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 <dataset> <title>Nanangroe Plantation Plot Network: Plot Details - Spatial Coordinates, Southwest Slopes, NSW, Australia</title>
 <creator id="1500360509028"><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>
 <associatedParty id="1500360528537"><individualName><salutation>Dr</salutation>
 <givenName>Ross</givenName>
 <surName>Cunningham</surName>
 </individualName>
 <organizationName>Fenner School of Environment and Society, The Australian National University</organizationName>
 <role>Content Provider</role>
 </associatedParty>
 <abstract><para>Nanangroe Plantation Plot Network was established in 1998 with a principle objective 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. These long term data include:
•	vegetation data,
•	bird point counts,
•	herpetofauna survey,
•	arboreal marsupial spotlighting,
•	nocturnal bird spotlighting,
•	opportunistic frog spotlighting

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>GPS co-ordinates</keyword>
 <keyword>Plot setup</keyword>
 <keyword>Geographic</keyword>
 <keyword>Plot details</keyword>
 <keyword>Spatial coordinates</keyword>
 <keywordThesaurus>Keywords</keywordThesaurus>
 </keywordSet>
 <keywordSet><keyword>0501</keyword>
 <keywordThesaurus>ANZSRC-FOR</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> <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>
 <boundingCoordinates><westBoundingCoordinate>148.313807</westBoundingCoordinate>
 <eastBoundingCoordinate>148.534563</eastBoundingCoordinate>
 <northBoundingCoordinate>-34.912979</northBoundingCoordinate>
 <southBoundingCoordinate>-35.069528</southBoundingCoordinate>
 </boundingCoordinates>
 </geographicCoverage>
 </coverage>
 <contact id="1500359251156"><individualName><salutation>Dr</salutation>
 <givenName>Mason</givenName>
 <surName>Crane</surName>
 </individualName>
 <organizationName>The Australian National University</organizationName>
 <positionName>Senior Research Officer</positionName>
 <address><deliveryPoint>Fenner School of Environment and Society</deliveryPoint>
 <deliveryPoint>The Australian National University</deliveryPoint>
 <city>Canberra</city>
 <administrativeArea>ACT</administrativeArea>
 <postalCode>2601</postalCode>
 </address>
 <phone phonetype="voice">0427 770 594</phone>
 <electronicMailAddress>mason.crane@anu.edu.au</electronicMailAddress>
 </contact>
 <methods><methodStep><description><section><title>Plot selection</title>
 <para>The study area is 10–20 km south-east of the town of Jugiong in southern NSW (Fig. 1), and it is bounded by the Murrumbidgee River to the north and the Bungongo State Forest, 5–8 km to the south and east. Annual precipitation across the study area ranges from 775 to 900 mm and is uniformly distributed throughout the year. Summers are typically hot. The name of the field study is taken from the Nanangroe Station — a large property where a major new radiata pine plantation has recently been established. The study region was chosen because:</para>
 <para>(1) recent large-scale changes in landscape cover have occurred due to the establishment of new radiata pine plantations at four former grazing properties newly acquired by State Forests of NSW;</para>
 <para>(2) long-term access to semi-cleared grazing properties which support numerous woodland remnants and which are located adjacent to the new Radiata Pine plantation has been obtained;</para>
 <para>(3) the region contains a wide range of woodland vegetation types (see later). This will allow us to quantify the differences in fauna between different types of woodland. This makes our natural experiment different from many other studies that have focussed on one or only a few woodland types (e.g. Er, 1995; Prober and Thiele, 1995; Haddeon and Westbrooke, 1996; Arnold and Weeldenberg, 1998); and</para>
 <para>(4) the woodland remnants in the study region vary in their physical condition, location (hilltops versus midslopes, etc.), and many other attributes (Table 1) making it possible to sample a broad range of environmental conditions and, in turn, model the relationships between species occurrence and these covariates.</para>
 <para>The original vegetation cover in the study area included a suite of woodland vegetation types, particularly those dominated by yellow box (Eucalyptus melliodora), red box (Eucalyptus polyanthemos), white box (Eucalyptus albens), red stringybark (Eucalyptus macrorhyncha), and Blakely’s red gum (Eucalyptus blakelyi). Much of the original cover has been cleared over the past 150 years, primarily for domestic stock grazing (Bungongo Centenary Committee, 1986). Only fragmented patches now remain of what was formerly continuous woodland vegetation cover.</para>
