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<eml:eml packageId="ltern.200.46" system="knb" xmlns:eml="eml://ecoinformatics.org/eml-2.1.1" xmlns:xsi="http://www.w3.org/2001/XMLSchema-instance" xsi:schemaLocation="eml://ecoinformatics.org/eml-2.1.1 eml.xsd"> <access authSystem="knb" order="allowFirst"><allow><principal>public</principal>
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 <allow><principal>cn=pn_vic_alpine,o=unaffiliated,dc=ecoinformatics,dc=org</principal>
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 <dataset>  <title>Victorian Alpine Plot Network (ATEX): Vegetation Change and Phenology in Response to Increased Temperature, South-east Highlands, Australia, 2004–2014</title>
<creator id="1434960420939"><individualName><salutation>Professor</salutation>
 <givenName>Ary</givenName>
 <surName>Hoffmann</surName>
 </individualName>
 <organizationName>The University of Melbourne</organizationName>
 <positionName>Plot Leader</positionName>
 <address><deliveryPoint>Bio21 Institute, Departments of Zoology and Genetics</deliveryPoint>
 <deliveryPoint>The University of Melbourne</deliveryPoint>
 <city>Melbourne</city>
 <administrativeArea>Vic</administrativeArea>
 <postalCode>3010</postalCode>
 <country>Australia</country>
 </address>
 <phone phonetype="voice">03 8344 2282</phone>
 <electronicMailAddress>ary@unimelb.edu.au</electronicMailAddress>
 </creator>
 <creator id="1435131355716"><individualName><salutation>Dr</salutation>
 <givenName>Henrik</givenName>
 <surName>Wahren</surName>
 </individualName>
 <organizationName>La Trobe University</organizationName>
 <address><deliveryPoint>Department of Botany</deliveryPoint>
 <deliveryPoint>La Trobe University</deliveryPoint>
 <city>Bundoora</city>
 <administrativeArea>Vic</administrativeArea>
 <postalCode>3086</postalCode>
 <country>Australia</country>
 </address>
 </creator>
 <creator id="1435148448619"><individualName><givenName>James</givenName>
 <surName>Camac</surName>
 </individualName>
 <organizationName>Quantitative &amp; Applied Ecology Group, The School of Botany, The University of Melbourne</organizationName>
 <phone phonetype="voice">0400 972 404</phone>
 <electronicMailAddress>james.camac@gmail.com</electronicMailAddress>
 </creator>
 <creator id="1435148514986"><organizationName>The University of Melbourne</organizationName>
 </creator>
 <creator id="1435148529731"><organizationName>Research Centre for Applied Alpine Ecology, La Trobe University</organizationName>
 </creator>
<abstract><para>This data package shows the effects of experimental warming on plants in the Victorian Alpine region between 2004–2014. These data are from the Australian Tundra Experiment (ATEX) which is part of the International Tundra Experiment (ITEX). The data tables consist of a subset of previously published data packages which have been combined to demonstrate the conclusions discussed on pages 188–191 of the book Lindenmayer et al., 2014. Biodiversity and Environemntal Change: Monitoring, Challenges and Direction (Core Study 4. Climate change experiment in open heathlands/grassland, Bogong High Plains). They also include data which has been collected since the book had been published.

This experiment looks at the effects of increasing the near-surface soil temperature by ~1–2°C. 

As a consequence, the cover of grasses decreased in cover, while both forbs and shrubs increased in cover. Diversity increased as a result of changes in relative abundance and most growth forms increased in height. 
