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<dataset> <title>Nanangroe Plantation Plot Network: Bird Point Count Data, Southwest Slopes, NSW,  Australia, 1998–2011</title>
 <creator id="1408532875740"> <individualName> <salutation>Professor</salutation>
 <givenName>David</givenName>
 <surName>Lindenmayer</surName>
 </individualName>
 <organizationName>The Fenner School of Environment and Society</organizationName>
 <positionName>Principal investigator</positionName>
 <address> <deliveryPoint>ANU College of Medicine, Biology and Environment</deliveryPoint>
 <deliveryPoint>The Australian National University</deliveryPoint>
 <city>Canberra</city>
 <administrativeArea>ACT</administrativeArea>
 <postalCode>2601</postalCode>
 <country>Australia</country>
 </address>
 <phone phonetype="voice">+61 2 6125 0654</phone>
 <electronicMailAddress>David.Lindenmayer@anu.edu.au</electronicMailAddress>
 </creator>
 <abstract><para>The Nanangroe Plantation Plot Network Bird Point Count Data contains counts of all birds seen and heard over five minute periods at each of the 0 m, 100 m and 200 m posts along a permanent 200m transect at each site.  Dawn bird counts are conducted every 1-2 years using repeated point interval counts.  Repeated point counts by two different observers on two different days are undertaken. The distance that each bird was seen/heard at is recorded along with bird abundance and any anecdotal comments (e.g. breeding behaviour). Bird species presence/absence or detection rates within 50 m of the observer is commonly used for analysis.

The principle objective of the Nanangroe study is to directly quantify changes in woodland vertebrate assemblages and their relationships with habitat variables when the surrounding landscape matrix is converted from a semi-cleared grazing landscape to a landscape dominated by an exotic softwood plantation (Lindenmayer, DB, Cunningham, RB, MacGregor, C, Tribolet, C &amp; Donnelly, CF 2001, ‘A prospective longitudinal study of landscape matrix effects on fauna in woodland remnants: experimental design and baseline data’, Biological Conservation, vol 101 no 2, p. 160).

The study area is located in the Southwest slopes of NSW west of Lake Burrinjuck and includes four exotic Pine Plantations (Nanangroe, Cotway, East Bungongo and Bungongo), as well as private properties adjacent those plantations. Repeated sampling of the vegetation structure and cover and selected vertebrate groups on all sites from 1998 has created a long term dataset. 

