests") (specify if there are any exclusion) and also with agroforestry systems (SAF).</Abstract>
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Integrated Suitability Assessment for the existing Land-use (2007)&lt;br&gt;
Agricultural crops&lt;br&gt;
Evaluation of Integrated Suitability to Agricultural Crops, each per se with respect to existing land-use (COS 2007) results from the comparison between the two and was limited by the existence of corresponding classes in COS. Thus, it was only possible to make this evaluation for the rice and the olive tree, this one conducted in a traditional way. </Abstract>
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          <Abstract>A classificação do território relativamente à aptidão ecológica à edificação (AEE) permite, não só determinar as áreas que apresentam mais ou menos condicionamentos à implementação de edificação, mas também avaliar a qualidade do espaço edificado relativamente a essa classificação, em termos da sua localização.
Com este objectivo, foi efectuada a comparação entre o espaço edificado existente, baseado na Carta de Uso e Ocupação do Solo para 2007 (classes 1.1 e 1.2 do Nível 2) e a carta da Aptidão Edafo-topo-climática à edificação.
&lt;br&gt;&lt;br&gt;Soil and Topo-climatic Suitability to Building Assessment&lt;br&gt;
The classification of the territory in relation to the ecological suitability for building (ESA) allows not only determining the areas that have more or less constraints to the implementation of building, but also evaluate the quality of built space in respect of that ranking in terms of location.
To this purpose, the comparison was made between the existing building space, based on the Land Use Map for 2007 (Class 1.1 and 1.2 of Level 2) and the Soil and Topo-climatic Suitability to Building map.</Abstract>
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Evaluation of Integrated Suitability to Tree Species to each per se with respect to existing Land-use (COS 2007) results from the comparison between the two and was limited by the existence of corresponding classes in COS.</Abstract>
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          <Abstract>A avaliação da Aptidão Integrada às Espécies Arbóreas, cada uma de per se,  relativamente à Ocupação Existente (2007) resulta da comparação entre as duas e foi limitada pela existência de classes correspondentes na COS.&lt;br&gt;&lt;br&gt;
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Tree species&lt;br&gt;
Evaluation of Integrated Suitability to Tree Species to each per se with respect to existing Land-use (COS 2007) results from the comparison between the two and was limited by the existence of corresponding classes in COS.</Abstract>
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          <Title>Comparação da Síntese Integrativa com a COS 2007</Title>
          <Abstract>A Síntese Integrativa prioriza as aptidões edafo-morfológicas à agricultura de sequeiro e à silvicultura, ao integrar as diferentes classes de aptidão edafo-morfológica. Este resultado advém da aplicação de um conceito de intervenção em que as áreas de maior produtividade agrícola devem ter agricultura, enquanto as áreas de relevo mais acidentado e menor qualidade de solo devem apresentar silvicultura de conservação do solo e da água. Nas situações intermédias entre estes dois extremos enquadra a aptidão múltipla. Deste modo, os recursos disponíveis são utilizados não só numa perspectiva de sustentabilidade ecológica, mas também de uma distribuição relativa que permite a produção dos alimentos e materiais necessários.
Esta avaliação foi obtida através da comparação entre a Síntese Integrativa e as classes da COS, “áreas agrícolas e agro-florestais” e “floresta”.&lt;br&gt; &lt;br&gt;

Integrative Synthesis Assessment in Relation to Existing Land-use (2007)&lt;br&gt;

Integrative Synthesis prioritizes soil and morphological suitability to rainfed agriculture and to silviculture, to integrate the different classes of soil and morphological suitability. This result comes from applying a concept of intervention in which the areas of higher agricultural productivity must have agriculture and areas of more rugged relief and lower quality of soil must have soil and water conservation silviculture. In intermediate situations, between these two extremes, fits multiple suitability. Thus, the available resources are used not only in an ecological sustainability perspective, but also considering a relative distribution that allows the production of food and materials.
This review was obtained by comparing the Integrative Synthesis and classes of COS, "agricultural and agro-forests" and "forest".</Abstract>
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Tree species&lt;br&gt;
Evaluation of Integrated Suitability to Tree Species to each per se with respect to existing Land-use (COS 2007) results from the comparison between the two and was limited by the existence of corresponding classes in COS.</Abstract>
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&lt;br&gt;&lt;br&gt;Produção potencial (ton/ha) do feijão (Phaseolus vulgaris L.) em regime de regadio. A produção apresenta-se dividida em quartis, calculados excluindo as produções iguais a zero.O modelo construído simula o crescimento e produção de qualquer cultura anual, bianual ou perene, entrando com as principais variáveis climáticas, textura e espessura do solo e as principais características das plantas. Foram consideradas áreas com aptidão nula os afloramentos rochosos (50 % a 70 %), arribas, areias de praia, dunas, massas de água, zonas húmidas interiores e litorais.
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          <Abstract>Este tipo de aptidão às culturas agrícolas integrou dados de solo, de clima e de relevo e as produtividades apresentadas são as produtividades potenciais limitadas apenas pelos elementos meteorológicos que caracterizam o ambiente físico das plantas, no caso das culturas em regadio, e sujeitas também à disponibilidade hídrica de origem pluvial, modelada pelas características físicas do solo e profundidade alcançada pelas raízes, no caso das culturas de sequeiro.&lt;br&gt;&lt;br&gt;Produção potencial (ton/ha) da beterraba sacarina (Beta vulgaris L..) em regime de regadio. A produção apresenta-se dividida em quartis, calculados excluindo as produções iguais a zero.
O modelo construído simula o crescimento e produção de qualquer cultura anual, bianual ou perene, entrando com as principais variáveis climáticas, textura e espessura do solo e as principais características das plantas. Foram consideradas áreas com aptidão nula os afloramentos rochosos (50 % a 70 %), arribas, areias de praia, dunas, massas de água, zonas húmidas interiores e litorais. &lt;br&gt;&lt;br&gt;Agro-ecological suitability to Agricultural Crops&lt;br&gt;This type of suitability to agricultural crops integrated soil, climate and relief data and presented productivities are the limited potential productivity only by the weather elements that characterize the physical environment of plants, in the case of crops on irrigated land, and also subject to availability water of rain origin, modeled by the physical characteristics of the soil and depth reached by the roots in the case of rainfed crops.
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          <Abstract>Este tipo de aptidão às culturas agrícolas integrou dados de solo, de clima e de relevo e as produtividades apresentadas são as produtividades potenciais limitadas apenas pelos elementos meteorológicos que caracterizam o ambiente físico das plantas, no caso das culturas em regadio, e sujeitas também à disponibilidade hídrica de origem pluvial, modelada pelas características físicas do solo e profundidade alcançada pelas raízes, no caso das culturas de sequeiro.&lt;br&gt;&lt;br&gt;Produção potencial (ton/ha) da couve brócolo (Brassica oleracea L. var. italica Plenck) em regime de regadio. A produção apresenta-se dividida em quartis, calculados excluindo as produções iguais a zero.
O modelo construído simula o crescimento e produção de qualquer cultura anual, bianual ou perene, entrando com as principais variáveis climáticas, textura e espessura do solo e as principais características das plantas. Foram consideradas áreas com aptidão nula os afloramentos rochosos (50 % a 70 %), arribas, areias de praia, dunas, massas de água, zonas húmidas interiores e litorais.
&lt;br&gt;&lt;br&gt;Agro-ecological suitability to Agricultural Crops&lt;br&gt;This type of suitability to agricultural crops integrated soil, climate and relief data and presented productivities are the limited potential productivity only by the weather elements that characterize the physical environment of plants, in the case of crops on irrigated land, and also subject to availability water of rain origin, modeled by the physical characteristics of the soil and depth reached by the roots in the case of rainfed crops.