 
The ATEX experiment is locate at four sites on the Bogong High Plains, each site comprising multiple 1 square metre plots. The composition of each plot is sample using point quadrats every second snow-free season. The Victorian Alpine Plot Network research plots are revisited on a biannual basis, though measurements taken during surveys differ from visit to visit. A synopsis of related data packages which have been collected as part of the Victorian Alpine Plot Network’s full program is provided at http://www.ltern.org.au/index.php/ltern-plot-networks/victorian-alpine</para>
</abstract>
  <keywordSet><keyword>Vegetation structure</keyword>
 <keyword>Plant species composition</keyword>
 <keyword>Plant species abundance</keyword>
 <keyword>Individual plants</keyword>
 <keyword>Climate change</keyword>
 <keywordThesaurus>LTERN Monitoring Themes</keywordThesaurus>
 </keywordSet>
 <keywordSet><keyword>0602</keyword>
 <keywordThesaurus>ANZSRC-FOR</keywordThesaurus>
 </keywordSet>
 <keywordSet><keyword>Earth Science &gt; Biosphere &gt; Vegetation</keyword>
 <keywordThesaurus>GCMD</keywordThesaurus>
 </keywordSet>
 <keywordSet><keyword>Plant phenology</keyword>
 <keyword>Australian Tundra Experiment</keyword>
 <keyword>ATEX</keyword>
 <keyword>International Tundra Experiment</keyword>
 <keyword>ITEX</keyword>
 <keywordThesaurus>Keyword list</keywordThesaurus>
 </keywordSet>
 <intellectualRights><para>TERN-BY
Special conditions
Spatial coordinates for site names are available at https://www.ltern.org.au/knb/metacat/ltern6.244/html (Victorian Alpine Plot Network (ATEX): Plot Details - Spatial Coordinates, South-east Highlands, Australia).</para>
 </intellectualRights>
 <coverage> <temporalCoverage><rangeOfDates><beginDate><calendarDate>2004</calendarDate>
 </beginDate>
 <endDate><calendarDate>2014</calendarDate>
 </endDate>
 </rangeOfDates>
 </temporalCoverage>
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 <taxonRankValue>Acaena novaezelandiae</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Acetosella vulgaris</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Acrothamnus</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Acrothamnus hookeri</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Acrothamnus montanus</taxonRankValue>
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 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Agropyron velutinum</taxonRankValue>
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 <taxonRankValue>Agrostis venusta</taxonRankValue>
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 <taxonRankValue>Ajuga australis</taxonRankValue>
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 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Argyrotegium fordianum</taxonRankValue>
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 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Argyrotegium mackayi</taxonRankValue>
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 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Asperula gunnii</taxonRankValue>
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 <taxonRankValue>Asterolasia trymalioides</taxonRankValue>
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 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Australopyrum velutinum</taxonRankValue>
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 <taxonRankValue>Brachyscome decipiens</taxonRankValue>
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 <taxonRankValue>Cardamine</taxonRankValue>
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 <taxonRankValue>Carex</taxonRankValue>
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 <taxonRankValue>Carex breviculmis</taxonRankValue>
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 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Carex hebes</taxonRankValue>
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 <taxonRankValue>Carex rara</taxonRankValue>
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 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Celmisia costiniana</taxonRankValue>
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 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Celmisia pugioniformis</taxonRankValue>
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 <taxonRankValue>Cladonia</taxonRankValue>
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 <taxonRankValue>Colobanthus affinis</taxonRankValue>
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 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Cotula alpina</taxonRankValue>
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 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Craspedia coolaminica</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Craspedia jamesii</taxonRankValue>
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 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Deyeuxia</taxonRankValue>
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 <taxonRankValue>Deyeuxia monticola</taxonRankValue>
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 <taxonRankValue>Erigeron bellidioides</taxonRankValue>
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 <taxonRankValue>Erigeron nitidus</taxonRankValue>
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 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Geranium antrorsum</taxonRankValue>
