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 <dataset> <title>Desert Ecology Plot Network: Reptile Abundance Plot-data, Simpson Desert, Western Queensland, 2015</title>
 <creator id="1442282051407"><individualName><salutation>Professor</salutation>
 <givenName>Glenda</givenName>
 <surName>Wardle</surName>
 </individualName>
 <organizationName>The University of Sydney</organizationName>
 <positionName>Plot Leader</positionName>
 <address><deliveryPoint>Heydon-Laurence Building A08</deliveryPoint>
 <deliveryPoint>The University of Sydney</deliveryPoint>
 <city>Sydney</city>
 <administrativeArea>NSW</administrativeArea>
 <postalCode>2006</postalCode>
 <country>Australia</country>
 </address>
 <phone phonetype="voice">02 9351 7113 or 0425 382 205</phone>
 <electronicMailAddress>glenda.wardle@sydney.edu.au</electronicMailAddress>
 </creator>
 <creator id="1442282105473"><individualName><salutation>Professor</salutation>
 <givenName>Chris</givenName>
 <surName>Dickman</surName>
 </individualName>
 <organizationName>The University of Sydney</organizationName>
 <positionName>Plot Leader</positionName>
 <address><deliveryPoint>Heydon-Laurence Building A08</deliveryPoint>
 <deliveryPoint>The University of Sydney</deliveryPoint>
 <city>Sydney</city>
 <administrativeArea>NSW</administrativeArea>
 <postalCode>2060</postalCode>
 <country>Australia</country>
 </address>
 <phone phonetype="voice">02 9351 2318</phone>
 <electronicMailAddress>chris.dickman@sydney.edu.au</electronicMailAddress>
 </creator>
 <abstract><para>This herpetofauna abundance plot data package comprises capture data for a specified duration of trapping nights (usually 3 night session) in the Simpson Desert, Western Queensland. Date, site and grid number were identified and recaptures during the same session were removed (i.e. individuals were only counted once). Date, site and grid number were recorded for all captures, and captured animals were also marked by a unique toe clip prior to their release to identify recaptures. The network program uses a core of 12 sites which are sampled every April-May. The trapping survey aims to quantitatively track long-term shifts in biodiversity and ecological processes in relation to key drivers, including unpredictable rainfall and droughts, fire, feral predators and grazing. A synopsis of related data packages which have been collected as part of the Desert Ecology's full program is provided at http://www.ltern.org.au/index.php/ltern-plot-networks/desert-ecology.</para>
 </abstract>
 <keywordSet><keyword>Earth Science &gt; Biological Classification &gt; Animals/Vertebrates &gt; Reptiles</keyword>
 <keywordThesaurus>GCMD</keywordThesaurus>
 </keywordSet>
 <keywordSet><keyword>0501</keyword>
 <keyword>0602</keyword>
 <keyword>0608</keyword>
 <keywordThesaurus>ANZSRC-FOR</keywordThesaurus>
 </keywordSet>
 <keywordSet><keyword>Herpetofauna</keyword>
 <keywordThesaurus>LTERN Monitoring Themes</keywordThesaurus>
 </keywordSet>
 <keywordSet><keyword>Herpetofauna</keyword>
 <keywordThesaurus>Keywords List</keywordThesaurus>
 </keywordSet>
 <intellectualRights><para>CC-BY-4_0
Special Conditions
Data users must request permission from the Data Provider (Glenda Wardle or Chris Dickman) before access to latitudinal and longitudinal data is granted.</para>
 </intellectualRights>
 <coverage> <geographicCoverage><geographicDescription>Simpson Desert, Western Queensland.</geographicDescription>
 <boundingCoordinates><westBoundingCoordinate>137.86511</westBoundingCoordinate>
 <eastBoundingCoordinate>138.6059</eastBoundingCoordinate>
 <northBoundingCoordinate>-23.20549</northBoundingCoordinate>
 <southBoundingCoordinate>-23.99417</southBoundingCoordinate>
 </boundingCoordinates>
 </geographicCoverage>
 <taxonomicCoverage><taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Ctenophorus clayi</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Ctenophorus isolepis</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Ctenophorus nuchalis</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Ctenotus ariadnae</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Ctenotus brooksi</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Ctenotus calurus</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Ctenotus dux</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Ctenotus helenae</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Ctenotus leae</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Ctenotus pantherinus</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Ctenotus regius</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Diporiphora winneckei</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Egernia inornata</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Eremiascincus fasciolatus</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Heteronotia binoei</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Lerista aericeps</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Lerista labialis</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Lophognathus longirostris</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Menetia greyii</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Moloch horridus</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Morethia ruficauda</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Nephrurus levis</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>No captures</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Notaden nichollsi</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Pogona vitticeps</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Ramphotyphlops endoterus</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Rhynchoedura ornata</taxonRankValue>