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          <Abstract>Considerando a preocupação que, desde há muito tempo, se tem verificado com a existência daquilo que se designou por incultos que são considerados como toda e qualquer área que não fosse cultivada, fez-se uma avaliação da ocupação por matos existentes na COS 2007 comparando-a, por um lado, com a Carta de Síntese Integrativa e, por outro, com a Carta de Declives. A classe da COS 2007 utilizada nesta avaliação foi 'Matos' e 'Vegetação esclerófita'.Os resultados obtidos mostram as situações em que os matos (2007) se localizam, consideradas ecologicamente adequadas ou passíveis de  serem substituídos por outros usos mais adequados.&lt;br&gt;&lt;br&gt;
				Bushlands&lt;br&gt;
Considering the concern that, for a long time, there has been the existence of what is termed uncultivated land, considered as any area that is not cultivated, there was an evaluation of the occupation by existing bushlands in COS 2007 and by first, the Map of Integrative Synthesis and secondly, the Map of Slopes. The results show the situations where bushlands (2007) are located, considered environmentally appropriate or expected to be replaced by other more appropriate uses.
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          <Title>Comparação dos declives com os matos (COS2007)</Title>
          <Abstract>Considerando a preocupação que, desde há muito tempo, se tem verificado com a existência daquilo que se designou por incultos que são considerados como toda e qualquer área que não fosse cultivada, fez-se uma avaliação da ocupação por matos existentes na COS 2007 comparando-a, por um lado, com a Carta de Síntese Integrativa e, por outro, com a Carta de Declives. A classe da COS 2007 utilizada nesta avaliação foi 'Matos' e 'Vegetação esclerófita'.Os resultados obtidos mostram as situações em que os matos (2007) se localizam, consideradas ecologicamente adequadas ou passíveis de  serem substituídos por outros usos mais adequados.&lt;br&gt;&lt;br&gt;
				Bushlands&lt;br&gt;
Considering the concern that, for a long time, there has been the existence of what is termed uncultivated land, considered as any area that is not cultivated, there was an evaluation of the occupation by existing bushlands in COS 2007 and by first, the Map of Integrative Synthesis and secondly, the Map of Slopes. The results show the situations where bushlands (2007) are located, considered environmentally appropriate or expected to be replaced by other more appropriate uses.
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          <Abstract>Os declives representam a inclinação da superfície do território. Foram atribuídas sete classes de declives (das áreas planas às áreas muito declivosas): 0-3%, 3-5%, 5-8%, 8-12%, 12-16%, 16-25%, &gt; 25%.
&lt;br&gt;&lt;br&gt;Slopes
&lt;br&gt;
The slopes represent the slope of the surface of the territory. seven slopes classes were assigned (from flat areas to very hilly areas): 0-3%, 3-5%, 5-8%, 8-12%, 12-16%, 16-25%,&gt; 25%.</Abstract>
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          <Abstract>A Estrutura Ecológica é um conceito espacial, entendido como uma estrutura planeada, assente em componentes ecológicas que constituem o suporte físico e biológico necessário à conservação e valorização das funções ecológicas, de modo a favorecer a diversidade biológica e da paisagem, promover o uso sustentável dos recursos naturais e fornecer os bens materiais e imateriais necessários à vida humana.
Este conceito está consagrado na legislação Portuguesa (no Decreto-Lei nº 380/99 de 22 de Setembro, alterado várias vezes e cuja  versão mais recente é dada pelo DL n.º 80/2015, de 14 de Maio) e constitui um instrumento indispensável para um ordenamento do território de base ecológica.
A Estrutura Ecológica Nacional (EEN) reúne todas as áreas necessárias à conservação dos recursos e ciclos naturais, considerados estruturais e indispensáveis ao desenvolvimento sustentável. Deste modo é constituída pelas áreas indispensáveis ao funcionamento dos vários factores ecológicos – solo e sub-solo, relevo, morfologia do terreno, água, ar, vegetação e fauna - e dos principais ecossistemas – litoral, habitats. A protecção destas áreas encontra-se dispersa na legislação (REN, RAN, Domínio Público Hídrico, Rede Fundamental de Conservação da Natureza, protecção ao sobreiro, azinheira e oliveira, etc), o que faz com que a sua gestão dependa de diferentes instituições.
Por outro lado, a sua delimitação nos Planos de Ordenamento do Território, em Portugal,  não existe a nível nacional, encontra-se deficientemente delimitada nos Planos Regionais e, a nível municipal, é delimitada por diferentes equipas, com diferentes competências e utilizando critérios distintos.
A disponibilização de cartografia uniformizada, para todo o País, georreferenciada e em formato digital, contribuirá para uma melhor qualidade dos Planos de Ordenamento do Território e uma melhor fundamentação de estratégias de desenvolvimento.
As políticas europeias, seguem a tendência da criação de uma estrutura Ecológica. Em 2013, a Comissão Europeia adoptou a “Green Infrastructures Strategy” com a intenção de, entre 2014 e 2020, a integrar nas principais políticas dos Estados Membro. Considerando que o conceito de “Green Infrastructure” é equivalente ao da Estrutura Ecológica desenvolvido neste Projecto, esta última poderá contribuir para a componente Portuguesa da grande Infra-estrutura Verde Europeia.
As actividades e ocupações compatíveis com a aptidão de cada componente da EEN são de índole muito diferente, o que conduziu à hierarquização da EEN em dois níveis, de acordo com o valor ou grau de sensibilidade ecológica atribuído a cada componente:&lt;br&gt;1º Nível&lt;br&gt;
As componentes da Estrutura Ecológica Nacional com valor ou grau de sensibilidade ecológica mais elevado foram integradas no 1º Nível e são as seguintes: Linhas de água, Águas marinhas e costeiras, Águas de transição (e embocadura fluvial), Águas interiores, Sistema Húmido, Solos de elevado e muito elevado valor ecológico, Litoral, Áreas declivosas (&gt; 25 %), Vegetação natural e semi-natural com valor de conservação elevado e muito elevado, Áreas de Conservação da Natureza que incluem: a) Rede Natura 2000 b) IBAs c) Sítios Ramsar; d) Rede de Reservas Biogenéticas do Conselho da Europa; e) Reservas da Biosfera da UNESCO; f) Rede Nacional de Áreas Protegidas.
&lt;br&gt;&lt;br&gt;
Ecological Network (1st level) &lt;br&gt;
Ecological Network is a spatial concept, understood as a planned structure, based on ecological components that make up the physical and biological support necessary for the conservation and enhancement of ecological functions, in order to favor the biological and landscape diversity, promoting sustainable use of natural resources and providing the tangible and intangible assets necessary for human life.
This concept is enshrined in the Portuguese legislation (Decree-Law No. 380/99 of 22 September, as amended several times and whose latest version is given by Decree No. 80/2015 of 14 May) and is an indispensable tool for an ecologically based landscape planning.
The National Ecological Network (NEN) brings together all the areas necessary for the conservation of natural resources and cycles, considered structural and indispensable to sustainable development. Thus it consists of the areas essential to the functioning of the various ecological factors - soil and sub-soil, relief, terrain morphology, water, air, vegetation and fauna - and major ecosystems - coastal areas, habitats. The protection of these areas is dispersed in the legislation (REN, RAN, Hydric Public Domain, Fundamental Network for Nature Conservation, the cork oak protection, holm oak and olive protection, etc.), giving its management to different institutions.

On the other hand, its delimitation in the Landscape Plans, in Portugal, does not exist at national level, it is poorly defined at regional level and the municipal level, is bounded by different teams with different skills and using different criteria.

The availability of uniform mapping for the whole country, georeferenced and digital format, will contribute to a better quality of Spatial Planning Plans and a better foundation of development strategies.

