Drivers of plant invasion vary globally: evidence from pine invasions within six ecoregions

AIM: To determine biotic and abiotic controls on pine invasion globally within six ecoregions that include both introduced and native ranges. LOCATIONS: Río Negro province, Argentina; Aysén and Araucanía regions, Chile; South Island (two ecoregions), New Zealand; Greater Yellowstone ecosystem, USA....

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Veröffentlicht in:Global ecology and biogeography 2016, Vol.25 (1), p.96-106
Hauptverfasser: Taylor, Kimberley T, Maxwell, Bruce D, Pauchard, Aníbal, Nuñez, Martin A, Peltzer, Duane A, Terwei, André, Rew, Lisa J
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container_issue 1
container_start_page 96
container_title Global ecology and biogeography
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creator Taylor, Kimberley T
Maxwell, Bruce D
Pauchard, Aníbal
Nuñez, Martin A
Peltzer, Duane A
Terwei, André
Rew, Lisa J
description AIM: To determine biotic and abiotic controls on pine invasion globally within six ecoregions that include both introduced and native ranges. LOCATIONS: Río Negro province, Argentina; Aysén and Araucanía regions, Chile; South Island (two ecoregions), New Zealand; Greater Yellowstone ecosystem, USA. METHODS: We quantified tree abundance and size across invasion fronts of the widespread invasive tree species Pinus contorta at each of the nine sites, encompassing both the native and introduced range. We also determined the relative importance of propagule pressure, abiotic characteristics and biotic factors for invasion success. Finally, key plant population metrics such as individual tree growth rates and reproductive effort were compared between native and introduced ranges. RESULTS: Pinus contorta density decreased with increasing distance from source population in all cases, but the importance and shape of this relationship differed among sites due, primarily to biotic factors. For example, areas dominated by native southern beech forest (Fuscospora cliffortioides or Nothofagus spp.) were not invaded, and this biotic resistance was not overcome by high propagule pressure. In contrast, shrublands were more highly invaded than grasslands, contradicting previous generalizations about pine invasions. Pinus contorta growth was faster, age to maturity was earlier and reproductive effort was higher in the introduced ranges compared with the native range, suggesting a demographic shift towards more rapid population growth in introduced regions. Climatic differences between the ranges may explain, at least in part, the observed pattern. MAIN CONCLUSIONS: We demonstrate that although biological invasions are driven by propagule pressure across different ecoregions, these processes interact strongly with biotic factors. Intriguingly, our results suggest that propagule pressure may become less important than biotic interactions as invasions proceed. Multi‐region studies including both the native and introduced ranges provide unparalleled opportunities for understanding how these interactions change among regions as invasions proceed.
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LOCATIONS: Río Negro province, Argentina; Aysén and Araucanía regions, Chile; South Island (two ecoregions), New Zealand; Greater Yellowstone ecosystem, USA. METHODS: We quantified tree abundance and size across invasion fronts of the widespread invasive tree species Pinus contorta at each of the nine sites, encompassing both the native and introduced range. We also determined the relative importance of propagule pressure, abiotic characteristics and biotic factors for invasion success. Finally, key plant population metrics such as individual tree growth rates and reproductive effort were compared between native and introduced ranges. RESULTS: Pinus contorta density decreased with increasing distance from source population in all cases, but the importance and shape of this relationship differed among sites due, primarily to biotic factors. For example, areas dominated by native southern beech forest (Fuscospora cliffortioides or Nothofagus spp.) were not invaded, and this biotic resistance was not overcome by high propagule pressure. In contrast, shrublands were more highly invaded than grasslands, contradicting previous generalizations about pine invasions. Pinus contorta growth was faster, age to maturity was earlier and reproductive effort was higher in the introduced ranges compared with the native range, suggesting a demographic shift towards more rapid population growth in introduced regions. Climatic differences between the ranges may explain, at least in part, the observed pattern. MAIN CONCLUSIONS: We demonstrate that although biological invasions are driven by propagule pressure across different ecoregions, these processes interact strongly with biotic factors. Intriguingly, our results suggest that propagule pressure may become less important than biotic interactions as invasions proceed. Multi‐region studies including both the native and introduced ranges provide unparalleled opportunities for understanding how these interactions change among regions as invasions proceed.