Long-term population changes in the Giant Quiver Tree, Aloe pillansii in the Richtersveld, South Africa
With probably fewer than 3000 individuals alive in the biodiversity hotspot of the Succulent Karoo in southern Africa, populations of the endemic, Giant Quiver Tree, Aloe pillansii, are thought to be declining and thus threatened with extinction. Using repeat photography and field data we investigat...
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description | With probably fewer than 3000 individuals alive in the biodiversity hotspot of the Succulent Karoo in southern Africa, populations of the endemic, Giant Quiver Tree, Aloe pillansii, are thought to be declining and thus threatened with extinction. Using repeat photography and field data we investigated the long-term changes in one population of A. pillansii at its type locality, the roughly 100 ha Cornell's Kop in the Richtersveld, South Africa. There are currently 75 individuals alive at this site. Of these, 44% are 3 m (adults). An analysis of 14 repeat photographs shows that since 1937 an average of 1.4% of the plants >3 m in height has died annually. At this rate all the remaining 39 plants on Cornell's Kop in this size class will be dead in 71 years. The relative paucity of plants in the 1-3 m size classes could be explained by several factors including plant theft, animal damage and unfavourable recruitment conditions during the first 80 years of the 20th century. Annual growth rates decrease as plants age. Individuals 3 m grow at 31.0 and 16.4 mm yr-1 respectively. At 8 m, the tallest plant on Cornell's Kop could be as old as 382 years and thus to maintain itself at this site, A. pillansii would only need to recruit relatively infrequently. The relatively high proportion of seedlings suggests that conditions have recently been favourable for recruitment at this site. Seedling ages, estimated from their heights, indicate that over 50% of the plants |
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Using repeat photography and field data we investigated the long-term changes in one population of A. pillansii at its type locality, the roughly 100 ha Cornell's Kop in the Richtersveld, South Africa. There are currently 75 individuals alive at this site. Of these, 44% are <1 m in height (seedlings), 4% are 1-3 m (juveniles) and 52% are >3 m (adults). An analysis of 14 repeat photographs shows that since 1937 an average of 1.4% of the plants >3 m in height has died annually. At this rate all the remaining 39 plants on Cornell's Kop in this size class will be dead in 71 years. The relative paucity of plants in the 1-3 m size classes could be explained by several factors including plant theft, animal damage and unfavourable recruitment conditions during the first 80 years of the 20th century. Annual growth rates decrease as plants age. Individuals <1 m in height grow at 42.5 mm yr-1 while plants 1-3 m and those >3 m grow at 31.0 and 16.4 mm yr-1 respectively. At 8 m, the tallest plant on Cornell's Kop could be as old as 382 years and thus to maintain itself at this site, A. pillansii would only need to recruit relatively infrequently. The relatively high proportion of seedlings suggests that conditions have recently been favourable for recruitment at this site. Seedling ages, estimated from their heights, indicate that over 50% of the plants <1 m in height germinated 5-10 years ago. This is consistent with local rainfall records which show that rainfall was consistently above the long-term annual average of 75 mm during this period. However, the loss of six seedlings from the population in the last 5 years, probably due to grazing or theft, suggests that without intervention this species will not survive on Cornell's Kop.