European policies, follow the trend of the creation of an ecological structure. In 2013, the European Commission adopted the "Green Infrastructure Strategy" with the intention of, between 2014 and 2020, to integrate the main policies of the Member States. Since the concept of "Green Infrastructure" is equivalent to the ecological structure developed in this project, the latter may contribute to the Portuguese component of the larger European Green infrastructure. Activities and land use compatible with the suitability of NEN’s each component are very different, NEN was hierarchical in two levels according to the amount or degree of ecological sensitivity assigned to each component:
&lt;br&gt;
1st Level&lt;br&gt;
The components of the National Ecological Network with value or higher degree of ecological sensitivity were included in the 1st level and are as follows: water lines, marine and coastal waters, transitional waters (and river mouth), inland waters, Wet System, Soils with very high and high ecological value, Coastline, steep slopes, natural and semi-natural vegetation  with very high and high conservation value, Nature conservation Areas that include: a) Natura 2000 b) IBAs c) Ramsar Sites; d) Biogenetic Reserves Network of the Council of Europe; e) UNESCO Biosphere Reserves; f) National Network of Protected Areas.</Abstract>
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          <Abstract>A Estrutura Ecológica é um conceito espacial, entendido como uma estrutura planeada, assente em componentes ecológicas que constituem o suporte físico e biológico necessário à conservação e valorização das funções ecológicas, de modo a favorecer a diversidade biológica e da paisagem, promover o uso sustentável dos recursos naturais e fornecer os bens materiais e imateriais necessários à vida humana.
Este conceito está consagrado na legislação Portuguesa (no Decreto-Lei nº 380/99 de 22 de Setembro, alterado várias vezes e cuja  versão mais recente é dada pelo DL n.º 80/2015, de 14 de Maio) e constitui um instrumento indispensável para um ordenamento do território de base ecológica.
A Estrutura Ecológica Nacional (EEN) reúne todas as áreas necessárias à conservação dos recursos e ciclos naturais, considerados estruturais e indispensáveis ao desenvolvimento sustentável. Deste modo é constituída pelas áreas indispensáveis ao funcionamento dos vários factores ecológicos – solo e sub-solo, relevo, morfologia do terreno, água, ar, vegetação e fauna - e dos principais ecossistemas – litoral, habitats. A protecção destas áreas encontra-se dispersa na legislação (REN, RAN, Domínio Público Hídrico, Rede Fundamental de Conservação da Natureza, protecção ao sobreiro, azinheira e oliveira, etc), o que faz com que a sua gestão dependa de diferentes instituições.
Por outro lado, a sua delimitação nos Planos de Ordenamento do Território, em Portugal,  não existe a nível nacional, encontra-se deficientemente delimitada nos Planos Regionais e, a nível municipal, é delimitada por diferentes equipas, com diferentes competências e utilizando critérios distintos.
A disponibilização de cartografia uniformizada, para todo o País, georreferenciada e em formato digital, contribuirá para uma melhor qualidade dos Planos de Ordenamento do Território e uma melhor fundamentação de estratégias de desenvolvimento.
As políticas europeias, seguem a tendência da criação de uma estrutura Ecológica. Em 2013, a Comissão Europeia adoptou a “Green Infrastructures Strategy” com a intenção de, entre 2014 e 2020, a integrar nas principais políticas dos Estados Membro. Considerando que o conceito de “Green Infrastructure” é equivalente ao da Estrutura Ecológica desenvolvido neste Projecto, esta última poderá contribuir para a componente Portuguesa da grande Infra-estrutura Verde Europeia.
As actividades e ocupações compatíveis com a aptidão de cada componente da EEN são de índole muito diferente, o que conduziu à hierarquização da EEN em dois níveis, de acordo com o valor ou grau de sensibilidade ecológica atribuído a cada componente:
&lt;br&gt;1º Nível&lt;br&gt;
As componentes da Estrutura Ecológica Nacional com valor ou grau de sensibilidade ecológica mais elevado foram integradas no 1º Nível e são as seguintes: Linhas de água, Águas marinhas e costeiras, Águas de transição (e embocadura fluvial), Águas interiores, Sistema Húmido, Solos de elevado e muito elevado valor ecológico, Litoral, Áreas declivosas (&gt; 25 %), Vegetação natural e semi-natural com valor de conservação elevado e muito elevado, Áreas de Conservação da Natureza que incluem: a) Rede Natura 2000 b) IBAs c) Sítios Ramsar; d) Rede de Reservas Biogenéticas do Conselho da Europa; e) Reservas da Biosfera da UNESCO; f) Rede Nacional de Áreas Protegidas.
&lt;br&gt;2º Nível&lt;br&gt;
As componentes da Estrutura Ecológica Nacional com menor grau de valor ecológico foram integradas no 2º Nível e são as seguintes: Cabeços em sistema húmido antigo, Terras altas, Áreas de máxima infiltração, Vegetação natural e semi-natural com valor de conservação moderado, baixo e muito baixo.
&lt;br&gt;&lt;br&gt;
Ecological Network (2nd level)&lt;br&gt;
Ecological Network is a spatial concept, understood as a planned structure, based on ecological components that make up the physical and biological support necessary for the conservation and enhancement of ecological functions, in order to favor the biological and landscape diversity, promoting sustainable use of natural resources and providing the tangible and intangible assets necessary for human life.
This concept is enshrined in the Portuguese legislation (Decree-Law No. 380/99 of 22 September, as amended several times and whose latest version is given by Decree No. 80/2015 of 14 May) and is an indispensable tool for an ecologically based landscape planning.
The National Ecological Network (NEN) brings together all the areas necessary for the conservation of natural resources and cycles, considered structural and indispensable to sustainable development. Thus it consists of the areas essential to the functioning of the various ecological factors - soil and sub-soil, relief, terrain morphology, water, air, vegetation and fauna - and major ecosystems - coastal areas, habitats. The protection of these areas is dispersed in the legislation (REN, RAN, Hydric Public Domain, Fundamental Network for Nature Conservation, the cork oak protection, holm oak and olive protection, etc.), giving its management to different institutions.
On the other hand, its delimitation in the Landscape Plans, in Portugal, does not exist at national level, it is poorly defined at regional level and the municipal level, is bounded by different teams with different skills and using different criteria.
The availability of uniform mapping for the whole country, georeferenced and digital format, will contribute to a better quality of Spatial Planning Plans and a better foundation of development strategies.
European policies, follow the trend of the creation of an ecological structure. In 2013, the European Commission adopted the "Green Infrastructure Strategy" with the intention of, between 2014 and 2020, to integrate the main policies of the Member States. Since the concept of "Green Infrastructure" is equivalent to the ecological structure developed in this project, the latter may contribute to the Portuguese component of the larger European Green infrastructure. Activities and land use compatible with the suitability of NEN’s each component are very different, NEN was hierarchical in two levels according to the amount or degree of ecological sensitivity assigned to each component:
&lt;br&gt;1st Level&lt;br&gt;
The components of the National Ecological Network with value or higher degree of ecological sensitivity were included in the 1st level and are as follows: water lines, marine and coastal waters, transitional waters (and river mouth), inland waters, Wet System, Soils with very high and high ecological value, Coastline, steep slopes, natural and semi-natural vegetation  with very high and high conservation value, Nature conservation Areas that include: a) Natura 2000 b) IBAs c) Ramsar Sites; d) Biogenetic Reserves Network of the Council of Europe; e) UNESCO Biosphere Reserves; f) National Network of Protected Areas.
