{"id":1012197,"date":"2026-03-04T10:53:59","date_gmt":"2026-03-04T09:53:59","guid":{"rendered":"https:\/\/new.obsnev.es\/?post_type=protocolos&#038;p=1012197"},"modified":"2026-03-04T12:21:35","modified_gmt":"2026-03-04T11:21:35","slug":"bosques-autoctonos-y-matorrales-de-media-y-alta-montana","status":"publish","type":"protocolos","link":"https:\/\/obsnev.es\/en\/protocolos\/bosques-autoctonos-y-matorrales-de-media-y-alta-montana\/","title":{"rendered":"Native forests and shrublands of middle and high elevations"},"content":{"rendered":"<div data-elementor-type=\"wp-post\" data-elementor-id=\"1012197\" class=\"elementor elementor-1012197\" data-elementor-post-type=\"protocolos\">\n\t\t\t\t<div class=\"elementor-element elementor-element-63787e3 e-flex e-con-boxed e-con e-parent\" data-id=\"63787e3\" data-element_type=\"container\" data-e-type=\"container\">\n\t\t\t\t\t<div class=\"e-con-inner\">\n\t\t\t\t<div class=\"elementor-element elementor-element-4db42ea elementor-widget elementor-widget-text-editor\" data-id=\"4db42ea\" data-element_type=\"widget\" data-e-type=\"widget\" data-widget_type=\"text-editor.default\">\n\t\t\t\t<div class=\"elementor-widget-container\">\n\t\t\t\t\t\t\t\t\t<div id=\"panel-gb4326-69a033732152e-0-0-0\" class=\"so-panel widget widget_sow-editor panel-first-child\" data-index=\"0\"><div class=\"fila_ficha panel-widget-style panel-widget-style-for-gb4326-69a033732152e-0-0-0\"><div class=\"so-widget-sow-editor so-widget-sow-editor-base\"><h3 class=\"widget-title\">Aims<\/h3><div class=\"siteorigin-widget-tinymce textwidget\"><p>The basic aim of this protocol is to detect changes in species richness in terms of cover and frequency. The study focuses on native forests (mainly Holm oak woodlands and pyrenean oak forests) and shrublands of the medium and high-mountain of Sierra Nevada massif.<\/p><\/div><\/div><\/div><\/div>\t\t\t\t\t\t\t\t<\/div>\n\t\t\t\t<\/div>\n\t\t\t\t<div class=\"elementor-element elementor-element-e2fa565 elementor-widget elementor-widget-image\" data-id=\"e2fa565\" data-element_type=\"widget\" data-e-type=\"widget\" data-widget_type=\"image.default\">\n\t\t\t\t<div class=\"elementor-widget-container\">\n\t\t\t\t\t\t\t\t\t\t\t\t\t\t\t<img fetchpriority=\"high\" decoding=\"async\" width=\"992\" height=\"565\" src=\"https:\/\/obsnev.es\/wp-content\/uploads\/2019\/10\/Figura_8_5-1_EN.png\" class=\"attachment-2048x2048 size-2048x2048 wp-image-4754\" alt=\"\" srcset=\"https:\/\/obsnev.es\/wp-content\/uploads\/2019\/10\/Figura_8_5-1_EN.png 992w, https:\/\/obsnev.es\/wp-content\/uploads\/2019\/10\/Figura_8_5-1_EN-300x171.png 300w, https:\/\/obsnev.es\/wp-content\/uploads\/2019\/10\/Figura_8_5-1_EN-768x437.png 768w, https:\/\/obsnev.es\/wp-content\/uploads\/2019\/10\/Figura_8_5-1_EN-18x10.png 18w\" sizes=\"(max-width: 992px) 100vw, 992px\" \/>\t\t\t\t\t\t\t\t\t\t\t\t\t\t\t<\/div>\n\t\t\t\t<\/div>\n\t\t\t\t<div class=\"elementor-element elementor-element-95f591f elementor-widget elementor-widget-text-editor\" data-id=\"95f591f\" data-element_type=\"widget\" data-e-type=\"widget\" data-widget_type=\"text-editor.default\">\n\t\t\t\t<div class=\"elementor-widget-container\">\n\t\t\t\t\t\t\t\t\t<div id=\"panel-gb4326-69a033732152e-0-0-0\" class=\"so-panel