 </taxonomicClassification>
 <taxonomicClassification><taxonRankName>Species</taxonRankName>
 <taxonRankValue>Varanus brevicauda</taxonRankValue>
 </taxonomicClassification>
 </taxonomicCoverage>
 <temporalCoverage><singleDateTime><calendarDate>2015</calendarDate>
 </singleDateTime>
 </temporalCoverage>
 </coverage>
 <contact><references>1442282051407</references>
 </contact>
 <contact><references>1442282105473</references>
 </contact>
 <contact id="1442282128694"><individualName><salutation>Dr</salutation>
 <givenName>Aaron</givenName>
 <surName>Greenville</surName>
 </individualName>
 <organizationName>The University of Sydney</organizationName>
 <positionName>Research Associate</positionName>
 <address><deliveryPoint>Heydon-Laurence Building A08</deliveryPoint>
 <deliveryPoint>The University of Sydney</deliveryPoint>
 <city>Sydney</city>
 <administrativeArea>NSW</administrativeArea>
 <postalCode>2006</postalCode>
 <country>Australia</country>
 </address>
 <phone phonetype="voice">02 9351 8577</phone>
 <electronicMailAddress>aaron.greenville@sydney.edu.au</electronicMailAddress>
 </contact>
 <contact id="1442282151469"><individualName><salutation>Mr</salutation>
 <givenName>Bobby</givenName>
 <surName>Tamayo</surName>
 </individualName>
 <organizationName>The University of Sydney</organizationName>
 <positionName>Operational Manager</positionName>
 <address><deliveryPoint>Heydon-Laurence Building A08</deliveryPoint>
 <deliveryPoint>The University of Sydney</deliveryPoint>
 <city>Sydney</city>
 <administrativeArea>NSW</administrativeArea>
 <postalCode>2060</postalCode>
 <country>Australia</country>
 </address>
 <phone phonetype="voice">02 9351 8577</phone>
 <electronicMailAddress>bobby.tamayo@sydney.edu.au</electronicMailAddress>
 </contact>
 <methods><methodStep><description><section><title>Plot set-up</title>
 <para>The network program uses a core of 12 sites which are spaced at least 15 km apart, each comprising two 1-ha trapping grids, or plots which are spaced between 0.5-2 km apart. Each of the 24 trapping grids is set out with thirty-six traps arrayed in a grid covering 1 ha; each grid comprises 6 lines of 6 traps spaced 20 m apart. The top line of traps extends along the dune crest, where consecutive numbering starts, and finishes along the sixth line 100 m distant in the dune valley or ‘swale’. Traps on each grid are opened for 1–6 nights (usually 3) at an annual sampling interval (usually each April) and checked in the mornings and sometimes afternoons, and animals are removed for processing.</para>
 </section>
 </description>
 <instrumentation>Pitfall traps capped with metal lids, fence droppers marking each trap</instrumentation>
 <instrumentation>PVC stormwater pipe, 160 mm in diameter and 600 mm deep drift fence of aluminium wire mesh (flyscreen) 30 cm x 2.5 m</instrumentation>
 </methodStep>
 <methodStep><description><section><title>Pitfall trapping</title>
 <para>Herpetofauna are captured in pitfall traps. Each pitfall is made from PVC stormwater pipe, 160 mm in diameter and 600 mm deep, sunk vertically into the ground so that its top is flush with ground level. To increase trap success, by intercepting and guiding surface-active animals into the trap, a drift fence of aluminium wire mesh (flyscreen) extends outwards from the top of each trap, secured in place by means of a shallow trench. The fence is 30 cm high and runs for 2.5 m on each side of the pitfall opening. The bottom end of the pit is covered with flyscreen to form a floor to prevent captured animals from digging their way out, and all pits are capped with metal lids when not in use. A tiny amount of insecticide (Coopex) is sprinkled around each trap to prevent ant attack.</para>
 <para>•	Pitfalls must be dug into the ground, so that the lip of the pipe is level to the ground, this can be done using a shovel. Wire mesh drift fence is bent at about 10 cm to form an L-shape and dug into the ground and pulled straight and upright.</para>
 <para>•	Open all 36 pits using a spoon or pocket screwdriver</para>
 <para>•	Make sure the mesh is directly over the open pit and there is no a lip as reptiles can use it as a bridge over the pit and don’t get caught.</para>
 <para>•	Empty out excess sand from all pits .</para>
 <para>•	Sprinkle Coopex around the edge of each pit to deter ants.</para>
 <para>•	Check pitfall traps in the cool of the early morning to reduce stress on the animal.</para>
 <para>•	Thoroughly check each pitfall, first by visually  ensuring that there is not a snake or other venomous animal inside the pit. Once certain that it is safe, cover hand with calico trapping bag and stick arm down pit and feel around for any mammals or reptiles, carefully sift through the sand as Leristas and other small lizards are hard to see. Leather gloves can be worn for extra protection against bites and scratches.</para>
 <para>•	Remove any invertebrates from the pit, such as scorpions and centipedes and release at point of capture.</para>
 <para>•	Be careful when removing animals from pitfalls, do not grab any animal by the tail. Place bag over animal and invert it inside pit to safely secure animal.</para>
 <para>•	Place each animal in a separate calico bag and tie the top tightly to avoid escapes. Write trap and grid number on bag with permanent marker to ensure animal can be relased at point of capture after processing. Store the animals in large calico bag.</para>