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 <taxonRankValue>Geranium potentilloides</taxonRankValue>
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 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Goodenia hederacea</taxonRankValue>
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 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Grevillea australis</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Hovea montana</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Leptinella filicula</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Leptorhynchos squamatus</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Leucopogon hookeri</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Luzula alpina</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Luzula modesta</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Melicytus dentatus</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Microseris lanceolata</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Olearia brevipedunculata</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Olearia phlogopappa</taxonRankValue>
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 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Oreomyrrhis argentea</taxonRankValue>
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 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Oreomyrrhis eriopoda</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Pimelea alpina</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Pimelea axiflora</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Pimelea biflora</taxonRankValue>
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 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Plantago euryphylla</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Poa</taxonRankValue>
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 <taxonRankValue>Poa costiniana</taxonRankValue>
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 <taxonRankValue>Poa hiemata</taxonRankValue>
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 <taxonRankValue>Podolepis</taxonRankValue>
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 <taxonRankValue>Podolepis robusta</taxonRankValue>
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 <taxonRankValue>Poranthera microphylla</taxonRankValue>
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 <taxonRankValue>Prasophyllum tadgellianum</taxonRankValue>
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 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Ranunculus victoriensis</taxonRankValue>
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 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Rytidosperma nudiflorum</taxonRankValue>
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 <taxonRankValue>Rytidosperma penicillatum</taxonRankValue>
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 <taxonRankValue>Scaevola hookeri</taxonRankValue>
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 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Scleranthus biflorus</taxonRankValue>
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 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Scleranthus singuliflorus</taxonRankValue>
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 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Senecio pinnatifolius</taxonRankValue>
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 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Trachymene humilis</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Trifolium repens</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Trisetum spicatum</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Viola betonicifolia</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Xerochrysum subundulatum</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>hypochaeris radicata</taxonRankValue>
 </taxonomicClassification>
 </taxonomicCoverage>
 <geographicCoverage><geographicDescription>South-east Highlands</geographicDescription>
 <boundingCoordinates><westBoundingCoordinate>146.41728</westBoundingCoordinate>
 <eastBoundingCoordinate>147.40598</eastBoundingCoordinate>
 <northBoundingCoordinate>-36.73575</northBoundingCoordinate>
 <southBoundingCoordinate>-37.49639</southBoundingCoordinate>
 </boundingCoordinates>
 </geographicCoverage>
 </coverage>
 <contact><references>1435131355716</references>
 </contact>
 <contact><references>1435148448619</references>
 </contact>
 <contact><references>1434960420939</references>
 </contact>
 <methods><methodStep><description><section><title>Plot set-up</title>
 <para>Following the International Tundra Experiment (ITEX) protocol (Molau and Mølgaard 1996; Jarrad et al. 2009; Wahren et al. 2013), four open-heathland ATEX field sites, two burnt and two unburnt, were established in the Rocky Knobs area (36.90ºS, 147.27ºE) on the Bogong High Plains in 2003. The burnt and unburnt sites were ca. 1.7 km apart while within burn-type, each of the sites were separated by approximately 0.5 km. At each of the two unburnt sites, 26, 1 m2 plots are located along permanently marked transects. Transects are 10 m apart, 50 m long, and are marked with sturdy, red gum end-pegs. At each unburnt site, 13 of the plots are covered by a hexagonal open-topped chamber (OTC; base diameter 168 cm, top diameter 110 cm) and the remaining, control plots are uncovered. At each of the two burnt sites there are 14, 1 m2 plots, seven of which are covered by an OTC, and seven of which are uncovered, controls.</para>