&lt;br&gt;2nd Level&lt;br&gt;
The components of the National Ecological Network with lower ecological value have been integrated on the 2nd level and are as follows: Hilltops in old wet system, Highlands, maximum infiltration areas, natural and semi-natural vegetation with moderate low and very low conservation value.</Abstract>
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          <Abstract>As áreas em que os declives são superiores a 25% integram a Estrutura Ecológica e correspondem às zonas com maior susceptibilidade à erosão hídrica do solo, para além de outros condicionamentos ao uso do solo.
&lt;br&gt;&lt;br&gt;Steep Areas&lt;br&gt;
The areas where the slopes are greater than 25% are part of the ecological structure and correspond to areas with increased susceptibility to soil erosion, as well as other constraints to land use.</Abstract>
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          <Abstract>A Estrutura Ecológica é um conceito espacial, entendido como uma estrutura planeada, assente em componentes ecológicas que constituem o suporte físico e biológico necessário à conservação e valorização das funções ecológicas, de modo a favorecer a diversidade biológica e da paisagem, promover o uso sustentável dos recursos naturais e fornecer os bens materiais e imateriais necessários à vida humana.
Este conceito está consagrado na legislação Portuguesa (no Decreto-Lei nº 380/99 de 22 de Setembro, alterado várias vezes e cuja  versão mais recente é dada pelo DL n.º 80/2015, de 14 de Maio) e constitui um instrumento indispensável para um ordenamento do território de base ecológica.
A Estrutura Ecológica Nacional (EEN) reúne todas as áreas necessárias à conservação dos recursos e ciclos naturais, considerados estruturais e indispensáveis ao desenvolvimento sustentável. Deste modo é constituída pelas áreas indispensáveis ao funcionamento dos vários factores ecológicos – solo e sub-solo, relevo, morfologia do terreno, água, ar, vegetação e fauna - e dos principais ecossistemas – litoral, habitats. A protecção destas áreas encontra-se dispersa na legislação (REN, RAN, Domínio Público Hídrico, Rede Fundamental de Conservação da Natureza, protecção ao sobreiro, azinheira e oliveira, etc), o que faz com que a sua gestão dependa de diferentes instituições.
Por outro lado, a sua delimitação nos Planos de Ordenamento do Território, em Portugal,  não existe a nível nacional, encontra-se deficientemente delimitada nos Planos Regionais e, a nível municipal, é delimitada por diferentes equipas, com diferentes competências e utilizando critérios distintos.
A disponibilização de cartografia uniformizada, para todo o País, georreferenciada e em formato digital, contribuirá para uma melhor qualidade dos Planos de Ordenamento do Território e uma melhor fundamentação de estratégias de desenvolvimento.
As políticas europeias, seguem a tendência da criação de uma estrutura Ecológica. Em 2013, a Comissão Europeia adoptou a “Green Infrastructures Strategy” com a intenção de, entre 2014 e 2020, a integrar nas principais políticas dos Estados Membro. Considerando que o conceito de “Green Infrastructure” é equivalente ao da Estrutura Ecológica desenvolvido neste Projecto, esta última poderá contribuir para a componente Portuguesa da grande Infra-estrutura Verde Europeia.
As actividades e ocupações compatíveis com a aptidão de cada componente da EEN são de índole muito diferente, o que conduziu à hierarquização da EEN em dois níveis, de acordo com o valor ou grau de sensibilidade ecológica atribuído a cada componente:
&lt;br&gt;2º Nível&lt;br&gt;
As componentes da Estrutura Ecológica Nacional com menor grau de valor ecológico foram integradas no 2º Nível e são as seguintes: Cabeços em sistema húmido antigo, Terras altas, Áreas de máxima infiltração, Vegetação natural e semi-natural com valor de conservação moderado, baixo e muito baixo.
&lt;br&gt;&lt;br&gt;
Ecological Network (2nd level)&lt;br&gt;
Ecological Network is a spatial concept, understood as a planned structure, based on ecological components that make up the physical and biological support necessary for the conservation and enhancement of ecological functions, in order to favor the biological and landscape diversity, promoting sustainable use of natural resources and providing the tangible and intangible assets necessary for human life.
This concept is enshrined in the Portuguese legislation (Decree-Law No. 380/99 of 22 September, as amended several times and whose latest version is given by Decree No. 80/2015 of 14 May) and is an indispensable tool for an ecologically based landscape planning.
The National Ecological Network (NEN) brings together all the areas necessary for the conservation of natural resources and cycles, considered structural and indispensable to sustainable development. Thus it consists of the areas essential to the functioning of the various ecological factors - soil and sub-soil, relief, terrain morphology, water, air, vegetation and fauna - and major ecosystems - coastal areas, habitats. The protection of these areas is dispersed in the legislation (REN, RAN, Hydric Public Domain, Fundamental Network for Nature Conservation, the cork oak protection, holm oak and olive protection, etc.), giving its management to different institutions.
On the other hand, its delimitation in the Landscape Plans, in Portugal, does not exist at national level, it is poorly defined at regional level and the municipal level, is bounded by different teams with different skills and using different criteria.
The availability of uniform mapping for the whole country, georeferenced and digital format, will contribute to a better quality of Spatial Planning Plans and a better foundation of development strategies.
European policies, follow the trend of the creation of an ecological structure. In 2013, the European Commission adopted the "Green Infrastructure Strategy" with the intention of, between 2014 and 2020, to integrate the main policies of the Member States. Since the concept of "Green Infrastructure" is equivalent to the ecological structure developed in this project, the latter may contribute to the Portuguese component of the larger European Green infrastructure. Activities and land use compatible with the suitability of NEN’s each component are very different, NEN was hierarchical in two levels according to the amount or degree of ecological sensitivity assigned to each component:
&lt;br&gt;2nd Level&lt;br&gt;
The components of the National Ecological Network with lower ecological value have been integrated on the 2nd level and are as follows: Hilltops in old wet system, Highlands, maximum infiltration areas, natural and semi-natural vegetation with moderate low and very low conservation value.</Abstract>
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          <Abstract>A hipsometria representa a elevação do terreno através de classes de altitude. A altitude influencia factores bioclimáticos como a precipitação e a distribuição da vegetação e da fauna, na medida em que provoca variações da pressão atmosférica e da temperatura do ar, condicionando também aspectos como o conforto bioclimático e a distribuição de pontos de vista dominantes na paisagem. Foram atribuídas 17 classes hipsométricas: -11-0m / 0-5m / 5-10m / 10-20m / 20-50m / 50-100m / 100-200m / 200-300m / 300-400m / 400-500m / 500/600m / 600-700m / 700-800m / 800-900m / 900-1000m / 1000-1500m / 1500-1992,71m.
&lt;br&gt;&lt;br&gt;Hypsometry
&lt;br&gt;The hypsometry is the terrain elevation represented by elevation classes. The altitude influences bioclimatic factors such as precipitation and distribution of vegetation and animals, as it causes variations in atmospheric pressure and air temperature also conditioned aspects as bioclimatic comfort and the distribution of dominant points of view in the landscape. 17 hipsometric classes were assigned: -11-0m / 0-5m / 5-10m / 10-20m / 20-50m / 50-100 / 100-200 / 200-300m / 300-400m / 400-500m / 500 / 600m / 600-700m / 700-800m / 800-900m / 900-1000m / 1000-1500m / 1500-1992,71m.
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          <Abstract> Este tipo de aptidão às culturas agrícolas integrou dados de solo, de clima e de relevo e as produtividades apresentadas são as produtividades potenciais limitadas apenas pelos elementos meteorológicos que caracterizam o ambiente físico das plantas, no caso das culturas em regadio, e sujeitas também à disponibilidade hídrica de origem pluvial, modelada pelas características físicas do solo e profundidade alcançada pelas raízes, no caso das culturas de sequeiro.&lt;br&gt;&lt;br&gt;Produção potencial (ton/ha) da cevada (Hordeum vulgare L.) em regime de regadio. A produção apresenta-se dividida em quartis, calculados excluindo as produções iguais a zero.