</description><identifier>ISSN: 1385-0237</identifier><identifier>EISSN: 1573-5052</identifier><identifier>DOI: 10.1007/s11258-005-9085-0</identifier><language>eng</language><publisher>Dordrecht: Springer</publisher><subject>Adults ; Aloe ; Aloe pillansii ; Biodiversity ; Biodiversity hot spots ; Climate change ; Endangered & extinct species ; endangered species ; forest decline ; forest trees ; grazing ; height ; longevity ; Mortality ; Plant ecology ; Plant growth ; Plant populations ; plant theft ; Plants ; Population dynamics ; Rain ; seedling recruitment ; Seedlings ; Species extinction ; Succulent plants ; Terrestrial ecosystems ; tree age ; tree growth ; Trees</subject><ispartof>Plant ecology, 2006-07, Vol.185 (1), p.73-84</ispartof><rights>Copyright 2005 Springer</rights><rights>Springer Science+Business Media, Inc. 2006</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c349t-3c07ec6b1931aa92dde2feffe526726e82fbf72a5fa4f2d484dfb3d1fa1634d53</citedby><cites>FETCH-LOGICAL-c349t-3c07ec6b1931aa92dde2feffe526726e82fbf72a5fa4f2d484dfb3d1fa1634d53</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://www.jstor.org/stable/pdf/20146942$$EPDF$$P50$$Gjstor$$H</linktopdf><linktohtml>$$Uhttps://www.jstor.org/stable/20146942$$EHTML$$P50$$Gjstor$$H</linktohtml><link.rule.ids>314,776,780,799,27903,27904,57996,58229</link.rule.ids></links><search><creatorcontrib>Duncan, J</creatorcontrib><creatorcontrib>Hoffman, T</creatorcontrib><creatorcontrib>Rohde, R</creatorcontrib><creatorcontrib>Powell, E</creatorcontrib><creatorcontrib>Hendricks, H</creatorcontrib><title>Long-term population changes in the Giant Quiver Tree, Aloe pillansii in the Richtersveld, South Africa</title><title>Plant ecology</title><description>With probably fewer than 3000 individuals alive in the biodiversity hotspot of the Succulent Karoo in southern Africa, populations of the endemic, Giant Quiver Tree, Aloe pillansii, are thought to be declining and thus threatened with extinction. Using repeat photography and field data we investigated the long-term changes in one population of A. pillansii at its type locality, the roughly 100 ha Cornell's Kop in the Richtersveld, South Africa. There are currently 75 individuals alive at this site. Of these, 44% are <1 m in height (seedlings), 4% are 1-3 m (juveniles) and 52% are >3 m (adults). An analysis of 14 repeat photographs shows that since 1937 an average of 1.4% of the plants >3 m in height has died annually. At this rate all the remaining 39 plants on Cornell's Kop in this size class will be dead in 71 years. The relative paucity of plants in the 1-3 m size classes could be explained by several factors including plant theft, animal damage and unfavourable recruitment conditions during the first 80 years of the 20th century. Annual growth rates decrease as plants age. Individuals <1 m in height grow at 42.5 mm yr-1 while plants 1-3 m and those >3 m grow at 31.0 and 16.4 mm yr-1 respectively. At 8 m, the tallest plant on Cornell's Kop could be as old as 382 years and thus to maintain itself at this site, A. pillansii would only need to recruit relatively infrequently. The relatively high proportion of seedlings suggests that conditions have recently been favourable for recruitment at this site. Seedling ages, estimated from their heights, indicate that over 50% of the plants <1 m in height germinated 5-10 years ago. This is consistent with local rainfall records which show that rainfall was consistently above the long-term annual average of 75 mm during this period. However, the loss of six seedlings from the population in the last 5 years, probably due to grazing or theft, suggests that without intervention this species will not survive on Cornell's Kop.</description><subject>Adults</subject><subject>Aloe</subject><subject>Aloe pillansii</subject><subject>Biodiversity</subject><subject>Biodiversity hot spots</subject><subject>Climate change</subject><subject>Endangered & extinct species</subject><subject>endangered species</subject><subject>forest decline</subject><subject>forest trees</subject><subject>grazing</subject><subject>height</subject><subject>longevity</subject><subject>Mortality</subject><subject>Plant ecology</subject><subject>Plant growth</subject><subject>Plant populations</subject><subject>plant theft</subject><subject>Plants</subject><subject>Population dynamics</subject><subject>Rain</subject><subject>seedling recruitment</subject><subject>Seedlings</subject><subject>Species extinction</subject><subject>Succulent plants</subject><subject>Terrestrial ecosystems</subject><subject>tree age</subject><subject>tree