 <para>•	Once all traps are checked, animals are processed on site and released at point of capture.</para>
 <para>•	At the end of the trapping survey (on the third day), place metal lids firmly on pitfall trap and ensure lid sits tight. Cover lid with a bit of sand to reduce exposure to sunlight and curious animals</para>
 </section>
 </description>
 <instrumentation>Pitfall traps capped with metal lids, fence droppers marking each trap</instrumentation>
 <instrumentation>PVC stormwater pipe, 160 mm in diameter and 600 mm deep drift fence of aluminium wire mesh (flyscreen) 30 cm x 2.5 m</instrumentation>
 </methodStep>
 <methodStep><description><section><title>Data collection</title>
 <para>Date, site and grid number were recorded for all captures, and captured animals were also marked with unique ID numbers allowing identification of recaptured animals.</para>
 </section>
 </description>
 </methodStep>
 <sampling><studyExtent><description><para>The network program uses a core of 12 sites which are spaced at least 15 km apart, each comprising two 1-ha trapping grids, or plots which are spaced between 0.5-2 km apart. Thirty-six traps were arrayed in a grid covering 1 ha; each grid comprised 6 lines of 6 traps spaced 20 m apart. The top line of traps extended along the dune crest where consecutive numbering starts, and finished along the sixth line 100 m distant in the dune valley or ‘swale’. Traps on each grid were opened for 3 nights once per year and checked in the mornings and sometimes afternoons.

The nomenclature for the species listed does not always represent the most recent taxonomic classification. This is to ensure that names are consistent over time across all faunal Desert Research Ecology data packages. A more recent nomenclature for some of these species can be seen below.
Egernia inornata — Liopholis inornata
Eremiascincus fasciolatus — Eremiascincus phantasmus
Rhynchoedura ornata — Rhynchoedura eyrensis</para>
 </description>
 </studyExtent>
 <samplingDescription><para>Other elements of the plot network’s full program share the sampling structure and core sites/plot/grid configuration of the study design.</para>
 </samplingDescription>
 </sampling>
 </methods>
 <project><title>Desert Ecology Plot Network</title>
 <personnel><references>1442282051407</references>
 <role>Data Owner</role>
 </personnel>
 <personnel><references>1442282105473</references>
 <role>Data Owner</role>
 </personnel>
 <personnel><references>1442282128694</references>
 <role>Plot Network Contact</role>
 </personnel>
 <personnel><references>1442282151469</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>
 </project>
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 <attributeList id="95ae4d3f-edb9-4310-998a-a6b7f8fd8dbb"> <attribute id="1414556632514"> <attributeName>year</attributeName>
 <attributeDefinition>Year of survey</attributeDefinition>
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 <attribute id="1414556666022"> <attributeName>monthyear</attributeName>
 <attributeDefinition>Month and year of survey identifier</attributeDefinition>
 <measurementScale> <dateTime> <formatString>Mmm.YY</formatString>
 </dateTime>
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 </attribute>
 <attribute id="1414375896641"> <attributeName>tripno</attributeName>
 <attributeDefinition>Arbitary trip identifer</attributeDefinition>
 <measurementScale> <nominal> <nonNumericDomain> <textDomain> <definition>Character</definition>
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 <attribute id="1414556702151"> <attributeName>sitename</attributeName>
 <attributeDefinition>Name of site</attributeDefinition>
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 <attribute id="1414556893892"> <attributeName>sitegrid</attributeName>
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 <attribute id="1414556967846"> <attributeName>total_trap_nights</attributeName>
 <attributeDefinition>Number of nights grids were opened x number of traps</attributeDefinition>
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 <attribute id="1414556986050"> <attributeName>fauna_descriptor</attributeName>
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 <attribute id="1414557066022"> <attributeName>recap_this_trip</attributeName>
 <attributeDefinition>Recaptures for the current trip. Blank means new animal i.e. not a recapature on the same sampling period as recaptures of the same individual have been removed</attributeDefinition>
 <measurementScale> <interval> <unit> <standardUnit>number</standardUnit>
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 <attribute id="1414557087760"> <attributeName>captures</attributeName>
 <attributeDefinition>Total captures over 3 nights of trapping</attributeDefinition>
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 <attribute id="1414557115139"> <attributeName>captures_100tn</attributeName>
 <attributeDefinition>Captures standardised for unequal trapping effort (captures/100 trap nights = captures/(number pitfalls (usually 36)*nights opened (usually 3))*100)</attributeDefinition>
 <measurementScale> <interval> <unit> <standardUnit>number</standardUnit>
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 <numericDomain> <numberType>whole</numberType>
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 <attribute id="1414557164374"> <attributeName>family</attributeName>
 <attributeDefinition>Reptile family name</attributeDefinition>
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