{"id":6775,"date":"2026-01-23T16:56:29","date_gmt":"2026-01-23T15:56:29","guid":{"rendered":"https:\/\/ist.blogs.inrae.fr\/afs\/?p=6775"},"modified":"2026-01-23T16:57:08","modified_gmt":"2026-01-23T15:57:08","slug":"tracking-a-decade-of-change-insights-from-long-term-monitoring-of-an-old-growth-temperate-rainforest-on-chiloe-island-chile","status":"publish","type":"post","link":"https:\/\/ist.blogs.inrae.fr\/afs\/2026\/01\/23\/tracking-a-decade-of-change-insights-from-long-term-monitoring-of-an-old-growth-temperate-rainforest-on-chiloe-island-chile\/","title":{"rendered":"Tracking a decade of change: insights from long-term monitoring of an old-growth temperate rainforest on Chilo\u00e9 Island, Chile"},"content":{"rendered":"<script type='text\/javascript' src='https:\/\/d1bxh8uas1mnw7.cloudfront.net\/assets\/embed.js'><\/script><p><strong><a href=\"https:\/\/ist.blogs.inrae.fr\/afs\/wp-content\/uploads\/sites\/5\/2026\/01\/26-01-23_Gutierrez-A.G.png\"><img loading=\"lazy\" decoding=\"async\" class=\"size-medium wp-image-6784 alignright\" src=\"https:\/\/ist.blogs.inrae.fr\/afs\/wp-content\/uploads\/sites\/5\/2026\/01\/26-01-23_Gutierrez-A.G-167x300.png\" alt=\"\" width=\"167\" height=\"300\" srcset=\"https:\/\/ist.blogs.inrae.fr\/afs\/wp-content\/uploads\/sites\/5\/2026\/01\/26-01-23_Gutierrez-A.G-167x300.png 167w, https:\/\/ist.blogs.inrae.fr\/afs\/wp-content\/uploads\/sites\/5\/2026\/01\/26-01-23_Gutierrez-A.G-569x1024.png 569w, https:\/\/ist.blogs.inrae.fr\/afs\/wp-content\/uploads\/sites\/5\/2026\/01\/26-01-23_Gutierrez-A.G-640x1151.png 640w, https:\/\/ist.blogs.inrae.fr\/afs\/wp-content\/uploads\/sites\/5\/2026\/01\/26-01-23_Gutierrez-A.G.png 685w\" sizes=\"auto, (max-width: 167px) 100vw, 167px\" \/><\/a>Key message\u00a0<\/strong><\/p>\n<p>Southern temperate rainforests harbor exceptional endemic biodiversity and large carbon stocks but remain underrepresented in global monitoring networks. Here, we present a dataset and standardized census protocol from a 1-ha permanent plot in an old-growth temperate rainforest in Chilo\u00e9, Chile. The data obtained in two censuses (2014, 2024) reveal that the forest has abundant regeneration but offsets high mortality and biomass accumulation in large trees. This dataset establishes the first long-term demographic baseline for these forests, enabling future censuses to assess how warming and drying trends may alter tree recruitment, growth, and mortality dynamics.<\/p>\n<p><strong>Keywords\u00a0<\/strong><br \/>\nTree demography; Forest dynamics; Forest succession; Demographic rates<\/p>\n<div class='altmetric-embed' data-badge-type='donut' data-doi='10.1186\/s13595-025-01323-5'  style='float: right; ' ><\/div>\n<p><strong>Publication\u00a0<\/strong><br \/>\nGuti\u00e9rrez, \u00c1.G., Montero-Silva, F., Gaxiola, A.\u00a0<i>et al.<\/i>\u00a0Tracking a decade of change: insights from long-term monitoring of an old-growth temperate rainforest on Chilo\u00e9 Island, Chile.