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<dataset> <title>Jervis Bay Booderee National Park Plot Network: Site-level Plot Data Collected During an Assessment of the Ecological and Cost Effectiveness of Invasive Plant Management in Achieving Conservation Goals: a Long-term Experimental Study, 2007-2014</title>
 <creator id="1397610412979"> <individualName> <salutation>Professor</salutation>
 <givenName>David</givenName>
 <surName>Lindenmayer</surName>
 </individualName>
 <organizationName>Fenner School of Environment and Society, The Australian National University</organizationName>
 <positionName>Principal Investigator</positionName>
 <address> <deliveryPoint>Fenner School of Environment and Society, The Australian National University</deliveryPoint>
 <deliveryPoint>Frank Fenner Building (Building 141), Fenner School of Environment and Society, The Australian National University</deliveryPoint>
 <city>Canberra</city>
 <administrativeArea>ACT</administrativeArea>
 <postalCode>0200</postalCode>
 </address>
 <phone phonetype="voice">02 61250654</phone>
 <electronicMailAddress>david.lindenmayer@anu.edu.au</electronicMailAddress>
 </creator>
 <creator id="1405302815995"> <individualName> <salutation>Mr</salutation>
 <givenName>Christopher</givenName>
 <surName>MacGregor</surName>
 </individualName>
 <organizationName>The Australian National University</organizationName>
 <positionName>Manager, Participant</positionName>
 <address> <deliveryPoint>The Fenner School of Environment and Society</deliveryPoint>
 <deliveryPoint>ANU College of Medicine, Biology and Environment, The Australian National University</deliveryPoint>
 <city>Canberra</city>
 <administrativeArea>ACT</administrativeArea>
 <postalCode>0200</postalCode>
 </address>
 <phone phonetype="voice">+61 2 4442 2238</phone>
 <electronicMailAddress>christopher.macgregor@anu.edu.au</electronicMailAddress>
 </creator>
 <creator id="1380080088288"> <organizationName>Director of National Parks (Parks Australia)</organizationName>
 </creator>
 <associatedParty id="1426482929527"> <individualName> <givenName>Martin</givenName>
 <surName>Fortescue</surName>
 </individualName>
 <role>Researcher</role>
 </associatedParty>
 <associatedParty id="1426482820402"> <individualName> <givenName>Nick</givenName>
 <surName>Dexter</surName>
 </individualName>
 <role>Researcher</role>
 </associatedParty>
 <associatedParty id="1405303552616"> <organizationName>Wreck Bay Aboriginal Community Council</organizationName>
 <role>The owners and joint managers of Booderee National Park.</role>
 </associatedParty>
 <associatedParty id="1426219213017"> <organizationName>Department of Defence (some sites on Defence land)</organizationName>
 <role>Land Owner</role>
 </associatedParty>
 <abstract><para>This vegetation data package comprises site level plot data collected as part of a controlled and replicated experimental study at Bherwerre Peninsula in Booderee National Park, which is located in the Jervis Bay Territory, Australia. The aim of the study is to estimate the effects of the different sub-treatments of Bitou Bush control methods on the abundance and recruitment of both the target species and native plant species. Sites were stratified into three broad groups, namely sites with no Bitou Bush; sites with Bitou Bush where a control regime of spray-fire-spray and spray-fire-fire was applied and combinations of particular treatments where only part of the treatment regime was applied. Data were collected from four 1 m x 1 m permanent survey plots situated on the 80 m transect on each of our 33 sites.  Each site was surveyed on 14 occasions, at different stages of the treatment sequence, so comparisons of no treatment, a partial sequence of treatments, and a full sequence can be made from observations at the same site, resulting in 356 site-survey combinations in total.  A synopsis of related data packages which have been collected as part of the Jervis Bay Booderee National Park Plot Network's full program is provided at http://www.ltern.org.au/index.php/ltern-plot-networks/jervis-bay-booderee-national-park.

