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    <shortName>b235_model</shortName>
    <title>Distribution models of microbial mats and mosses across Fryxell Basin, Taylor Valley, Antarctica (2018-2019)</title>
    <creator>
      <individualName>
        <givenName>Schuyler</givenName>
        <surName>Borges</surName>
      </individualName>
      <electronicMailAddress>srb558@nau.edu</electronicMailAddress>
      <userId directory="https://orcid.org">https://orcid.org/0000-0002-4565-6463</userId>
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    <creator>
      <individualName>
        <givenName>Mark</givenName>
        <surName>Salvatore</surName>
      </individualName>
      <electronicMailAddress>mark.salvatore@nau.edu</electronicMailAddress>
      <onlineUrl>http://msalvatore.net</onlineUrl>
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    <creator>
      <individualName>
        <givenName>Lee</givenName>
        <surName>Stanish</surName>
      </individualName>
      <electronicMailAddress>lstanish@gmail.com</electronicMailAddress>
      <userId directory="https://orcid.org">https://orcid.org/0000-0002-9775-6861</userId>
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    <creator>
      <individualName>
        <givenName>Sarah</givenName>
        <surName>Power</surName>
      </individualName>
      <electronicMailAddress>snpower@vt.edu</electronicMailAddress>
      <userId directory="https://orcid.org">https://orcid.org/0000-0002-4863-290X</userId>
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    <creator>
      <individualName>
        <givenName>Eric</givenName>
        <surName>Sokol</surName>
      </individualName>
      <electronicMailAddress>sokole@gmail.com</electronicMailAddress>
      <onlineUrl>http://sokole.blogspot.com/</onlineUrl>
      <userId directory="https://orcid.org">https://orcid.org/0000-0001-5952-0917</userId>
    </creator>
    <creator>
      <individualName>
        <givenName>John "Jeb"</givenName>
        <surName>Barrett</surName>
      </individualName>
      <electronicMailAddress>jebarre@vt.edu</electronicMailAddress>
      <onlineUrl>https://www.biol.vt.edu/faculty/barrett/index.html</onlineUrl>
      <userId directory="https://orcid.org">https://orcid.org/0000-0002-7610-0505</userId>
    </creator>
    <creator>
      <individualName>
        <givenName>Christian</givenName>
        <surName>Tai Udovicic</surName>
      </individualName>
      <electronicMailAddress>cjtu@nau.edu</electronicMailAddress>
      <userId directory="https://orcid.org">https://orcid.org/0000-0001-9972-1534</userId>
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    <metadataProvider>
      <organizationName>McMurdo Dry Valleys LTER</organizationName>
      <onlineUrl>http://mcmlter.org/</onlineUrl>
    </metadataProvider>
    <associatedParty>
      <individualName>
        <givenName>Renée</givenName>
        <surName>Brown</surName>
      </individualName>
      <electronicMailAddress>rfbrown@unm.edu</electronicMailAddress>
      <userId directory="https://orcid.org">https://orcid.org/0000-0002-4986-7663</userId>
      <role>data manager</role>
    </associatedParty>
    <pubDate>2023-09-28</pubDate>
    <language>English</language>
    <abstract>
      <section>
        <para>
          <literalLayout>Long-term ecological field surveys from the McMurdo Dry Valleys Long Term Ecological Research program (MCM LTER) have documented the abundance and diversity of microbial mat types across ephemeral glacial meltwater streams in the McMurdo Dry Valleys region of Antarctica. However, field surveys are limited and are incapable of being performed across the entirety of streams within a field season. Therefore, we used remote sensing to examine the distribution of these diverse communities across streams in order to determine whether large scale distribution patterns are similar to those the MCM LTER has already thoroughly studied in situ. As part of our 2018-2019 field campaign, we established two to three 20 x 20 m plots within five different streams (Bowles Creek, McKnight Creek, a relict channel, Canada Stream, and Crescent Stream) in the Fryxell Basin of Taylor Valley. We performed point transect and quadrat field surveys of microbial mat and moss cover within each 20 x 20 m plot. We then used hyperspectral measurements of mat and moss collected in the field, previously archived in “Spectral and biological characteristics of microbial mats and mosses across Fryxell Basin, Taylor Valley, Antarctica (2018-2019),” in linear spectral mixing models to determine mat and moss coverage in the same 20 x 20 m plots within an atmospherically corrected WorldView-2 satellite image from Dec. 12, 2018. We ground truthed our modeled mat and moss abundances with our field survey coverages and determined the limitations of our methods. We then modeled mat and moss coverage across Huey Creek and Von Guerard Stream to apply our methods to streams without ground truthing measurements. Our results demonstrate the spatial distribution of moss and black, orange, red, and green microbial mat across Fryxell Basin streams. Observations of mat and moss coverage at the basin-wide scale are similar to those seen in localized stream areas.</literalLayout>