O modelo construído simula o crescimento e produção de qualquer cultura anual, bianual ou perene, entrando com as principais variáveis climáticas, textura e espessura do solo e as principais características das plantas. Foram consideradas áreas com aptidão nula os afloramentos rochosos (50 % a 70 %), arribas, areias de praia, areias de duna, dunas, massas de água, zonas húmidas interiores e litorais.&lt;br&gt;&lt;br&gt;Agro-ecological suitability to Agricultural Crops
This type of suitability to agricultural crops integrated soil, climate and relief data and presented productivities are the limited potential productivity only by the weather elements that characterize the physical environment of plants, in the case of crops on irrigated land, and also subject to availability water of rain origin, modeled by the physical characteristics of the soil and depth reached by the roots in the case of rainfed crops.
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          <Abstract> Este tipo de aptidão às culturas agrícolas integrou dados de solo, de clima e de relevo e as produtividades apresentadas são as produtividades potenciais limitadas apenas pelos elementos meteorológicos que caracterizam o ambiente físico das plantas, no caso das culturas em regadio, e sujeitas também à disponibilidade hídrica de origem pluvial, modelada pelas características físicas do solo e profundidade alcançada pelas raízes, no caso das culturas de sequeiro.&lt;br&gt;&lt;br&gt;Produção potencial (ton/ha) da cevada (Hordeum vulgare L.) em regime de sequeiro. A produção apresenta-se dividida em quartis, calculados excluindo as produções iguais a zero.
O modelo construído simula o crescimento e produção de qualquer cultura anual, bianual ou perene, entrando com as principais variáveis climáticas, textura e espessura do solo e as principais características das plantas. Foram consideradas áreas com aptidão nula os afloramentos rochosos (50 % a 70 %), arribas, areias de praia, areias de duna, dunas, massas de água, zonas húmidas interiores e litorais.&lt;br&gt;&lt;br&gt;Agro-ecological suitability to Agricultural Crops&lt;br&gt;
This type of suitability to agricultural crops integrated soil, climate and relief data and presented productivities are the limited potential productivity only by the weather elements that characterize the physical environment of plants, in the case of crops on irrigated land, and also subject to availability water of rain origin, modeled by the physical characteristics of the soil and depth reached by the roots in the case of rainfed crops.
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          <Abstract>Este tipo de aptidão às culturas agrícolas integrou dados de solo, de clima e de relevo e as produtividades apresentadas são as produtividades potenciais limitadas apenas pelos elementos meteorológicos que caracterizam o ambiente físico das plantas, no caso das culturas em regadio, e sujeitas também à disponibilidade hídrica de origem pluvial, modelada pelas características físicas do solo e profundidade alcançada pelas raízes, no caso das culturas de sequeiro.&lt;br&gt;&lt;br&gt;Produção potencial (ton/ha) da alface (Lactuca sativa L.) em regime de regadio. A produção apresenta-se dividida em quartis, calculados excluindo as produções iguais a zero.
O modelo construído simula o crescimento e produção de qualquer cultura anual, bianual ou perene, entrando com as principais variáveis climáticas, textura e espessura do solo e as principais características das plantas. Foram consideradas áreas com aptidão nula os afloramentos rochosos (50 % a 70 %), arribas, areias de praia, dunas, massas de água, zonas húmidas interiores e litorais.&lt;br&gt;&lt;br&gt;Agro-ecological suitability to Agricultural Crops&lt;br&gt;
This type of suitability to agricultural crops integrated soil, climate and relief data and presented productivities are the limited potential productivity only by the weather elements that characterize the physical environment of plants, in the case of crops on irrigated land, and also subject to availability water of rain origin, modeled by the physical characteristics of the soil and depth reached by the roots in the case of rainfed crops.
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          <Abstract>Este tipo de aptidão às culturas agrícolas integrou dados de solo, de clima e de relevo e as produtividades apresentadas são as produtividades potenciais limitadas apenas pelos elementos meteorológicos que caracterizam o ambiente físico das plantas, no caso das culturas em regadio, e sujeitas também à disponibilidade hídrica de origem pluvial, modelada pelas características físicas do solo e profundidade alcançada pelas raízes, no caso das culturas de sequeiro.&lt;br&gt;&lt;br&gt;Produção potencial (ton/ha) do melão (Cucumis melo L.) em regime de regadio. A produção apresenta-se dividida em quartis, calculados excluindo as produções iguais a zero.
O modelo construído simula o crescimento e produção de qualquer cultura anual, bianual ou perene, entrando com as principais variáveis climáticas, textura e espessura do solo e as principais características das plantas. Foram consideradas áreas com aptidão nula os afloramentos rochosos (50 % a 70 %), arribas, areias de praia, dunas, massas de água, zonas húmidas interiores e litorais.&lt;br&gt;&lt;br&gt;Agro-ecological suitability to Agricultural Crops&lt;br&gt;
This type of suitability to agricultural crops integrated soil, climate and relief data and presented productivities are the limited potential productivity only by the weather elements that characterize the physical environment of plants, in the case of crops on irrigated land, and also subject to availability water of rain origin, modeled by the physical characteristics of the soil and depth reached by the roots in the case of rainfed crops.
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          <Abstract>A presença de obstáculos físicos no solo é uma característica que impede, dificulta ou onera a livre circulação de máquinas e de gado e limita a dimensão das parcelas cultivadas ou a possibilidade de execução das diversas operações culturais, sobretudo a mobilização do solo (Agroconsultores e Geometral, 1995). As áreas com afloramentos rochosos e os solos que apresentam grande quantidade de elementos grosseiros (diâmetro&gt; 2mm segundo Costa (1995)) apresentam significativas limitações no que se refere à sua utilização agrícola ou florestal. Por outro lado, os patamares, os muros de suporte, ou os socalcos construídos pelo Homem, que alteram muito significativamente a superfície das encostas, aumentam as potencialidades das terras, reduzindo substancialmente o risco de erosão, viabilizando o regadio em condições específicas, bem como o aproveitamento de culturas com enraizamento mais ou menos profundo, como as fruteiras e a vinha. No entanto, estas estruturas limitam a dimensão dos campos de cultura, dificultando a sua acessibilidade e as operações culturais, sobretudo com utilização de máquinas (Agroconsultores e Geometral, 1999)
&lt;br&gt;
&lt;br&gt;
Presence of Physical Barriers&lt;br&gt;
The presence of physical obstacles in the soil is a feature that prevents, hinders or burdens the free movement of machinery and livestock and limits the size of cultivated plots or the possibility of implementing the various cultural operations, particularly tillage (Agroconsultores e Geometral , 1995). The areas with rocky outcrops and soils with lots of coarse elements (diameter&gt; 2 mm according to Costa (1995)) have significant limitations with regard to their agricultural or forestry use. On the other hand, the platforms, the supporting walls or terraces built by man, which very significantly alter the surface of the slopes, increase the potential of the land, substantially reducing the risk of erosion, allowing the irrigation in specific conditions and the use of cultures with more or less deep rooting such as fruit trees and vines. However, these structures limit the size of crop fields, hindering accessibility and cultural operations, particularly with the use of machines (Agroconsultores e Geometral 1999)</Abstract>
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          <Abstract>Este tipo de aptidão às culturas agrícolas integrou dados de solo, de clima e de relevo e as produtividades apresentadas são as produtividades potenciais limitadas apenas pelos elementos meteorológicos que caracterizam o ambiente físico das plantas, no caso das culturas em regadio, e sujeitas também à disponibilidade hídrica de origem pluvial, modelada pelas características físicas do solo e profundidade alcançada pelas raízes, no caso das culturas de sequeiro.&lt;br&gt;&lt;br&gt;Produção potencial (ton/ha) da cebola (Allium cepa L..) em regime de regadio. A produção apresenta-se dividida em quartis, calculados excluindo as produções iguais a zero.