</description><identifier>ISSN: 1466-822X</identifier><identifier>EISSN: 1466-8238</identifier><identifier>DOI: 10.1111/geb.12391</identifier><identifier>CODEN: GEBIFS</identifier><language>eng</language><publisher>Oxford: Blackwell Science</publisher><subject>Biogeography ; biological invasions ; biotic resistance ; colonizing ability ; ecological invasion ; ecoregions ; ecosystems ; forests ; grasslands ; indigenous species ; introduced species ; invasive species ; New Zealand ; non-native tree invasion ; Nothofagus ; Patagonia ; Pinus contorta ; population growth ; propagule pressure ; shrublands ; tree growth ; tree population dynamics ; trees</subject><ispartof>Global ecology and biogeography, 2016, Vol.25 (1), p.96-106</ispartof><rights>Copyright © 2016 John Wiley &amp; Sons Ltd.</rights><rights>2015 John Wiley &amp; Sons Ltd</rights><rights>Copyright © 2016 John Wiley &amp; Sons Ltd</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c4141-c52521a1d319b11524e88fe88efecbf4552470a66fc97cb0e8b82075f835c1b73</citedby><cites>FETCH-LOGICAL-c4141-c52521a1d319b11524e88fe88efecbf4552470a66fc97cb0e8b82075f835c1b73</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://www.jstor.org/stable/pdf/43871603$$EPDF$$P50$$Gjstor$$H</linktopdf><linktohtml>$$Uhttps://www.jstor.org/stable/43871603$$EHTML$$P50$$Gjstor$$H</linktohtml><link.rule.ids>314,776,780,799,1411,4010,27900,27901,27902,45550,45551,57992,58225</link.rule.ids></links><search><creatorcontrib>Taylor, Kimberley T</creatorcontrib><creatorcontrib>Maxwell, Bruce D</creatorcontrib><creatorcontrib>Pauchard, Aníbal</creatorcontrib><creatorcontrib>Nuñez, Martin A</creatorcontrib><creatorcontrib>Peltzer, Duane A</creatorcontrib><creatorcontrib>Terwei, André</creatorcontrib><creatorcontrib>Rew, Lisa J</creatorcontrib><title>Drivers of plant invasion vary globally: evidence from pine invasions within six ecoregions</title><title>Global ecology and biogeography</title><addtitle>Global Ecology and Biogeography</addtitle><description>AIM: To determine biotic and abiotic controls on pine invasion globally within six ecoregions that include both introduced and native ranges. LOCATIONS: Río Negro province, Argentina; Aysén and Araucanía regions, Chile; South Island (two ecoregions), New Zealand; Greater Yellowstone ecosystem, USA. METHODS: We quantified tree abundance and size across invasion fronts of the widespread invasive tree species Pinus contorta at each of the nine sites, encompassing both the native and introduced range. We also determined the relative importance of propagule pressure, abiotic characteristics and biotic factors for invasion success. Finally, key plant population metrics such as individual tree growth rates and reproductive effort were compared between native and introduced ranges. RESULTS: Pinus contorta density decreased with increasing distance from source population in all cases, but the importance and shape of this relationship differed among sites due, primarily to biotic factors. For example, areas dominated by native southern beech forest (Fuscospora cliffortioides or Nothofagus spp.) were not invaded, and this biotic resistance was not overcome by high propagule pressure. In contrast, shrublands were more highly invaded than grasslands, contradicting previous generalizations about pine invasions. Pinus contorta growth was faster, age to maturity was earlier and reproductive effort was higher in the introduced ranges compared with the native range, suggesting a demographic shift towards more rapid population growth in introduced regions. Climatic differences between the ranges may explain, at least in part, the observed pattern. MAIN CONCLUSIONS: We demonstrate that although biological invasions are driven by propagule pressure across different ecoregions, these processes interact strongly with biotic factors. Intriguingly, our results suggest that propagule pressure may become less important than biotic interactions as invasions proceed. Multi‐region studies including both the native and introduced ranges provide unparalleled opportunities for understanding how these interactions change among regions as invasions proceed.