        </para>
      </section>
    </abstract>
    <keywordSet>
      <keyword>communities</keyword>
      <keyword>global positioning systems</keyword>
      <keyword>imagery</keyword>
      <keyword>modeling</keyword>
      <keyword>models</keyword>
      <keyword>mosses</keyword>
      <keyword>physiology</keyword>
      <keyword>reflectance</keyword>
      <keyword>remote sensing</keyword>
      <keyword>stream ecology</keyword>
      <keywordThesaurus>LTER Controlled Vocabulary</keywordThesaurus>
    </keywordSet>
    <keywordSet>
      <keyword>algae</keyword>
      <keyword>Antarctic desert streams</keyword>
      <keyword>Antarctica</keyword>
      <keyword>global positioning system</keyword>
      <keyword>LTER</keyword>
      <keyword>McMurdo Dry Valleys</keyword>
      <keyword>microbial mat</keyword>
      <keyword>Moss</keyword>
      <keyword>Taylor Valley</keyword>
      <keywordThesaurus>Station Keywords</keywordThesaurus>
    </keywordSet>
    <keywordSet>
      <keyword>primary production</keyword>
      <keywordThesaurus>LTER Core Areas</keywordThesaurus>
    </keywordSet>
    <additionalInfo>
      <para>
        <literalLayout>Funding for this work was provided by the National Science Foundation grants #OPP-1758224 and #OPP-1745053 to Mark Salvatore, a Graduate Research Fellowship award to Schuyler Borges, and&#160;#OPP-1637708 and #OPP-2224760 to the MCM LTER for assistance with data management.</literalLayout>
      </para>
    </additionalInfo>
    <intellectualRights>
      <section>
        <title>Data Policies</title>
        <para>
          <literalLayout>This data package is released under the Creative Commons Attribution 4.0 International License (CC BY 4.0; http://creativecommons.org/licenses/by/4.0/), which allows consumers (hereinafter referred to as “Data Users”) to freely reuse, redistribute, transform, or build on this work (even commercially) so long as appropriate credit is provided. Accordingly, Data Users are required to properly cite this data package in any publications or in the metadata of any derived products that result from its use (in whole or in part). A recommended citation is provided on the summary metadata page associated with this data package in the McMurdo Dry Valleys LTER Data Catalog (https://mcmlter.org/data), and a generic citation may be found on the summary metadata page in the repository where this data package was obtained. When these data contribute significantly to the contents of a publication, Data Users must also acknowledge that data were provided by the NSF-supported McMurdo Dry Valleys Long Term Ecological Research program (OPP-2224760). This data package has been released in the spirit of open scientific collaboration. Hence, Data Users are strongly encouraged to consider consultation, collaboration, and/or co-authorship (as appropriate) with the data package creator(s). Data Users should be aware these data may be actively used by others for ongoing research; thus, coordination may be necessary to prevent duplicate publication. Data Users should also recognize that misinterpretation of data may occur if they are used outside the context of the original study. Hence, Data Users are urged to contact the data package creator(s) if they have any questions regarding methodology or results. While substantial efforts are made to ensure the accuracy of this data package (with all its components), complete accuracy cannot be guaranteed. Periodic updates to this data package may occur, and it is the responsibility of Data Users to check for new versions. This data package is made available “as is” and comes with no warranty of accuracy or fitness for use. The creator(s) of this data package and the repository where these data were obtained shall not be liable for any damages resulting from misinterpretation, use, or misuse of these data. Finally, as a professional courtesy, we kindly request Data Users notify the primary contact referenced in the metadata when these data are used in the production of any derivative work or publication. Notification should include an explanation of how the data were used, along with a digital copy of the derived product(s). Thank you.</literalLayout>
        </para>
      </section>
    </intellectualRights>
    <distribution>
      <online>
        <url function="information">https://mcm.lternet.edu/content/distribution-models-microbial-mats-and-mosses-across-fryxell-basin-taylor-valley-antarctica</url>
      </online>
    </distribution>
    <coverage>
      <geographicCoverage>