These data were published as a component of the paper Lindenmayer et al., 2015. A Long-Term Experimental Case Study of the Ecological Effectiveness and Cost Effectiveness of Invasive Plant Management in Achieving Conservation Goals: Bitou Bush Control in Booderee National Park in Eastern Australia. PLOS ONE. DOI: http://dx.doi.org/10.1371/journal.pone.0128482</para>
 </abstract>
 <keywordSet> <keyword>Vegetation structure</keyword>
 <keyword>Plant species composition</keyword>
 <keyword>Plant species abundance</keyword>
 <keyword>Individual plants</keyword>
 <keyword>Fire</keyword>
 <keyword>Invasive plants</keyword>
 <keyword>Restoration</keyword>
 <keywordThesaurus>LTERN Monitoring Themes</keywordThesaurus>
 </keywordSet>
 <keywordSet> <keyword>0602</keyword>
 <keywordThesaurus>ANZSRC-FOR</keywordThesaurus>
 </keywordSet>
 <keywordSet> <keyword>Biological Classification&gt;Plants</keyword>
 <keywordThesaurus>GCMD Science Keywords</keywordThesaurus>
 </keywordSet>
<intellectualRights><para>TERN-BY-SA
Special Conditions
Access and use subject to negotiation upon request to data provider (Professor David Lindenmayer).</para>
</intellectualRights>
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 <taxonRankValue>Schelhammera undulata</taxonRankValue>
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 <taxonRankValue>Smilax australis</taxonRankValue>
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 <taxonRankValue>Solanum species</taxonRankValue>
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 <taxonRankValue>Solanum stelligerum</taxonRankValue>
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 <taxonRankValue>Sporobolus virginicus</taxonRankValue>
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 <taxonRankValue>Stephania japonica variety discolor</taxonRankValue>
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 <taxonomicClassification> <taxonRankName>Species</taxonRankName>
 <taxonRankValue>Styphelia triflora</taxonRankValue>
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 <taxonomicClassification> <taxonRankName>Species</taxonRankName>
 <taxonRankValue>Synoum glandulosum</taxonRankValue>
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 <taxonRankValue>Tetratheca thymifolia</taxonRankValue>
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 <taxonomicClassification> <taxonRankName>Species</taxonRankName>
 <taxonRankValue>Themeda australis</taxonRankValue>
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 <taxonRankValue>Trema aspera</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification> <taxonRankName>Species</taxonRankName>
 <taxonRankValue>Unidentified grass</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification> <taxonRankName>Species</taxonRankName>
 <taxonRankValue>Unidentified seedling</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification> <taxonRankName>Species</taxonRankName>
 <taxonRankValue>Veronica calycina</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification> <taxonRankName>Species</taxonRankName>
 <taxonRankValue>Viola hederacea</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification> <taxonRankName>Species</taxonRankName>
 <taxonRankValue>Zieria smithii</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification> <taxonRankName>Species</taxonRankName>
 <taxonRankValue>Zoysia macrantha</taxonRankValue>
 </taxonomicClassification>
 </taxonomicCoverage>
 <geographicCoverage> <geographicDescription>Bherwerre Peninsula in Booderee National Park which is located in the Jervis Bay Territory.</geographicDescription>
 <boundingCoordinates> <westBoundingCoordinate>150.613285</westBoundingCoordinate>
 <eastBoundingCoordinate>150.678648</eastBoundingCoordinate>
 <northBoundingCoordinate>-35.131813</northBoundingCoordinate>
 <southBoundingCoordinate>-35.164476</southBoundingCoordinate>
 </boundingCoordinates>
 </geographicCoverage>
 <temporalCoverage><rangeOfDates><beginDate><calendarDate>2007-05-14</calendarDate>
 </beginDate>
 <endDate><calendarDate>2014-03-03</calendarDate>
 </endDate>
 </rangeOfDates>
 </temporalCoverage>
 </coverage>
 <contact> <references>1397610412979</references>
 </contact>
 <contact> <references>1405302815995</references>
 </contact>
 <methods> <methodStep> <description> <section> <title>Plot setup</title>
 <para>Data were collected from four 1 m x 1 m permanent survey plots situated on the 80 m transect on each of our 34 sites.  Plots on each transect were set at least 20 m apart. At each plot, a 1m x 1m frame was placed over the vegetation.</para>
 </section>
 </description>
 <instrumentation>Not specified</instrumentation>
 </methodStep>
 <methodStep> <description> <section> <title>Treatment</title>