widget widget_sow-editor panel-first-child\" data-index=\"0\"><div class=\"fila_ficha panel-widget-style panel-widget-style-for-gb4326-69a033732152e-0-0-0\"><div class=\"so-widget-sow-editor so-widget-sow-editor-base\"><div id=\"panel-gb4326-69a033732152e-0-0-2\" class=\"so-panel widget widget_sow-editor\" data-index=\"2\"><div class=\"fila_ficha panel-widget-style panel-widget-style-for-gb4326-69a033732152e-0-0-2\"><div class=\"so-widget-sow-editor so-widget-sow-editor-base\"><h3 class=\"widget-title\">Method and effort<\/h3><div class=\"siteorigin-widget-tinymce textwidget\"><p>Sampling points were chosen in the different ecosystems studied using the available mapping of the vegetation. The monitoring effort for each community selected is directly proportional to its presence in the natural space and to its singularity. In this way, the selection made of a number of localities was intended to be sufficient to encompass the maximum diversity that Sierra Nevada offers, seeking to maintain a balanced geographical distribution. At each location, 3 replicates were established in an effort to maintain, as far as possible, the same conditions of orientation, elevation, and slope. Each of the replicates consists of a plot 20 m x 20 m which is subdivided into 16 quadrats of 5 m x 5 m each. In each quadrat, a complete inventory of taxa present is prepared and the relative coverage of each taxon is determined in the plot. The ecosystem studied are: acidophilous holm oak woodland, pyrenean oak forest, native pine forest, juniper thicket, spanish juniper stands, dolomitic thyme thickets and semiarid shrublands.<\/p><\/div><\/div><\/div><\/div><\/div><\/div><\/div>\t\t\t\t\t\t\t\t<\/div>\n\t\t\t\t<\/div>\n\t\t\t\t<div class=\"elementor-element elementor-element-07a90e4 elementor-widget elementor-widget-image\" data-id=\"07a90e4\" data-element_type=\"widget\" data-e-type=\"widget\" data-widget_type=\"image.default\">\n\t\t\t\t<div class=\"elementor-widget-container\">\n\t\t\t\t\t\t\t\t\t\t\t\t\t\t\t<img decoding=\"async\" width=\"992\" height=\"528\" src=\"https:\/\/obsnev.es\/wp-content\/uploads\/2019\/10\/Figura_8_5-2_ES.png\" class=\"attachment-2048x2048 size-2048x2048 wp-image-4756\" alt=\"\" srcset=\"https:\/\/obsnev.es\/wp-content\/uploads\/2019\/10\/Figura_8_5-2_ES.png 992w, https:\/\/obsnev.es\/wp-content\/uploads\/2019\/10\/Figura_8_5-2_ES-300x160.png 300w, https:\/\/obsnev.es\/wp-content\/uploads\/2019\/10\/Figura_8_5-2_ES-768x409.png 768w, https:\/\/obsnev.es\/wp-content\/uploads\/2019\/10\/Figura_8_5-2_ES-18x10.png 18w\" sizes=\"(max-width: 992px) 100vw, 992px\" \/>\t\t\t\t\t\t\t\t\t\t\t\t\t\t\t<\/div>\n\t\t\t\t<\/div>\n\t\t\t\t<div class=\"elementor-element elementor-element-0f416af elementor-widget elementor-widget-text-editor\" data-id=\"0f416af\" data-element_type=\"widget\" data-e-type=\"widget\" data-widget_type=\"text-editor.default\">\n\t\t\t\t<div class=\"elementor-widget-container\">\n\t\t\t\t\t\t\t\t\t<div id=\"panel-gb4326-69a033732152e-0-0-0\" class=\"so-panel widget widget_sow-editor panel-first-child\" data-index=\"0\"><div class=\"fila_ficha panel-widget-style panel-widget-style-for-gb4326-69a033732152e-0-0-0\"><div class=\"so-widget-sow-editor so-widget-sow-editor-base\"><div