        <geographicDescription>This is the Taylor Valley, a subjectively approximated contour by San Gil. We use this to denote the geographical extent of studies that encompass the whole Taylor Valley.According to Wiki contributors, the&#160;Taylor Valley&#160;is the southernmost of the three large&#160;Dry Valleys&#160;in the&#160;Transantarctic Mountains,&#160;Victoria Land, located west of&#160;McMurdo Sound. The valley extends from&#160;Taylor Glacier&#160;in the west to&#160;McMurdo Sound&#160;at&#160;Explorers Cove&#160;at the northwest head of&#160;New Harbour&#160;in the east and is about 29 kilometres (18&#160;mi) long. It was once occupied by the receding Taylor Glacier, from which it derives its name. Taylor Valley contains&#160;Lake Bonney&#160;in the west (inward), and&#160;Lake Fryxell&#160;in the east (coastward), and&#160;Lake Hoare,&#160;Lake Chad,&#160;Mummy Pond&#160;and&#160;Parera Pond&#160;close together between the two. Further east of Lake Bonney is&#160;Pearse Valley. Taylor Valley is separated from Wright Valley in the north by&#160;Asgard Range, and from&#160;Ferrar Glacier&#160;in the south by&#160;Kukri Hills.</geographicDescription>
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          <westBoundingCoordinate>161.707763671880</westBoundingCoordinate>
          <eastBoundingCoordinate>163.624877929690</eastBoundingCoordinate>
          <northBoundingCoordinate>-77.519802097166</northBoundingCoordinate>
          <southBoundingCoordinate>-77.808487073526</southBoundingCoordinate>
        </boundingCoordinates>
      </geographicCoverage>
      <temporalCoverage>
        <rangeOfDates>
          <beginDate>
            <calendarDate>2018-12-06</calendarDate>
          </beginDate>
          <endDate>
            <calendarDate>2019-01-25</calendarDate>
          </endDate>
        </rangeOfDates>
      </temporalCoverage>
    </coverage>
    <contact>
      <individualName>
        <givenName>McMurdo Dry Valleys LTER</givenName>
        <surName>Information Manager</surName>
      </individualName>
      <electronicMailAddress>im@mcmlter.org</electronicMailAddress>
    </contact>
    <publisher>
      <organizationName>McMurdo Dry Valleys LTER</organizationName>
      <onlineUrl>http://mcmlter.org/</onlineUrl>
    </publisher>
    <pubPlace>McMurdo Dry Valleys LTER</pubPlace>
    <methods>
      <methodStep>
        <description>
          <section>
            <para>
              <literalLayout>During the 2018-2019 austral summer, field surveys were conducted across 20 x 20 m plots established in several streams across the Fryxell Basin of Taylor Valley, Antarctica. Two plots were established in Bowles Creek, McKnight Creek, and Crescent Stream. Three plots were established in Canada Stream and a relict channel, but only the first and third plot in the relict channel was surveyed because plot 2 was outside the channel. Plots were assigned before the field season based on areas with homogenous NDVI signatures. Field surveys involved point transect and quadrat coverage estimates. Point transect measurements were collected by establishing cardinal (N, E, S, W), and intercardinal (NE, NW, SE, SW) transects across the 20 x 20 m plots. Every 25 cm along all transects, surface types were categorized as “dry” and “exposed” or “inundated” and “black mat, orange mat, red mat, black/orange mat, black/orange/red mat, orange/red mat, moss, cobbles/pebbles, sand, or rock.” Results were then averaged across the 20 x 20 m plots as abundances. For quadrat surveying, 1 x 1 m quadrats were randomly generated in the Esri geographic information system software, ArcGIS, within the 20 x 20 m plots. Ten quadrats per 20 x 20 m plot were established for most stream plots. However, due to field logistics and time constraints, some plots only had 6, 8, or 9 quadrats surveyed. Once in the field, 20 x 20 m general plot overview descriptions were recorded (weather, flow conditions, vegetation coverage, any notable features or changes since previous visit), and then each 1 x 1 m quadrat was surveyed. Observations of mat or moss type (black mat, orange mat, red mat, green mat, sandy orange mat, black/orange mat, black/orange/red mat, black/red mat, orange/red mat, moss, moss with black mat on top, black mat with moss on top, black mat and moss with orange mat on top), coverage, water levels (dry, moist, saturated, inundated), and substrate type were recorded. All coverages were then averaged for each quadrat and applied to the entire 20 x 20 m plot (multiple by two if ten quadrats). Further methodological details can be found in&#160;Spectral and biological characteristics of microbial mats and mosses across Fryxell Basin, Taylor Valley, Antarctica (2018-2019). For our remote sensing techniques, we first atmospherically corrected a WorldView-2 (WV2) image of Fryxell basin taken on Dec. 12, 2018 using the same methods as Salvatore et al. 2021. We then used multispectral data, found in “Spectral and biological characteristics of microbial mats and mosses across Fryxell Basin, Taylor Valley, Antarctica (2018-2019),” as