 <para>The full treatment regime for the control of Bitou Bush in BNP is a combination of sequential sub-treatments. A key sub-treatment is spraying of Ultra Low Volume (ULV) glyphosate either aerially by helicopter or on the ground. The concentration of glyphosate varies by method of application, due to the size of droplets and the coverage provided by the applicator. Aerial spraying uses a concentration of 15% glyphosate, the splatter method from a hose connected to a tank on a 4WD vehicle uses 10% glyphosate, and the spot-spray method from a knapsack uses 5% glyphosate. Spraying takes place in winter (when native plants are relatively metabolically inactive but Bitou Bush remains metabolically active; Toth, Milham &amp; Nazer 1993). After the first application of herbicide, treated Bitou Bush plants cure for &gt;1 year before being burned in a prescribed fire. The fire triggers germination of Bitou Bush seed in the soil and a year later, a follow-up spray of ULV glyphosate kills fire-triggered seedlings. Prescribed fires are applied to 15-85 ha compartment units of treated vegetation in any given year.</para>
 </section>
 </description>
 <instrumentation>Not specified</instrumentation>
 </methodStep>
 <methodStep> <description> <section> <title>Data collection</title>
 <para>Percentage cover measurements were collected for live Bitou Bush, dead Bitou Bush, all native vegetation, crown cover (by observation above the plot to an area of approximately 10 m x 10 m). In addition, we completed counts of the number of individual live Bitou Bush plants, dead Bitou Bush plants, other exotic plant species, and native plant species. We also derived a list of species in each 1 m x 1 m survey plot, from which we generated data for the number of exotic and native plant species. A single observer completed all vegetation surveys four times annually from 2007 to 2013.</para>
 </section>
 </description>
 <instrumentation>Not specified</instrumentation>
 </methodStep>
 <sampling> <studyExtent> <description> <para>The effects of different sub-treatments of Bitou Bush control methods on the abundance and recruitment of both the target species and on native plant species are measured. Sites were stratified into three broad groups, namely sites with no Bitou Bush; sites with Bitou Bush where the complete control regime of spray-fire-spray was applied; and sites with Bitou Bush where only part of the treatment regime was applied. Data were collected from four 1 m x 1 m permanent survey plots situated on the 80 m transect on each of our 33 sites, and each site was surveyed on up to 14 occasions, giving 356 site-survey combinations in total. Plot-level mean values are provided for a number of variables. In one observation (1-51), plants were only counted for a subset of the four plots. Those values are denoted as an &quot;*&quot;.</para>
 </description>
 </studyExtent>
 <samplingDescription> <para>The study design accounted for several practical realities associated with the control of a weed of national significance in a reserve. First, under the management plan for BNP, all areas infested with Bitou Bush must be subject to some kind of treatment (even if the recommended protocol cannot be fully implemented; see below). This precluded the establishment of control sites where Bitou Bush occurred but remained untreated. However, we included some sites where Bitou Bush had not occurred. These sites were used as controls in assessing the effect of the treatments on native vegetation. Second, the large spatial extent of Bitou Bush infestation on Bherwerre Peninsula meant that it is not possible to spray all affected areas at the same time; even if this was possible, there were insufficient resources to burn all treated areas simultaneously. Third, logistical and human safety issues mean that only some areas received the complete spray-fire-spray regime and others were subject to only parts of it or different combinations of particular treatments. Therefore, all of the sites in our experiment had different treatment histories. Fourth, the recommended spray-fire-spray treatment regime requires several years to be fully implemented at a given site. This meant that because a given site is surveyed many times throughout the duration of the study, it could appear under different treatment sequences according to the progression of particular treatments over time. Fifth, it was not possible to prevent some kinds of other disturbances and in late 2007, a low to moderate severity wildfire burned part of our study area resulting in some sites being burned once by prescribed fire (post-Bitou Bush treatment) and once by a wildfire.</para>
 </samplingDescription>
 </sampling>
 </methods>
 <project><title>Jervis Bay Booderee National Park Plot Network</title>
 <personnel><references>1397610412979</references>
 <role>Data Owner</role>
 </personnel>
 <personnel><references>1405302815995</references>
 <role>Data Manager</role>
 </personnel>
 <funding><para>Since 2012 this project 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 facility established under the National Collaborative Research Infrastructure Strategy and Education Infrastructure Fund–Super Science Initiative through the Department of Industry, Innovation, Science, Research and Tertiary Education.</para>
 </funding>
 </project>
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