 </section>
 </description>
 <instrumentation>Red gum end-pegs</instrumentation>
 <instrumentation>13 x hexagonal open-topped chambers</instrumentation>
 </methodStep>
 <methodStep><description><section><title>Hexagonal open-topped chambers (OTCs)</title>
 <para>The OTCs, which increase ambient temperatures inside the chambers at these sites by about 2 – 2.5°C, are constructed from lightweight, shatter-resistant fibreglass with high light transmittance (86%) and low transmittance of infra-red (&lt;5%). The OTCs for this project are about 50 cm tall, with 110 cm diameter open-tops, and bases 170 cm wide. This size is large enough to accommodate all species to be monitored, without influencing growth habits or reproductive structures via, e.g. edge effects..</para>
 </section>
 </description>
 </methodStep>
 <methodStep><description><section><title>Vegetation growth measurements</title>
 <para>Every second snow free season vegetative growth is recorded in seven species by measuring of growth amounts and converting measurements into a relative rate (i.e. relative rate of growth = (ti +1 – ti)/ti, where ti = measurement at time i). Measurements of selected species involved leaves of Carex breviculmis, Poa hiemata (Graminiods) and Celmisia pugioniformis, Erigeron bellidioides, and Plantago euryphylla (Forbs), and stems of Asterolasia trymalioides and Pimelea alpina. By using the relative rate of growth, the effect of initial size on measurements is removed. At the beginning of each growing season, plants are selected randomly for monitoring at every sub-plot within all ATEX plots. The ﬁrst measurements are taken as soon as the snow melts and sites can be accessed in October or November, the second measurements is taken mid-season in January, and the ﬁnal measurements is taken in March, the end of the active growing season. For the graminoids and C. pugioniformis, leaves are gathered and the longest live leaf is measured to the nearest 0.25cm for three random individuals of each species per plot.</para>
 <para>For the forbs, two random leaves on three random individuals of each species per plot are measured for length (from base to tip, excluding petiole) and width (at the widest point) to the nearest 1mm. Older leaves at the base of the rosette are avoided, as they have already grown to their full length. For the shrubs, the lengths of three random new shoots are monitored on three random individuals of each species per plot. The ITEX protocol recommends a variety of vegetative measurements (Molau and Mølgaard 1996), from which a subset of measurements are selected that are appropriate for the species in this study. Further details are in Jarrad et al. (2009).</para>
 <para>Contact data provider for more information.</para>
 </section>
 </description>
 </methodStep>
 <methodStep><description><section><title>Plant species composition</title>
 <para>Every second year vegetation is sampled by point quadrats using a 4 mm diameter steel pin, inserted vertically at 10 cm intervals within a grid of 100 points defined by a 1 m2 point-frame. At each point the top, intermediate and bottom species; canopy height; and condition of ground surface (bare soil, attached live or dead vegetation, loose litter) are recorded.</para>
 </section>
 </description>
 </methodStep>
 <sampling><studyExtent><description><para>See:
Molau U, Mølgaard P (1996) 'International Tundra Experiment (ITEX) Manual.' (Danish Polar Center: Copenhagen, Denmark)
Jarrad FC, Wahren C, Williams RJ, Burgman MA (2009) Subalpine plants show short-term positive growth responses to experimental warming and fire. Australian Journal of Botany 57(6), 465-473. 
Wahren C-H, Camac JS, Jarrad FC, Williams RJ, Papst WA, Hoffmann AA (2013) Experimental warming and long-term vegetation dynamics in an alpine heathland. Australian Journal of Botany 61(1), 36-51.</para>
 </description>
 </studyExtent>
 <samplingDescription><para>As for Study Extent Description.</para>
 </samplingDescription>
 </sampling>
 </methods>
 <project><title>Victorian Alpine Plot Network: Australian Tundra Experiment (ATEX)</title>
 <personnel><references>1435148514986</references>
 <role>Data Owner</role>
 </personnel>
 <personnel><references>1434960420939</references>
 <role>Plot Leader</role>
 </personnel>
 <personnel><references>1435131355716</references>
 <role>Data Provider</role>
 </personnel>
 <personnel><references>1435148448619</references>
 <role>Data Content Speacialist</role>
 </personnel>
 <funding><para>Funding for collection of these data prior to 2012 was provided through an Australia Research Council Linkage Grant, partnered through the Department of Sustainability and Environment, Commonwealth Scientific and Industrial Research Organisation (CSIRO), ES Link Services Pty Ltd, Mt Hotham Resort Management and Parks Victoria. These data were curated and published with strategic funds from a TERN initiative to publish long term data packages from the book Lindenmayer et al. 2014 Biodiversity and Environmental Change: Monitoring, Challenges and Direction. Since 2012 the Victorian Alpine Plot Network has been part of the Long Term Ecological Research Network (LTERN). This work was supported by the Australian Government’s Terrestrial Ecosystems Research Network (www.tern.org.au) – an Australian research infrastructure project established under the National Collaborative Research Infrastructure Strategy and Education Infrastructure Fund–Super Science Initiative through the (now) Department of Education and Training.</para>