O modelo construído simula o crescimento e produção de qualquer cultura anual, bianual ou perene, entrando com as principais variáveis climáticas, textura e espessura do solo e as principais características das plantas. Foram consideradas áreas com aptidão nula os afloramentos rochosos (50 % a 70 %), arribas, areias de praia, dunas, massas de água, zonas húmidas interiores e litorais.&lt;br&gt;&lt;br&gt;Agro-ecological suitability to Agricultural Crops&lt;br&gt;
This type of suitability to agricultural crops integrated soil, climate and relief data and presented productivities are the limited potential productivity only by the weather elements that characterize the physical environment of plants, in the case of crops on irrigated land, and also subject to availability water of rain origin, modeled by the physical characteristics of the soil and depth reached by the roots in the case of rainfed crops.
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          <Abstract>A orientação das vertentes indica a exposição das superfícies ao movimento aparente do sol que determina a quantidade de radiação solar recebida, influenciando de modo determinante o microclima (sobretudo humidade e temperatura do ar e do solo) e outras variáveis como a taxa de degradação da matéria orgânica e o tipo e quantidade de vegetação. Consideram-se 5 classes: Norte, Sul, Este, Oeste, Plano.
				&lt;br&gt;&lt;br&gt;
Aspect &lt;br&gt;Slope Orientation indicates the exposure of surfaces to the sun's apparent movement that determines the amount of incoming solar radiation, influencing in a decisive way the microclimate (especially humidity and temperature of air and soil) and other variables such as the degradation rate of organic matter and the type and amount of vegetation. Considered to be 5 classes: North, South, East, West, Flat areas.</Abstract>
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          <Abstract>Este tipo de aptidão às culturas agrícolas integrou dados de solo, de clima e de relevo e as produtividades apresentadas são as produtividades potenciais limitadas apenas pelos elementos meteorológicos que caracterizam o ambiente físico das plantas, no caso das culturas em regadio, e sujeitas também à disponibilidade hídrica de origem pluvial, modelada pelas características físicas do solo e profundidade alcançada pelas raízes, no caso das culturas de sequeiro.&lt;br&gt;Produção potencial (ton/ha) da pêra rocha (Pyrus communis L.) em regime de regadio. A produção apresenta-se dividida em quartis, calculados excluindo as produções iguais a zero.
O modelo construído simula o crescimento e produção de qualquer cultura anual, bianual ou perene, entrando com as principais variáveis climáticas, textura e espessura do solo e as principais características das plantas. Foram consideradas áreas com aptidão nula os afloramentos rochosos (50 % a 70 %), arribas, areias de praia, dunas, massas de água, zonas húmidas interiores e litorais.&lt;br&gt;&lt;br&gt;Agro-ecological suitability to Agricultural Crops&lt;br&gt;
This type of suitability to agricultural crops integrated soil, climate and relief data and presented productivities are the limited potential productivity only by the weather elements that characterize the physical environment of plants, in the case of crops on irrigated land, and also subject to availability water of rain origin, modeled by the physical characteristics of the soil and depth reached by the roots in the case of rainfed crops.
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          <Abstract>Avaliação qualitativa da capacidade de infiltração de água no solo, considerando a influência do substrato geológico, dos solos, do declive e do coberto vegetal (uso do solo). Resulta da avaliação da permeabilidade potencial (factores físicos) em conjunto com a aptidão à infiltração dada pelo coberto vegetal. É designada por Permeabilidade Actual, porque considera informação sobre o actual uso do solo (Classe 5 - alta; Classe 4 - moderada a alta; Classe 3 - moderada; Classe 2 - baixa a moderada; Classe 1 - baixa).
&lt;br&gt;&lt;br&gt;
Current permeability &lt;br&gt;
Qualitative assessment of water infiltration capacity of the soil, considering the influence of the geological substrate, soil, slope and vegetation cover. It follows assessing the potential permeability (physical factor) together with the ability to infiltration given by vegetation. It is called Current Permeability, because it considers information on the current land use(Class 5 - high; Class 4 - medium to high; Class 3 - medium; Class 2 - low to medium; Class 1 - low).</Abstract>
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          <Abstract>Avaliação qualitativa da capacidade de infiltração de água no solo, considerando a influência do substrato geológico, dos solos e do declive. Por não se considerar o parâmetro uso do solo, é considerada potencial. A Classificação da permeabilidade potencial considera cinco classes de permeabilidade (Classe 5 - alta; Classe 4 - moderada a alta; Classe 3 - moderada; Classe 2 - baixa a moderada; Classe 1 - baixa).
&lt;br&gt;&lt;br&gt;Soil and sub-soil
Potential permeability &lt;br&gt;
Qualitative assessment of water infiltration capacity of the soil, considering the influence of the geological substrate, soil and slope. As it does not consider the parameter land use is considered potential (Class 5 - high; Class 4 - medium to high; Class 3 - medium; Class 2 - low to medium; Class 1 - low)</Abstract>
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          <Abstract>Este tipo de aptidão às culturas agrícolas integrou dados de solo, de clima e de relevo e as produtividades apresentadas são as produtividades potenciais limitadas apenas pelos elementos meteorológicos que caracterizam o ambiente físico das plantas, no caso das culturas em regadio, e sujeitas também à disponibilidade hídrica de origem pluvial, modelada pelas características físicas do solo e profundidade alcançada pelas raízes, no caso das culturas de sequeiro.&lt;br&gt;&lt;br&gt;Produção potencial (ton/ha) da batata (Solanum tuberosum L..) em regime de regadio. A produção apresenta-se dividida em quartis, calculados excluindo as produções iguais a zero.
O modelo construído simula o crescimento e produção de qualquer cultura anual, bianual ou perene, entrando com as principais variáveis climáticas, textura e espessura do solo e as principais características das plantas. Foram consideradas áreas com aptidão nula os afloramentos rochosos (50 % a 70 %), arribas, areias de praia, dunas, massas de água, zonas húmidas interiores e litorais.&lt;br&gt;&lt;br&gt;Agro-ecological suitability to Agricultural Crops
This type of suitability to agricultural crops integrated soil, climate and relief data and presented productivities are the limited potential productivity only by the weather elements that characterize the physical environment of plants, in the case of crops on irrigated land, and also subject to availability water of rain origin, modeled by the physical characteristics of the soil and depth reached by the roots in the case of rainfed crops.
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          <Abstract>Este tipo de aptidão às culturas agrícolas integrou dados de solo, de clima e de relevo e as produtividades apresentadas são as produtividades potenciais limitadas apenas pelos elementos meteorológicos que caracterizam o ambiente físico das plantas, no caso das culturas em regadio, e sujeitas também à disponibilidade hídrica de origem pluvial, modelada pelas características físicas do solo e profundidade alcançada pelas raízes, no caso das culturas de sequeiro.&lt;br&gt;&lt;br&gt;Produção potencial (ton/ha) do arroz carolino (Oryza sativa L. ssp. japonica) em regime de regadio. A produção apresenta-se dividida em quartis, calculados excluindo as produções iguais a zero.