 <para>Clearing operations to plant radiata pine in the areas surrounding the woodland remnants involves the felling and burning of isolated paddock trees and other shrubby vegetation. The cleared land is then deep-ripped with a bulldozer to create mounds of earth in which radiata pine seedlings are planted. These are standard plantation establishment procedures employed widely throughout south-eastern Australia.</para>
 <para>[Lindenmayer, et al. 2001, A prospective longitudinal study of landscape matrix effects on fauna in woodland remnants: experimental design and baseline data. Biological Conservation 101: 157–169 [159–160]</para>
 </section>
 </description>
 </methodStep>
 <methodStep><description><section><title>Plot setup</title>
 <para>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. Thus, the initial phase of the experiment is the establishment of a set of foundation sites. This involved characterizng all patches of remnant native vegetation on areas designated for pine plantation. Attributes of the 70 remnants included patch size (ha), dominant tree species, age and condition of overstorey trees, understorey condition, shape class, topographic position, and the density of trees within the patch. Patch sizes varied from 0.5 to 9.7 ha. Four broad vegetation classes were recognizd as part of field surveys. The species in these groups were:</para>
 <para>(1) red box and red stringybark (co-dominant), apple box (Eucalyptus bridgesiana), long-leaf box (Eucalyptus goniocalyx), and broad-leaved peppermint (Eucalyptus dives);</para>
 <para>(2) swamp gum (Eucalyptus camphora);</para>
 <para>(3) yellow box, white box, red stringybark (co-dominant) and Blakely’s red gum; and</para>
 <para>(4) river oak (Casuarina cunninghamiana).</para>
 <para>[Lindenmayer, et al. 2001, A prospective longitudinal study of landscape matrix effects on fauna in woodland remnants: experimental design and baseline data. Biological Conservation 101: 157–169 [160]</para>
 </section>
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 <project><title>Nanangroe Plantation Plot Network</title>
 <personnel><references>1500360509028</references>
 <role>Data Owner</role>
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 <personnel><references>1500359251156</references>
 <role>Plot network contact</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>
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 <attributeDefinition>Plot context</attributeDefinition>
 <measurementScale><nominal><nonNumericDomain><enumeratedDomain><codeDefinition><code>AGR</code>
 <definition>Agricurtural land</definition>
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 <codeDefinition><code>PPR</code>
 <definition>Private property reserve</definition>
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 <definition>State forest reserve</definition>
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 <attributeDefinition>Topography of plot</attributeDefinition>
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<attributeDefinition>Average degree of the slope of the landscape based on the slope at three points along the transect (0 m, 100 m, and 200 m)</attributeDefinition>
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 <codeDefinition><code>178</code>
 <definition>Blakely's dominates</definition>
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 <codeDefinition><code>211</code>
 <definition>River Oak</definition>
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 <codeDefinition><code>216</code>
 <definition>Improved Pasture and Cropland</definition>
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 <codeDefinition><code>217</code>
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 <codeDefinition><code>218</code>
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 <measurementScale><nominal><nonNumericDomain><enumeratedDomain><codeDefinition><code>94</code>
 <definition>Scribbly Gum-Stringybark-Silvertop Ash</definition>
 </codeDefinition>
 <codeDefinition><code>132</code>
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 <codeDefinition><code>170</code>
 <definition>Yellow-White-Red Gum</definition>
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 <definition>White Box Dom.</definition>
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 <definition>Apple/Long leaved Box</definition>
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 <definition>Swamp Gum/Oak</definition>
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 <definition>Blakelys/Yellow Box</definition>
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 <codeDefinition><code>6</code>
 <definition>Misc.</definition>
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<attributeDefinition>Disturbance score avereaged from 3 points along the transect (0 m, 100 m, and 200 m). The score is based on the number of disturbance categories evident at each point. The categories are: Logging, Fire, Livestock grazing, Mining, Other</attributeDefinition>
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