 </funding>
 </project>
 <dataTable id="1435038273158"><entityName>vatx_grid_height_details_2004-2014_p592t906.csv</entityName>
 <entityDescription>Tree heights in ATEX plots</entityDescription>
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 <attributeDefinition>Date of observation</attributeDefinition>
 <measurementScale><dateTime><formatString>YYYY-MM-DD</formatString>
 </dateTime>
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 <attributeDefinition>Point quadrat site</attributeDefinition>
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 <attributeDefinition>Height of cover grid corner &quot;A&quot; of quadrant. The four corners A–D are arraged clockwise with corners A and B runing West to East, B and C run North to South, etc., with minor variations to account for terrain.</attributeDefinition>
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 <attributeDefinition>Height of cover grid corner &quot;B&quot; of quadrant. The four corners A–D are arraged clockwise with corners A and B runing West to East, B and C run North to South, etc., with minor variations to account for terrain.</attributeDefinition>
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 <attributeDefinition>Height of cover grid corner &quot;C&quot; of quadrant. The four corners A–D are arraged clockwise with corners A and B runing West to East, B and C run North to South, etc., with minor variations to account for terrain.</attributeDefinition>
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 <attributeDefinition>Height of cover grid corner &quot;D&quot; of quadrant. The four corners A–D are arraged clockwise with corners A and B runing West to East, B and C run North to South, etc., with minor variations to account for terrain.</attributeDefinition>
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 <attributeDefinition>Distance from overlying grid (approximately 1 metre above the ground surface) down to the top of tallest plant at this point</attributeDefinition>
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 <attributeDefinition>Type of ground cover at point</attributeDefinition>
 <measurementScale><nominal><nonNumericDomain><enumeratedDomain><codeDefinition><code>BG</code>
 <definition>Bare ground</definition>
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 <codeDefinition><code>BGD</code>
 <definition>Bare ground with a dense cover (depends on species, but mostly ≥10 leaves)</definition>
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 <codeDefinition><code>BGM</code>
 <definition>Bare ground with a medium cover (4 to 9 leaves)</definition>
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 <codeDefinition><code>BGS</code>
 <definition>Bare ground with a sparse cover (1-3 leaves)</definition>
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 <codeDefinition><code>FIXEDL</code>
 <definition>Fixed litter</definition>
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 <codeDefinition><code>FLL</code>
 <definition>Fine loose litter (litter &lt;5 mm thick)</definition>
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 <codeDefinition><code>FLLD</code>
 <definition>Fine loose litter with a dense cover</definition>
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 <codeDefinition><code>FLLM</code>
 <definition>Fine loose litter with a medium cover</definition>
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 <codeDefinition><code>FLLS</code>
 <definition>Fine loose litter with a sparse cover</definition>
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 <codeDefinition><code>PROBE</code>
 <definition>Temperature sensor</definition>
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 <codeDefinition><code>TLL</code>
 <definition>Thick loose litter (litter ≥5 mm thick)</definition>
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 <definition>Thick loose litter with a dense cover</definition>
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 <codeDefinition><code>TLLM</code>
 <definition>Thick loose litter with a medium cover</definition>
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 <codeDefinition><code>TLLS</code>
 <definition>Thick loose litter with a sparse cover</definition>
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 <attributeDefinition>Comments</attributeDefinition>
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 <attributeDefinition>Point quadrat point</attributeDefinition>
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 <attribute id="1540189162568"><attributeName>pq_status</attributeName>
 <attributeDefinition>Plant status (alive or dead)</attributeDefinition>
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 <additionalMetadata> <metadata> <additionalLinks> <url name="Victorian Alpine Plot Network home page">http://www.ltern.org.au/ltern-plot-networks/victorian-alpine</url>
 </additionalLinks>
 </metadata>
 </additionalMetadata>
 <additionalMetadata> <metadata> <additionalProjectInfo>This data package is comprised of data from the book Lindenmayer et al. 2014 Biodiversity and Environmental Change: Monitoring Challenges and Direction</additionalProjectInfo>
 </metadata>
 </additionalMetadata>
 </eml:eml>