O modelo construído simula o crescimento e produção de qualquer cultura anual, bianual ou perene, entrando com as principais variáveis climáticas, textura e espessura do solo e as principais características das plantas. A produção apenas foi considerada possível nas áreas correspondentes ao sistema húmido (Cunha et al., 2013 – ISBN 978-972-9669-53-9) e foram consideradas áreas com aptidão nula os afloramentos rochosos (50 % a 70 %), arribas, areias de praia, areias de duna, dunas, massas de água, zonas húmidas interiores e litorais.&lt;br&gt;&lt;br&gt;Agro-ecological suitability to Agricultural Crops&lt;br&gt;
This type of suitability to agricultural crops integrated soil, climate and relief data and presented productivities are the limited potential productivity only by the weather elements that characterize the physical environment of plants, in the case of crops on irrigated land, and also subject to availability water of rain origin, modeled by the physical characteristics of the soil and depth reached by the roots in the case of rainfed crops.
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          <Abstract>O conceito de Síntese Integrativa implica uma opção em que se abandona o conceito de Aptidão Ecológica em termos absolutos e se adopta uma perspectiva relativa da Aptidão. Agora, olha-se para o País como um todo e propõe-se um modo de ocupação que aproveite os recursos disponíveis para as actividades que fornecem os bens necessários para o homem (alimentos e materiais), mantendo o pressuposto da sustentabilidade ecológica.
&lt;br&gt;Classes desta carta:&lt;br&gt;
&lt;br&gt;	Aptidão à Agricultura de Sequeiro – refere-se às melhores condições edafo-morfológicas. No caso do regadio, esta potencialidade é alargada para a representada na carta de Aptidão à Agricultura de Regadio;
&lt;br&gt;	Aptidão Múltipla – corresponde a condições intermédias e, nestas áreas poder-se-à desenvolver agricultura de sequeiro ou silvicultura. É nesta situação que se poderá desenvolver a floresta de produção (pinheiro e eucalipto), com práticas de compartimentação dos povoamentos, de protecção contra incêndios, etc
&lt;br&gt;	Aptidão à Silvicultura de Conservação da Água e do Solo - corresponde às condições mais difíceis de morfologia do terreno e de qualidade do solo. A composição do revestimento, nestas áreas, deverá incluir folhosas e resinosas e, entre as folhosas, o predomínio de espécies autóctones; o pinheiro bravo é adequado, desde que gerido em mata mista, e isto devido às implicações que esta espécie tem na acidez do solo e, por conseguinte, na redução da retenção da matéria orgânica, ou seja na manutenção do seu fundo de fertilidade. O eucalipto deverá ser excluído, nestas áreas, devido às técnicas de exploração, ao fraco revestimento do solo que implica e aos elevados impactos na fertilidade do solo, na conservação da água e na redução da biodiversidade.
&lt;br&gt;&lt;br&gt;
Integrative Synthesis from Soil and Morphological Suitability for the Rainfed Agriculture and Silviculture&lt;br&gt;
The Integrative Synthesis concept implies an option in which the concept of ecological suitability in absolute terms is abandoned and it is adopted a relative perspective of suitability. Now, looking toward the country as a whole proposes land uses that take advantage of the available resources for activities that provide the goods necessary for man (food and materials), maintaining the assumption of ecological sustainability. Classes of this map:
&lt;br&gt; Irrigated Agriculture Suitability - refers to the best soil and morphological conditions. In the case of irrigation, this capability is extended to the represented in the map of Irrigated Agriculture Suitability;
&lt;br&gt; Multiple Suitability - corresponds to intermediate conditions and in these areas it may be developed rainfed agriculture or silviculture. It is this situation where the production forest (pine and eucalyptus) could be developed with compartmentalisation practices of forest stands, fire protection practices, etc.
&lt;br&gt; Water and Soil Conservation Forestry Suitability - corresponds to the most difficult conditions of the terrain morphology and soil quality. The composition of the woods in these areas should include hardwoods and softwoods and among hardwoods the predominance of native species; maritime pine is suitable in mixed forests, and this due to the implications that this species has in the soil acidity and thus the reduction of organic matter retention, ie the maintenance of their fertility background. Eucalyptus should be excluded in these areas due to its exploration techniques, the weak soil covering produced and the high negative impact on soil fertility, water conservation and biodiversity.</Abstract>
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          <Abstract>Este tipo de aptidão às culturas agrícolas integrou dados de solo, de clima e de relevo e as produtividades apresentadas são as produtividades potenciais limitadas apenas pelos elementos meteorológicos que caracterizam o ambiente físico das plantas, no caso das culturas em regadio, e sujeitas também à disponibilidade hídrica de origem pluvial, modelada pelas características físicas do solo e profundidade alcançada pelas raízes, no caso das culturas de sequeiro.&lt;br&gt;&lt;br&gt;Produção potencial (ton/ha) do sorgo (Sorghum bicolor (L.) Moench) em regime de regadio. A produção apresenta-se dividida em quartis, calculados excluindo as produções iguais a zero.
O modelo construído simula o crescimento e produção de qualquer cultura anual, bianual ou perene, entrando com as principais variáveis climáticas, textura e espessura do solo e as principais características das plantas. Foram consideradas áreas com aptidão nula os afloramentos rochosos (50 % a 70 %), arribas, areias de praia, areias de duna, dunas, massas de água, zonas húmidas interiores e litorais.&lt;br&gt;&lt;br&gt;Agro-ecological suitability to Agricultural Crops&lt;br&gt;
This type of suitability to agricultural crops integrated soil, climate and relief data and presented productivities are the limited potential productivity only by the weather elements that characterize the physical environment of plants, in the case of crops on irrigated land, and also subject to availability water of rain origin, modeled by the physical characteristics of the soil and depth reached by the roots in the case of rainfed crops.
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          <Abstract>Este tipo de aptidão às culturas agrícolas integrou dados de solo, de clima e de relevo e as produtividades apresentadas são as produtividades potenciais limitadas apenas pelos elementos meteorológicos que caracterizam o ambiente físico das plantas, no caso das culturas em regadio, e sujeitas também à disponibilidade hídrica de origem pluvial, modelada pelas características físicas do solo e profundidade alcançada pelas raízes, no caso das culturas de sequeiro.&lt;br&gt;&lt;br&gt;Produção potencial (ton/ha) do sorgo (Sorghum bicolor (L.) Moench) em regime de sequeiro. A produção apresenta-se dividida em quartis, calculados excluindo as produções iguais a zero.
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This type of suitability to agricultural crops integrated soil, climate and relief data and presented productivities are the limited potential productivity only by the weather elements that characterize the physical environment of plants, in the case of crops on irrigated land, and also subject to availability water of rain origin, modeled by the physical characteristics of the soil and depth reached by the roots in the case of rainfed crops.
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This type of suitability to agricultural crops integrated soil, climate and relief data and presented productivities are the limited potential productivity only by the weather elements that characterize the physical environment of plants, in the case of crops on irrigated land, and also subject to availability water of rain origin, modeled by the physical characteristics of the soil and depth reached by the roots in the case of rainfed crops.
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This type of suitability to agricultural crops integrated soil, climate and relief data and presented productivities are the limited potential productivity only by the weather elements that characterize the physical environment of plants, in the case of crops on irrigated land, and also subject to availability water of rain origin, modeled by the physical characteristics of the soil and depth reached by the roots in the case of rainfed crops.
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          <Abstract>Este tipo de aptidão às culturas agrícolas integrou dados de solo, de clima e de relevo e as produtividades apresentadas são as produtividades potenciais limitadas apenas pelos elementos meteorológicos que caracterizam o ambiente físico das plantas, no caso das culturas em regadio, e sujeitas também à disponibilidade hídrica de origem pluvial, modelada pelas características físicas do solo e profundidade alcançada pelas raízes, no caso das culturas de sequeiro.&lt;br&gt;&lt;br&gt;Produção potencial (ton/ha) do girassol (Helianthus annuus L.) em regime de sequeiro. A produção apresenta-se dividida em quartis, calculados excluindo as produções iguais a zero.
