Genetic Conservation of Insular Populations of Monterey Pine (Pinus Radiata D. Don)
Issue Title: Agroforestry and biodiversity conservation: Traditional practices, present dynamics, and lessons for the future Monterey pine (Pinus radiata D. Don) has only five extant native populations: three disjunct populations along the coast of California, USA and two on Mexican islands. All pop...
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description | Issue Title: Agroforestry and biodiversity conservation: Traditional practices, present dynamics, and lessons for the future Monterey pine (Pinus radiata D. Don) has only five extant native populations: three disjunct populations along the coast of California, USA and two on Mexican islands. All populations have been influenced by human activity, but the island populations in particular have been affected by introduced biota. On Guadalupe Island, the pine population has suffered drastically from overgrazing by introduced goats. We visited both island populations and described their status, took measurements, and made seed collections. We counted approximately 200 mature pine trees and virtually no seedlings on Guadalupe Island: a reduction of approximately half the population in the last 50 years. The trees are all large (mean diameter of 144 cm) -considerably larger than trees from the other four populations - and arguably near the end of their natural lifespan. The population on Cedros Island is much more robust, with thousands of trees. None sampled were as large as those on Guadalupe Island (mean diameter of 20 cm) and many groves were young and even-aged - presumably the consequence of natural regeneration after a recent fire. Tissue samples from trees on both islands did not show evidence of infection from the pitch canker pathogen, Fusarium circinatum, that has caused significant mortality in the three mainland populations. Caution is recommended in any restoration activity for the Guadalupe Island pines. Inbreeding levels could indicate the need for some planting or seeding intervention but there are also risks associated with this. Natural regeneration - after goat removal - is preferred.[PUBLICATION ABSTRACT] |
doi_str_mv | 10.1007/s10531-004-1066-4 |
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Don)</title><source>SpringerNature Journals</source><creator>Rogers, Deborah L. ; Matheson, A. Colin ; Vargas-Hernández, J. Jesùs ; Guerra-Santos, Jesús J.</creator><creatorcontrib>Rogers, Deborah L. ; Matheson, A. Colin ; Vargas-Hernández, J. Jesùs ; Guerra-Santos, Jesús J.</creatorcontrib><description>Issue Title: Agroforestry and biodiversity conservation: Traditional practices, present dynamics, and lessons for the future Monterey pine (Pinus radiata D. Don) has only five extant native populations: three disjunct populations along the coast of California, USA and two on Mexican islands. All populations have been influenced by human activity, but the island populations in particular have been affected by introduced biota. On Guadalupe Island, the pine population has suffered drastically from overgrazing by introduced goats. We visited both island populations and described their status, took measurements, and made seed collections. We counted approximately 200 mature pine trees and virtually no seedlings on Guadalupe Island: a reduction of approximately half the population in the last 50 years. The trees are all large (mean diameter of 144 cm) -considerably larger than trees from the other four populations - and arguably near the end of their natural lifespan. The population on Cedros Island is much more robust, with thousands of trees. None sampled were as large as those on Guadalupe Island (mean diameter of 20 cm) and many groves were young and even-aged - presumably the consequence of natural regeneration after a recent fire. Tissue samples from trees on both islands did not show evidence of infection from the pitch canker pathogen, Fusarium circinatum, that has caused significant mortality in the three mainland populations. Caution is recommended in any restoration activity for the Guadalupe Island pines. Inbreeding levels could indicate the need for some planting or seeding intervention but there are also risks associated with this. Natural regeneration - after goat removal - is preferred.[PUBLICATION ABSTRACT]</description><identifier>ISSN: 0960-3115</identifier><identifier>EISSN: 1572-9710</identifier><identifier>DOI: 10.1007/s10531-004-1066-4</identifier><language>eng</language><publisher>Dordrecht: Springer Nature B.V</publisher><subject>Agroforestry ; Animal populations ; Biota ; Evergreen trees ; Fusarium circinatum ; Inbreeding ; Islands ; Pine trees ; Pinus radiata ; Seedlings</subject><ispartof>Biodiversity and conservation, 2006-02, Vol.15 (2), p.779-798</ispartof><rights>Springer 2006</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c303t-71d050c012ddace27eab7d60f848d80bba55dc8670abc3a8c94eaf9ff8420f613</citedby><cites>FETCH-LOGICAL-c303t-71d050c012ddace27eab7d60f848d80bba55dc8670abc3a8c94eaf9ff8420f613</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><link.rule.ids>315,781,785,27926,27927</link.rule.ids></links><search><creatorcontrib>Rogers, Deborah L.</creatorcontrib><creatorcontrib>Matheson, A. Colin</creatorcontrib><creatorcontrib>Vargas-Hernández, J. Jesùs</creatorcontrib><creatorcontrib>Guerra-Santos, Jesús J.