growth</subject><subject>Trees</subject><issn>1385-0237</issn><issn>1573-5052</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>eNpdkU1LxDAQhoso-PkDPIjBg6et5rNpj8uiq7AgunoO2Xaym6Xb1KQV_PemVj14mmHmeV-Gd5LknOAbgrG8DYRQkacYi7TAuUjxXnJEhGSpwILux54NQ8rkYXIcwhbjqGLiKFkvXLNOO_A71Lq2r3VnXYPKjW7WEJBtULcBNLe66dBzbz_Ao1cPMEHT2gFqbV3rJlj7C77YchO9wgfU1QQtXd9t0NR4W-rT5MDoOsDZTz1J3u7vXmcP6eJp_jibLtKS8aJLWYkllNmKFIxoXdCqAmrAGBA0kzSDnJqVkVQLo7mhFc95ZVasIkaTjPFKsJPkevRtvXvvIXRqZ0MJw53g-qBIwQsquIzg1T9w63rfxNuUzJgklHMaITJCpXcheDCq9Xan_aciWA25qzF3FXNXQ-4KR83FqNmGzvk_AcWEZ8W35-W4N9opvfY2qLdl3LL4kjzDImdfR8aI7A</recordid><startdate>20060701</startdate><enddate>20060701</enddate><creator>Duncan, J</creator><creator>Hoffman, T</creator><creator>Rohde, R</creator><creator>Powell, E</creator><creator>Hendricks, H</creator><general>Springer</general><general>Springer Nature B.V</general><scope>FBQ</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>3V.</scope><scope>7QL</scope><scope>7SN</scope><scope>7ST</scope><scope>7T7</scope><scope>7U9</scope><scope>7X2</scope><scope>88A</scope><scope>8FD</scope><scope>8FE</scope><scope>8FH</scope><scope>8FK</scope><scope>ABUWG</scope><scope>AEUYN</scope><scope>AFKRA</scope><scope>ATCPS</scope><scope>AZQEC</scope><scope>BBNVY</scope><scope>BENPR</scope><scope>BHPHI</scope><scope>C1K</scope><scope>CCPQU</scope><scope>DWQXO</scope><scope>FR3</scope><scope>GNUQQ</scope><scope>H94</scope><scope>HCIFZ</scope><scope>LK8</scope><scope>M0K</scope><scope>M7N</scope><scope>M7P</scope><scope>P64</scope><scope>PQEST</scope><scope>PQQKQ</scope><scope>PQUKI</scope><scope>RC3</scope><scope>SOI</scope></search><sort><creationdate>20060701</creationdate><title>Long-term population changes in the Giant Quiver Tree, Aloe pillansii in the Richtersveld, South Africa</title><author>Duncan, J ; Hoffman, T ; Rohde, R ; Powell, E ; Hendricks, H</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c349t-3c07ec6b1931aa92dde2feffe526726e82fbf72a5fa4f2d484dfb3d1fa1634d53</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2006</creationdate><topic>Adults</topic><topic>Aloe</topic><topic>Aloe pillansii</topic><topic>Biodiversity</topic><topic>Biodiversity hot spots</topic><topic>Climate change</topic><topic>Endangered & extinct species</topic><topic>endangered species</topic><topic>forest decline</topic><topic>forest trees</topic><topic>grazing</topic><topic>height</topic><topic>longevity</topic><topic>Mortality</topic><topic>Plant ecology</topic><topic>Plant growth</topic><topic>Plant populations</topic><topic>plant theft</topic><topic>Plants</topic><topic>Population dynamics</topic><topic>Rain</topic><topic>seedling recruitment</topic><topic>Seedlings</topic><topic>Species extinction</topic><topic>Succulent plants</topic><topic>Terrestrial ecosystems</topic><topic>tree age</topic><topic>tree growth</topic><topic>Trees</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Duncan, J</creatorcontrib><creatorcontrib>Hoffman, T</creatorcontrib><creatorcontrib>Rohde, R</creatorcontrib><creatorcontrib>Powell, E</creatorcontrib><creatorcontrib>Hendricks, H</creatorcontrib><collection>AGRIS</collection><collection>CrossRef</collection><collection>ProQuest Central (Corporate)</collection><collection>Bacteriology Abstracts (Microbiology B)</collection><collection>Ecology Abstracts</collection><collection>Environment Abstracts</collection><collection>Industrial and Applied Microbiology Abstracts (Microbiology A)</collection><collection>Virology and AIDS Abstracts</collection><collection>Agricultural Science Collection</collection><collection>Biology Database (Alumni Edition)</collection><collection>Technology Research Database</collection><collection>ProQuest SciTech Collection</collection><collection>ProQuest Natural Science Collection</collection><collection>ProQuest Central (Alumni) (purchase pre-March 2016)</collection><collection>ProQuest Central (Alumni Edition)</collection><collection>ProQuest One Sustainability</collection><collection>ProQuest Central UK/Ireland</collection><collection>Agricultural & Environmental Science Collection</collection><collection>ProQuest Central Essentials</collection><collection>Biological Science Collection</collection><collection>ProQuest Central</collection><collection>Natural Science Collection</collection><collection>Environmental Sciences