A synopsis of related data packages which have been collected as part of the Nanangroe Plantation Forest Plot Network’s full program is provided at   http://www.ltern.org.au/index.php/ltern-plot-networks/nanangroe-plantation.</para>
 </abstract>
 <keywordSet> <keyword>Birds</keyword>
 <keyword>Bird counts</keyword>
 <keywordThesaurus>Keywords List</keywordThesaurus>
 </keywordSet>
 <keywordSet> <keyword>Birds</keyword>
 <keyword>Grazing domestic livestock</keyword>
 <keyword>Fragmentation</keyword>
 <keywordThesaurus>LTERN Monitoring Themes</keywordThesaurus>
 </keywordSet>
 <keywordSet> <keyword>0501</keyword>
 <keyword>0602</keyword>
 <keyword>0608</keyword>
 <keywordThesaurus>ANZSRC-FOR</keywordThesaurus>
 </keywordSet>
 <keywordSet> <keyword>Earth Science &gt; Biological Classification &gt; Animals/Vertebrates &gt; Birds</keyword>
 <keywordThesaurus>GCMD</keywordThesaurus>
 </keywordSet>
<intellectualRights><para>CC-BY-4_0
Special Conditions:
Co-authorship with the data provider (Professor David Lindenmayer) of any publication of research utilising this data is an expected outcome.  The data provider requests consultation, including a summary of the proposed research and intended use before publication of research utilising this data is possible.</para>
</intellectualRights>
  <coverage> <temporalCoverage><rangeOfDates><beginDate><calendarDate>1998</calendarDate>
 </beginDate>
 <endDate><calendarDate>2011</calendarDate>
 </endDate>
 </rangeOfDates>
 </temporalCoverage>
 <geographicCoverage><geographicDescription>The Nanangroe Plantation Plot Network is located in the southwest slopes of NSW west of Lake Burrinjuck and includes four exotic Pine Plantations (Nanangroe, Cotway, East Bungongo and Bungongo), as well as private properties adjacent those plantations.</geographicDescription>
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 <taxonRankValue>Rhipidura leucophrys</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Rhipidura rufifrons</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Sericornis frontalis</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Smicrornis brevirostris</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Stagonopleura guttata</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Strepera graculina</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Strepera versicolor</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Sturnus vulgaris</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Tachybaptus novaehollandiae</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Threskiornis molucca</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Threskiornis spinicollis</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Todiramphus pyrrhopygius</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Todiramphus sanctus</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Turdus merula</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Turnix pyrrhothorax</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Turnix varius</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Vanellus miles</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Zoothera lunulata</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Zosterops lateralis</taxonRankValue>
 </taxonomicClassification>
 </taxonomicCoverage>
 </coverage>
 <contact> <references>1409029639827</references>
 </contact>
 <methods><methodStep><description><section><title>Plot set-up</title>
 <para>Initially all patches of remnant native vegetation on areas designated for pine plantation were characterised. Fifty remnants were randomly selected with stratification, such as vegetation type, patch size, established year of surrounding pine trees.  Fifty-six remnants on adjacent farms to pine plantations were selected to match those 50 remnants, to make sure that remnants from two groups were as similar as possible.  Ten sites in cleared paddocks around the woodland remnants on the grazing properties and 10 sites in areas dominated by newly planted radiate pine trees were established as ‘‘landscape matrix’’ sites. Those sites were established in 1998, but a few sites were scrapped due to non-accessibility or vast invasion of weed. To make up for those abandoned sites, additional sites were established within a few years since the first establishment.</para>
 <para>For more details, please refer to Lindenmayer, DB, Cunningham, RB, MacGregor, C, Tribolet, C &amp; Donnelly, CF 2001, ‘A prospective longitudinal study of landscape matrix effects on fauna in woodland remnants: experimental design and baseline data’, Biological Conservation,  vol 101 no 2,  pp. 157-169.</para>
 </section>
 </description>
 <instrumentation>ArcGIS, GPS, Tape measure, Steel star picket posts, reflective tape, cattle ear tags: a star picket has been placed from 0m to 200m along a transect with 50m intervals.</instrumentation>
 </methodStep>
 <methodStep><description><section><title>Bird Point Count Surveys</title>
 <para>Dawn bird counts are conducted every 1-2 years using repeated point interval counts. Bird observers count all birds seen and heard over five minute periods at each of the 0 m, 100 m and 200 m posts along a permanent 200m transect established at each site. Repeated point counts by two different observers on two different days are undertaken. The distance that each bird was heard and seen at is recorded along with bird abundance and any anecdotal comments (e.g. breeding behaviour). Bird species presence/absence or detection rates within 50 m of the observer is commonly used for analysis.</para>
 </section>
 </description>
 <instrumentation>Binoculars, field guide.</instrumentation>
 </methodStep>
 <methodStep><description><section><title>Documentation</title>
 <para>The distance that each bird was heard and seen at is recorded along with bird abundance and any anecdotal comments (e.g. breeding behaviour).</para>
 </section>
 </description>
 <instrumentation>Clipboard, pencil and datasheet.</instrumentation>
 </methodStep>
 <sampling><studyExtent><description><para>Bird point count surveys were not coducted between 2008 and 2010 inclusive.</para>
 </description>
 </studyExtent>
 <samplingDescription><para>Refer to Lindenmayer, DB, Cunningham, RB, MacGregor, C, Tribolet, C &amp; Donnelly, CF 2001, ‘A prospective longitudinal study of landscape matrix effects on fauna in woodland remnants: experimental design and baseline data’, Biological Conservation, vol 101 no 2.</para>
 </samplingDescription>
 </sampling>
 </methods>
 <project><title>Nanangroe Plantation Plot Network</title>
 <personnel><references>1408532875740</references>
 <role>Data Owner</role>
 </personnel>
 <personnel id="1409029639827"><individualName><givenName>Sachiko</givenName>
 <surName>Okada</surName>
 </individualName>
 <organizationName>The Fenner School of Environment and Society</organizationName>
 <positionName>Manager, Participant</positionName>
 <address><deliveryPoint>ANU College of Medicine, Biology and Environment</deliveryPoint>
 <deliveryPoint>The Australian National University</deliveryPoint>
 <city>Canberra</city>
 <administrativeArea>ACT</administrativeArea>
 <postalCode>2601</postalCode>
 <country>Australia</country>
 </address>
 <electronicMailAddress>sachiko.okada@anu.edu.au</electronicMailAddress>
 <role>Manager, Participant</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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 </additionalMetadata>
 </eml:eml>