</creatorcontrib><title>Genetic Conservation of Insular Populations of Monterey Pine (Pinus Radiata D. Don)</title><title>Biodiversity and conservation</title><description>Issue Title: Agroforestry and biodiversity conservation: Traditional practices, present dynamics, and lessons for the future Monterey pine (Pinus radiata D. Don) has only five extant native populations: three disjunct populations along the coast of California, USA and two on Mexican islands. All populations have been influenced by human activity, but the island populations in particular have been affected by introduced biota. On Guadalupe Island, the pine population has suffered drastically from overgrazing by introduced goats. We visited both island populations and described their status, took measurements, and made seed collections. We counted approximately 200 mature pine trees and virtually no seedlings on Guadalupe Island: a reduction of approximately half the population in the last 50 years. The trees are all large (mean diameter of 144 cm) -considerably larger than trees from the other four populations - and arguably near the end of their natural lifespan. The population on Cedros Island is much more robust, with thousands of trees. None sampled were as large as those on Guadalupe Island (mean diameter of 20 cm) and many groves were young and even-aged - presumably the consequence of natural regeneration after a recent fire. Tissue samples from trees on both islands did not show evidence of infection from the pitch canker pathogen, Fusarium circinatum, that has caused significant mortality in the three mainland populations. Caution is recommended in any restoration activity for the Guadalupe Island pines. Inbreeding levels could indicate the need for some planting or seeding intervention but there are also risks associated with this. Natural regeneration - after goat removal - is preferred.[PUBLICATION ABSTRACT]</description><subject>Agroforestry</subject><subject>Animal populations</subject><subject>Biota</subject><subject>Evergreen trees</subject><subject>Fusarium circinatum</subject><subject>Inbreeding</subject><subject>Islands</subject><subject>Pine trees</subject><subject>Pinus radiata</subject><subject>Seedlings</subject><issn>0960-3115</issn><issn>1572-9710</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2006</creationdate><recordtype>article</recordtype><sourceid>ABUWG</sourceid><sourceid>AFKRA</sourceid><sourceid>AZQEC</sourceid><sourceid>BENPR</sourceid><sourceid>CCPQU</sourceid><sourceid>DWQXO</sourceid><sourceid>GNUQQ</sourceid><recordid>eNpdkN9LwzAQx4MoOKd_gG_BB9GHzrumTZpH2XQOJg5_PIc0TaGjS2bSCvvvbZlPvtwX7j53HB9CrhFmCCAeIkLOMAHIEgTOk-yETDAXaSIFwimZgOSQMMT8nFzEuIVhJ-c4IR9L62zXGDr3Ltrwo7vGO-prunKxb3WgG78fcuzGsf3qXWeDPdBN4yy9G2of6buuGt1pupjRhXf3l-Ss1m20V385JV_PT5_zl2T9tlzNH9eJYcC6RGAFORjAtKq0samwuhQVh7rIiqqAstR5XpmCC9ClYbowMrO6lvUwT6HmyKbk9nh3H_x3b2Ondk00tm21s76PCmUq0wLlAN78A7e-D274TYkcOUoENkB4hEzwMQZbq31odjocFIIaHaujYzU4VqNjlbFfa6JuUA</recordid><startdate>20060201</startdate><enddate>20060201</enddate><creator>Rogers, Deborah L.</creator><creator>Matheson, A. 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Don)</title><author>Rogers, Deborah L. ; Matheson, A. Colin ; Vargas-Hernández, J. Jesùs ; Guerra-Santos, Jesús J.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c303t-71d050c012ddace27eab7d60f848d80bba55dc8670abc3a8c94eaf9ff8420f613</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2006</creationdate><topic>Agroforestry</topic><topic>Animal populations</topic><topic>Biota</topic><topic>Evergreen trees</topic><topic>Fusarium circinatum</topic><topic>Inbreeding</topic><topic>Islands</topic><topic>Pine trees</topic><topic>Pinus radiata</topic><topic>Seedlings</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Rogers, Deborah L.</creatorcontrib><creatorcontrib>Matheson, A. Colin</creatorcontrib><creatorcontrib>Vargas-Hernández, J. 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Colin</au><au>Vargas-Hernández, J. Jesùs</au><au>Guerra-Santos, Jesús J.</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Genetic Conservation of Insular Populations of Monterey Pine (Pinus Radiata D. Don)</atitle><jtitle>Biodiversity and conservation</jtitle><date>2006-02-01</date><risdate>2006</risdate><volume>15</volume><issue>2</issue><spage>779</spage><epage>798</epage><pages>779-798</pages><issn>0960-3115</issn><eissn>1572-9710</eissn><abstract>Issue Title: Agroforestry and biodiversity conservation: Traditional practices, present dynamics, and lessons for the future Monterey pine (Pinus radiata D. Don) has only five extant native populations: three disjunct populations along the coast of California, USA and two on Mexican islands. All populations have been influenced by human activity, but the island populations in particular have been affected by introduced biota. On Guadalupe Island, the pine population has suffered drastically from overgrazing by introduced goats. We visited both island populations and described their status, took measurements, and made seed collections. We counted approximately 200 mature pine trees and virtually no seedlings on Guadalupe Island: a reduction of approximately half the population in the last 50 years. The trees are all large (mean diameter of 144 cm) -considerably larger than trees from the other four populations - and arguably near the end of their natural lifespan. The population on Cedros Island is much more robust, with thousands of trees. None sampled were as large as those on Guadalupe Island (mean diameter of 20 cm) and many groves were young and even-aged - presumably the consequence of natural regeneration after a recent fire. Tissue samples from trees on both islands did not show evidence of infection from the pitch canker pathogen, Fusarium circinatum, that has caused significant mortality in the three mainland populations. Caution is recommended in any restoration activity for the Guadalupe Island pines. Inbreeding levels could indicate the need for some planting or seeding intervention but there are also risks associated with this. Natural regeneration - after goat removal - is preferred.[PUBLICATION ABSTRACT]</abstract><cop>Dordrecht</cop><pub>Springer Nature B.V</pub><doi>10.1007/s10531-004-1066-4</doi><tpages>20</tpages></addata></record> |
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subjects | Agroforestry Animal populations Biota Evergreen trees Fusarium circinatum Inbreeding Islands Pine trees Pinus radiata Seedlings |
title | Genetic Conservation of Insular Populations of Monterey Pine (Pinus Radiata D. Don) |
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