and Pollution Management</collection><collection>ProQuest One Community College</collection><collection>ProQuest Central Korea</collection><collection>Engineering Research Database</collection><collection>ProQuest Central Student</collection><collection>AIDS and Cancer Research Abstracts</collection><collection>SciTech Premium Collection</collection><collection>ProQuest Biological Science Collection</collection><collection>Agricultural Science Database</collection><collection>Algology Mycology and Protozoology Abstracts (Microbiology C)</collection><collection>Biological Science Database</collection><collection>Biotechnology and BioEngineering Abstracts</collection><collection>ProQuest One Academic Eastern Edition (DO NOT USE)</collection><collection>ProQuest One Academic</collection><collection>ProQuest One Academic UKI Edition</collection><collection>Genetics Abstracts</collection><collection>Environment Abstracts</collection><jtitle>Plant ecology</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Duncan, J</au><au>Hoffman, T</au><au>Rohde, R</au><au>Powell, E</au><au>Hendricks, H</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Long-term population changes in the Giant Quiver Tree, Aloe pillansii in the Richtersveld, South Africa</atitle><jtitle>Plant ecology</jtitle><date>2006-07-01</date><risdate>2006</risdate><volume>185</volume><issue>1</issue><spage>73</spage><epage>84</epage><pages>73-84</pages><issn>1385-0237</issn><eissn>1573-5052</eissn><abstract>With probably fewer than 3000 individuals alive in the biodiversity hotspot of the Succulent Karoo in southern Africa, populations of the endemic, Giant Quiver Tree, Aloe pillansii, are thought to be declining and thus threatened with extinction. Using repeat photography and field data we investigated the long-term changes in one population of A. pillansii at its type locality, the roughly 100 ha Cornell's Kop in the Richtersveld, South Africa. There are currently 75 individuals alive at this site. Of these, 44% are <1 m in height (seedlings), 4% are 1-3 m (juveniles) and 52% are >3 m (adults). An analysis of 14 repeat photographs shows that since 1937 an average of 1.4% of the plants >3 m in height has died annually. At this rate all the remaining 39 plants on Cornell's Kop in this size class will be dead in 71 years. The relative paucity of plants in the 1-3 m size classes could be explained by several factors including plant theft, animal damage and unfavourable recruitment conditions during the first 80 years of the 20th century. Annual growth rates decrease as plants age. Individuals <1 m in height grow at 42.5 mm yr-1 while plants 1-3 m and those >3 m grow at 31.0 and 16.4 mm yr-1 respectively. At 8 m, the tallest plant on Cornell's Kop could be as old as 382 years and thus to maintain itself at this site, A. pillansii would only need to recruit relatively infrequently. The relatively high proportion of seedlings suggests that conditions have recently been favourable for recruitment at this site. Seedling ages, estimated from their heights, indicate that over 50% of the plants <1 m in height germinated 5-10 years ago. This is consistent with local rainfall records which show that rainfall was consistently above the long-term annual average of 75 mm during this period. However, the loss of six seedlings from the population in the last 5 years, probably due to grazing or theft, suggests that without intervention this species will not survive on Cornell's Kop.</abstract><cop>Dordrecht</cop><pub>Springer</pub><doi>10.1007/s11258-005-9085-0</doi><tpages>12</tpages></addata></record> |
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subjects | Adults Aloe Aloe pillansii Biodiversity Biodiversity hot spots Climate change Endangered & extinct species endangered species forest decline forest trees grazing height longevity Mortality Plant ecology Plant growth Plant populations plant theft Plants Population dynamics Rain seedling recruitment Seedlings Species extinction Succulent plants Terrestrial ecosystems tree age tree growth Trees |
title | Long-term population changes in the Giant Quiver Tree, Aloe pillansii in the Richtersveld, South Africa |
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