endmember spectra in linear spectral mixing models in the program, Davinci. Model outputs included averaged abundances of mat and moss within each 20 x 20 m plot and the measured and modeled WV2 spectrum of the 20 x 20 m plot. After merging all coverage datasets, averaged abundances of mat and moss within each 20 x 20 m plot were statistically compared with field survey abundances to determine how well our models were fitting measured&#160;in situ&#160;data (R2,&#160;p-value, RMSE, AIC, and reduced chi-squared were calculated from the results). Other modeled results of mat and moss abundances for entire stream channels were outputted as geotiffs, which were then uploaded to the Harris geospatial deep learning software, ENVI, for further analysis. In ENVI, the reassigned WV2 bands displayed the different coverages of moss and each mat type. Using the statistics tool, percent coverages of mat and moss were found for entire stream channels. Percent coverages were converted to areal coverages by dividing the percentages by the total area of the stream channels.&#160;</literalLayout>
            </para>
          </section>
        </description>
      </methodStep>
    </methods>
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          <attributeName>model_id</attributeName>
          <attributeLabel>Model ID</attributeLabel>
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          <attributeLabel>Stream name</attributeLabel>
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          <attributeName>moisture_content</attributeName>
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          <attributeLabel>Stream name</attributeLabel>
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          <attributeLabel>Model ID</attributeLabel>
          <attributeDefinition>Unique model identifier that corresponds with the name of the model and field survey measurements being compared.</attributeDefinition>
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          <measurementScale>
            <nominal>
              <nonNumericDomain>
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          <attributeLabel>Plot ID</attributeLabel>
          <attributeDefinition>Plot identifier within the stream where the field measurement was taken. See methods for further details.</attributeDefinition>
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          <measurementScale>
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          <attributeDefinition>Data type, either field measurement (i.e., point transect or quadrat) or model. See methods for further details.</attributeDefinition>
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        <attribute>
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          <attributeLabel>Regression slope</attributeLabel>
          <attributeDefinition>Regression slope calculated between the modeled and measured abundances of mat and moss.</attributeDefinition>
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                  <definition>Regression slope calculated between the modeled and measured abundances of mat and moss.</definition>
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          <attributeLabel>Regression p-value</attributeLabel>
          <attributeDefinition>Regression p-value calculated between the modeled and measured abundances of mat and moss.</attributeDefinition>
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          <measurementScale>
            <nominal>
              <nonNumericDomain>
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                  <definition>Regression p-value calculated between the modeled and measured abundances of mat and moss.</definition>
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        <attribute>
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          <attributeLabel>Root mean square error</attributeLabel>
          <attributeDefinition>Regression root mean square error (RMSE) calculated between the modeled and measured abundances of mat and moss.</attributeDefinition>
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                  <definition>Regression root mean square error (RMSE) calculated between the modeled and measured abundances of mat and moss.</definition>
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          <attributeDefinition>Akaike Information Criterion (AIC) value calculated between the modeled and measured abundances of mat and moss.</attributeDefinition>
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          <attributeDefinition>Reduced chi-squared value calculated between the modeled and measured abundances of mat and moss.</attributeDefinition>
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                  <definition>Reduced chi-squared value calculated between the modeled and measured abundances of mat and moss.</definition>
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