</description><subject>Biogeography</subject><subject>biological invasions</subject><subject>biotic resistance</subject><subject>colonizing ability</subject><subject>ecological invasion</subject><subject>ecoregions</subject><subject>ecosystems</subject><subject>forests</subject><subject>grasslands</subject><subject>indigenous species</subject><subject>introduced species</subject><subject>invasive species</subject><subject>New Zealand</subject><subject>non-native tree invasion</subject><subject>Nothofagus</subject><subject>Patagonia</subject><subject>Pinus contorta</subject><subject>population growth</subject><subject>propagule pressure</subject><subject>shrublands</subject><subject>tree growth</subject><subject>tree population dynamics</subject><subject>trees</subject><issn>1466-822X</issn><issn>1466-8238</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2016</creationdate><recordtype>article</recordtype><recordid>eNp1kE9v1DAQxSMEEqVw4AMgLHGhh7QeO_6z3KAtKVIBIahA5WA57njxNhsvdnbb_fa4BPaAhCXLo3m_Nxq_qnoK9BDKOZpjdwiMz-BetQeNlLVmXN_f1ezbw-pRzgtKqWiE3Ku-n6SwwZRJ9GTV22EkYdjYHOJANjZtybyPne377SuCm3CFg0PiU1ySVRhwh2ZyE8YfYSA53BJ0MeH8rvu4euBtn_HJn3e_unh7-uX4rD7_2L47fn1euwYaqJ1ggoGFKw6zDkCwBrX25aJH1_lGlI6iVkrvZsp1FHWnGVXCay4cdIrvVy-nuasUf64xj2YZssO-fAfjOhtQSkopiqmgL_5BF3GdhrJdoYRiUvGZLtTBRLkUc07ozSqFZYnDADV3MZsSs_kdc2GPJvYm9Lj9P2ja0zd_Hc8mxyKPMe0cDdcKJOVFryc95BFvd7pN16asp4T5-qE1LT-7bN_DpflU-OcT7200dp5CNhefGS2zKNUSNPBfEwOgNw</recordid><startdate>2016</startdate><enddate>2016</enddate><creator>Taylor, Kimberley T</creator><creator>Maxwell, Bruce D</creator><creator>Pauchard, Aníbal</creator><creator>Nuñez, Martin A</creator><creator>Peltzer, Duane A</creator><creator>Terwei, André</creator><creator>Rew, Lisa J</creator><general>Blackwell Science</general><general>Blackwell Publishing Ltd</general><general>John Wiley &amp; 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LOCATIONS: Río Negro province, Argentina; Aysén and Araucanía regions, Chile; South Island (two ecoregions), New Zealand; Greater Yellowstone ecosystem, USA. METHODS: We quantified tree abundance and size across invasion fronts of the widespread invasive tree species Pinus contorta at each of the nine sites, encompassing both the native and introduced range. We also determined the relative importance of propagule pressure, abiotic characteristics and biotic factors for invasion success. Finally, key plant population metrics such as individual tree growth rates and reproductive effort were compared between native and introduced ranges. RESULTS: Pinus contorta density decreased with increasing distance from source population in all cases, but the importance and shape of this relationship differed among sites due, primarily to biotic factors. For example, areas dominated by native southern beech forest (Fuscospora cliffortioides or Nothofagus spp.) were not invaded, and this biotic resistance was not overcome by high propagule pressure. In contrast, shrublands were more highly invaded than grasslands, contradicting previous generalizations about pine invasions. Pinus contorta growth was faster, age to maturity was earlier and reproductive effort was higher in the introduced ranges compared with the native range, suggesting a demographic shift towards more rapid population growth in introduced regions. Climatic differences between the ranges may explain, at least in part, the observed pattern. MAIN CONCLUSIONS: We demonstrate that although biological invasions are driven by propagule pressure across different ecoregions, these processes interact strongly with biotic factors. Intriguingly, our results suggest that propagule pressure may become less important than biotic interactions as invasions proceed. Multi‐region studies including both the native and introduced ranges provide unparalleled opportunities for understanding how these interactions change among regions as invasions proceed.</abstract><cop>Oxford</cop><pub>Blackwell Science</pub><doi>10.1111/geb.12391</doi><tpages>11</tpages></addata></record>
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source Jstor Complete Legacy; Wiley Online Library Journals Frontfile Complete
subjects Biogeography
biological invasions
biotic resistance
colonizing ability
ecological invasion
ecoregions
ecosystems
forests
grasslands
indigenous species
introduced species
invasive species
New Zealand
non-native tree invasion
Nothofagus
Patagonia
Pinus contorta
population growth
propagule pressure
shrublands
tree growth
tree population dynamics
trees
title Drivers of plant invasion vary globally: evidence from pine invasions within six ecoregions
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