id=\"panel-gb4326-69a033732152e-0-0-2\" class=\"so-panel widget widget_sow-editor\" data-index=\"2\"><div class=\"fila_ficha panel-widget-style panel-widget-style-for-gb4326-69a033732152e-0-0-2\"><div class=\"so-widget-sow-editor so-widget-sow-editor-base\"><div id=\"panel-gb4581-69a0338952d0b-0-0-2\" class=\"so-panel widget widget_sow-editor\" data-index=\"2\"><div class=\"so-widget-sow-editor so-widget-sow-editor-base\"><div id=\"panel-gb4753-69a7ff2eb3e56-0-0-2\" class=\"so-panel widget widget_sow-editor\" data-index=\"2\"><div class=\"so-widget-sow-editor so-widget-sow-editor-base\"><h3 class=\"widget-title\">Periodicity<\/h3><div class=\"siteorigin-widget-tinymce textwidget\"><p>Monitoring is undertaken every three years.<\/p><\/div><\/div><\/div><div id=\"panel-gb4753-69a7ff2eb3e56-0-0-3\" class=\"so-panel widget widget_sow-editor panel-last-child\" data-index=\"3\"><div class=\"so-widget-sow-editor so-widget-sow-editor-base\"><h3 class=\"widget-title\">References<\/h3><div class=\"siteorigin-widget-tinymce textwidget\"><p>Felic\u00edsimo, \u00c1.M. (coord.) 2011. Impactos, vulnerabilidad y adaptaci\u00f3n al cambio clim\u00e1tico de la biodiversidad espa\u00f1ola. Oficina espa\u00f1ola de Cambio Clim\u00e1tico. Ministerio de Medio Ambiente y Medio Rural y Marino. Madrid, 552 pp.<br \/>Benito de Pando, B. 2008. El Calentamiento Global en Sierra Nevada. Modelos de distribuci\u00f3n potencial de formaciones vegetales sobre distintos escenarios de Cambio Global. Proyecto DEA. Departamento de Bot\u00e1nica. Universidad de Granada. Granada.<br \/>Mart\u00ednez Parras, J.M. y Molero Mesa, J.1982. Ecolog\u00eda y fitosociolog\u00eda de Quercus pyrenaica Willd. en la provincia b\u00e9tica. Los melojares b\u00e9ticos y sus etapas de sustituci\u00f3n. Lazaroa, 4: 91-104.<\/p><\/div><\/div><\/div><\/div><\/div><\/div><\/div><\/div><\/div><\/div><\/div>\t\t\t\t\t\t\t\t<\/div>\n\t\t\t\t<\/div>\n\t\t\t\t\t<\/div>\n\t\t\t\t<\/div>\n\t\t\t\t<\/div>","protected":false},"featured_media":4754,"template":"","meta":{"_acf_changed":false},"ambito-tematico":[352],"class_list":["post-1012197","protocolos","type-protocolos","status-publish","has-post-thumbnail","hentry","ambito-tematico-repercusiones-sobre-la-biodiversidad-modelos-de-distribucion-potencial"],"acf":[],"aioseo_notices":[],"_links":{"self":[{"href":"https:\/\/obsnev.es\/en\/wp-json\/wp\/v2\/protocolos\/1012197","targetHints":{"allow":["GET"]}}],"collection":[{"href":"https:\/\/obsnev.es\/en\/wp-json\/wp\/v2\/protocolos"}],"about":[{"href":"https:\/\/obsnev.es\/en\/wp-json\/wp\/v2\/types\/protocolos"}],"version-history":[{"count":8,"href":"https:\/\/obsnev.es\/en\/wp-json\/wp\/v2\/protocolos\/1012197\/revisions"}],"predecessor-version":[{"id":1012236,"href":"https:\/\/obsnev.es\/en\/wp-json\/wp\/v2\/protocolos\/1012197\/revisions\/1012236"}],"wp:featuredmedia":[{"embeddable":true,"href":"https:\/\/obsnev.es\/en\/wp-json\/wp\/v2\/media\/4754"}],"wp:attachment":[{"href":"https:\/\/obsnev.es\/en\/wp-json\/wp\/v2\/media?parent=1012197"}],"wp:term":[{"taxonomy":"ambito-tematico","embeddable":true,"href":"https:\/\/obsnev.es\/en\/wp-json\/wp\/v2\/ambito-tematico?post=1012197"}],"curies":[{"name":"wp","href":"https:\/\/api.w.org\/{rel}","templated":true}]}}