\u00a0<i>Annals of Forest Science<\/i>\u00a0(2026). <a href=\"https:\/\/doi.org\/10.1186\/s13595-025-01323-5\">https:\/\/doi.org\/10.1186\/s13595-025-01323-5<\/a><\/p>\n<p><strong>Data availability\u00a0<\/strong><br \/>\nThe datasets generated during the present study have been published in the data-repository\u00a0Zenodo (<a href=\"https:\/\/doi.org\/10.5281\/zenodo.17398246\">https:\/\/doi.org\/10.5281\/zenodo.17398246<\/a>), Guti\u00e9rrez and Montero-Silva\u00a0<a id=\"ref-link-section-d125264584e582\" title=\"Guti\u00e9rrez AG, Montero-Silva F (2025) EBSD Tepual database (v1.0.3). Zenodo. https:\/\/doi.org\/10.5281\/zenodo.17398246\" href=\"https:\/\/link-springer-com.inrae.idm.oclc.org\/article\/10.1186\/s13595-025-01323-5#ref-CR25\" data-track=\"click\" data-track-action=\"reference anchor\" data-track-label=\"link\" data-test=\"citation-ref\" aria-label=\"Reference 2025\">2025<\/a>). The available datasets correspond to the following files: permanent_data.csv, census_database2014.csv, census_database2024.csv, quadrant_team2014.csv, quadrant_team2024.csv and spp_names.csv. The variable descriptions are in the variables_names.csv file. Associated metadata is available at:\u00a0<a href=\"https:\/\/metadata-afs.nancy.inra.fr\/geonetwork\/srv\/fre\/catalog.search#\/metadata\/7a3e9aca-9125-4ab3-a072-10b034eb122b\">https:\/\/metadata-afs.nancy.inra.fr\/geonetwork\/srv\/fre\/catalog.search#\/metadata\/7a3e9aca-9125-4ab3-a072-10b034eb122b<\/a>,\u00a0<a href=\"https:\/\/zenodo.org\/records\/17398246\">https:\/\/zenodo.org\/records\/17398246<\/a>.<\/p>\n<p><strong>Handling editor<\/strong><br \/>\nIr\u00e8ne Gabriel<\/p>\n","protected":false},"excerpt":{"rendered":"<p>Key message\u00a0 Southern temperate rainforests harbor exceptional endemic biodiversity and large carbon stocks but remain underrepresented in global monitoring networks. Here, we present a dataset and standardized census protocol from a 1-ha permanent plot in an old-growth temperate rainforest in Chilo\u00e9, Chile. The data obtained in two censuses (2014, 2024) reveal that the forest has [&hellip;]<\/p>\n","protected":false},"author":240,"featured_media":0,"comment_status":"open","ping_status":"open","sticky":false,"template":"","format":"standard","meta":{"footnotes":""},"categories":[14,100,1,109],"tags":[],"class_list":["post-6775","post","type-post","status-publish","format-standard","hentry","category-article-type","category-data-paper","category-non-classe","category-open-access","cat-14-id","cat-100-id","cat-1-id","cat-109-id"],"_links":{"self":[{"href":"https:\/\/ist.blogs.inrae.fr\/afs\/wp-json\/wp\/v2\/posts\/6775","targetHints":{"allow":["GET"]}}],"collection":[{"href":"https:\/\/ist.blogs.inrae.fr\/afs\/wp-json\/wp\/v2\/posts"}],"about":[{"href":"https:\/\/ist.blogs.inrae.fr\/afs\/wp-json\/wp\/v2\/types\/post"}],"author":[{"embeddable":true,"href":"https:\/\/ist.blogs.inrae.fr\/afs\/wp-json\/wp\/v2\/users\/240"}],"replies":[{"embeddable":true,"href":"https:\/\/ist.blogs.inrae.fr\/afs\/wp-json\/wp\/v2\/comments?post=6775"}],"version-history":[{"count":4,"href":"https:\/\/ist.blogs.inrae.fr\/afs\/wp-json\/wp\/v2\/posts\/6775\/revisions"}],"predecessor-version":[{"id":6787,"href":"https:\/\/ist.blogs.inrae.fr\/afs\/wp-json\/wp\/v2\/posts\/6775\/revisions\/6787"}],"wp:attachment":[{"href":"https:\/\/ist.blogs.inrae.fr\/afs\/wp-json\/wp\/v2\/media?parent=6775"}],"wp:term":[{"taxonomy":"category","embeddable":true,"href":"https:\/\/ist.blogs.inrae.fr\/afs\/wp-json\/wp\/v2\/categories?post=6775"},{"taxonomy":"post_tag","embeddable":true,"href":"https:\/\/ist.blogs.inrae.fr\/afs\/wp-json\/wp\/v2\/tags?post=6775"}],"curies":[{"name":"wp","href":"https:\/\/api.w.org\/{rel}","templated":true}]}}