O modelo construído simula o crescimento e produção de qualquer cultura anual, bianual ou perene, entrando com as principais variáveis climáticas, textura e espessura do solo e as principais características das plantas. Foram consideradas áreas com aptidão nula os afloramentos rochosos (50 % a 70 %), arribas, areias de praia, areias de duna, dunas, massas de água, zonas húmidas interiores e litorais.&lt;br&gt;&lt;br&gt;Agro-ecological suitability to Agricultural Crops&lt;br&gt;
This type of suitability to agricultural crops integrated soil, climate and relief data and presented productivities are the limited potential productivity only by the weather elements that characterize the physical environment of plants, in the case of crops on irrigated land, and also subject to availability water of rain origin, modeled by the physical characteristics of the soil and depth reached by the roots in the case of rainfed crops.
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          <Abstract>Este tipo de aptidão às culturas agrícolas integrou dados de solo, de clima e de relevo e as produtividades apresentadas são as produtividades potenciais limitadas apenas pelos elementos meteorológicos que caracterizam o ambiente físico das plantas, no caso das culturas em regadio, e sujeitas também à disponibilidade hídrica de origem pluvial, modelada pelas características físicas do solo e profundidade alcançada pelas raízes, no caso das culturas de sequeiro.&lt;br&gt;Produção potencial (ton/ha) da batata-doce (Ipomoea batatas (L.) Lam.) em regime de regadio. A produção apresenta-se dividida em quartis, calculados excluindo as produções iguais a zero.
O modelo construído simula o crescimento e produção de qualquer cultura anual, bianual ou perene, entrando com as principais variáveis climáticas, textura e espessura do solo e as principais características das plantas. Foram consideradas áreas com aptidão nula os afloramentos rochosos (50 % a 70 %), arribas, areias de praia, dunas, massas de água, zonas húmidas interiores e litorais.&lt;br&gt;&lt;br&gt;Agro-ecological suitability to Agricultural Crops&lt;br&gt;
This type of suitability to agricultural crops integrated soil, climate and relief data and presented productivities are the limited potential productivity only by the weather elements that characterize the physical environment of plants, in the case of crops on irrigated land, and also subject to availability water of rain origin, modeled by the physical characteristics of the soil and depth reached by the roots in the case of rainfed crops.
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          <Abstract>A determinação da textura do solo foca-se na avaliação das partículas com diâmetro inferior a 2 mm,
designadas por terra fina, responsável por influenciar de forma determinante importantes propriedades
físicas e químicas dos solos, nomeadamente a estrutura, a porosidade, a capacidade de troca catiónica, o
poder tampão etc. (FAO-UNESCO, 1974; Costa, 1995; Varennes, 2003).
Segundo Costa (1995), a textura do solo depende de vários factores, sendo de realçar a importância de: a
rocha-mãe, a topografia e o clima. O autor refere os solos menos evoluídos como os solos cuja textura está mais dependente da natureza da rocha-mãe, particularmente na presença de rocha-mãe do tipo detrítico.
Apresentam-se duas cartas da textura dos solos de Portugal Continental: a primeira refere-se à camada superficial do solo (até 30 cm); a segunda refere-se à textura da camada sub-superficial do solo (a mais de 30 cm).
&lt;br&gt;
&lt;br&gt;Soil texture 30 cm &lt;br&gt;
The determination of soil texture focuses on the evaluation of the particulates with a diameter less than 2 mm, called fine earth, responsible for influencing decisively important physical and chemical properties of soils, including structure, porosity, cation exchange capacity, buffer power etc. (FAO-UNESCO, 1974; Costa, 1995; Varennes, 2003).According to Costa (1995), soil texture depends on several factors, and to highlight the importance of: the parent rock, topography and climate. The author refers to the less evolved soils such as soil whose texture is more dependent on the bedrock nature, particularly in the presence of bedrock of detrital type.They are presented two maps of mainland Portugal soil texture: the first refers to the topsoil (30 cm); the second refers to the texture of the sub-surface soil layer (more than 30cm).</Abstract>
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          <Abstract>Este tipo de aptidão às culturas agrícolas integrou dados de solo, de clima e de relevo e as produtividades apresentadas são as produtividades potenciais limitadas apenas pelos elementos meteorológicos que caracterizam o ambiente físico das plantas, no caso das culturas em regadio, e sujeitas também à disponibilidade hídrica de origem pluvial, modelada pelas características físicas do solo e profundidade alcançada pelas raízes, no caso das culturas de sequeiro.&lt;br&gt;&lt;br&gt;Produção potencial (ton/ha) do tomate (Solanum lycopersicum L.) em regime de regadio. A produção apresenta-se dividida em quartis, calculados excluindo as produções iguais a zero.
O modelo construído simula o crescimento e produção de qualquer cultura anual, bianual ou perene, entrando com as principais variáveis climáticas, textura e espessura do solo e as principais características das plantas. Foram consideradas áreas com aptidão nula os afloramentos rochosos (50 % a 70 %), arribas, areias de praia, dunas, massas de água, zonas húmidas interiores e litorais.&lt;br&gt;&lt;br&gt;Agro-ecological suitability to Agricultural Crops&lt;br&gt;
This type of suitability to agricultural crops integrated soil, climate and relief data and presented productivities are the limited potential productivity only by the weather elements that characterize the physical environment of plants, in the case of crops on irrigated land, and also subject to availability water of rain origin, modeled by the physical characteristics of the soil and depth reached by the roots in the case of rainfed crops.
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Agro-ecological suitability to Agricultural Crops&lt;br&gt;
This type of suitability to agricultural crops integrated soil, climate and relief data and presented productivities are the limited potential productivity only by the weather elements that characterize the physical environment of plants, in the case of crops on irrigated land, and also subject to availability water of rain origin, modeled by the physical characteristics of the soil and depth reached by the roots in the case of rainfed crops.
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This type of suitability to agricultural crops integrated soil, climate and relief data and presented productivities are the limited potential productivity only by the weather elements that characterize the physical environment of plants, in the case of crops on irrigated land, and also subject to availability water of rain origin, modeled by the physical characteristics of the soil and depth reached by the roots in the case of rainfed crops.
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          <Abstract>Este tipo de aptidão às culturas agrícolas integrou dados de solo, de clima e de relevo e as produtividades apresentadas são as produtividades potenciais limitadas apenas pelos elementos meteorológicos que caracterizam o ambiente físico das plantas, no caso das culturas em regadio, e sujeitas também à disponibilidade hídrica de origem pluvial, modelada pelas características físicas do solo e profundidade alcançada pelas raízes, no caso das culturas de sequeiro.&lt;br&gt;&lt;br&gt;Produção potencial (ton/ha) do milho (Zea mays subsp. mayz L.) em regime de sequeiro. A produção apresenta-se dividida em quartis, calculados excluindo as produções iguais a zero.
O modelo construído simula o crescimento e produção de qualquer cultura anual, bianual ou perene, entrando com as principais variáveis climáticas, textura e espessura do solo e as principais características das plantas. Foram consideradas áreas com aptidão nula os afloramentos rochosos (50 % a 70 %), arribas, areias de praia, areias de duna, dunas, massas de água, zonas húmidas interiores e litorais.&lt;br&gt;&lt;br&gt;Agro-ecological suitability to Agricultural Crops&lt;br&gt;
This type of suitability to agricultural crops integrated soil, climate and relief data and presented productivities are the limited potential productivity only by the weather elements that characterize the physical environment of plants, in the case of crops on irrigated land, and also subject to availability water of rain origin, modeled by the physical characteristics of the soil and depth reached by the roots in the case of rainfed crops.
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