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            <gco:CharacterString>Cite this dataset as: Hirsh, H., Nickols, K. J., Takeshita, Y., Traiger, S., Monismith, S. G., Mucciarone, D., Dunbar, R. B. (2020) Kelp forest mooring DIC, TA, pCO2, and aragonite saturation state estimations inside the kelp canopy (36° 37.297’ N, 121° 54.102’ W.) at Hopkins Marine Station, recorded between June and October 2018. Biological and Chemical Oceanography Data Management Office (BCO-DMO). (Version 1) Version Date 2020-09-02 [if applicable, indicate subset used]. doi:10.26008/1912/bco-dmo.823008.1 [access date]</gco:CharacterString>
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        <gco:CharacterString>Dataset Description: &amp;lt;p&amp;gt;These data are published in Hirsh &amp;lt;em&amp;gt;et al., &amp;lt;/em&amp;gt;see related publications section.&amp;lt;/p&amp;gt; Methods and Sampling: &amp;lt;p&amp;gt;In order to estimate other carbonate parameters from sensor pH data, we require an additional carbonate parameter. To accomplish this, we created a local empirical relationship to estimate total alkalinity (TA) based on discrete samples, and combined this with sensor data to calculate DIC, pCO2, and aragonite saturation state (ΩAr).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;TA was estimated using a multiple linear regression (MLR) approach, with temperature (T) and salinity (S) as inputs (Alin et al., 2012; Carter et al., 2018). This approach has been demonstrated to be effective in the open ocean (Carter et al., 2018) and along the California Coast below 50 m depth (Alin et al., 2012). Takeshita et al. (2015) demonstrated that this MLR approach can be extended to nearshore environments and showed TA could be estimated to ± 6 μmol kg-1 (RMSE) inside a kelp forest in Southern California by applying an offset to the equations from Alin et al. (2012).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Here, we fit an equation of the form used in Alin et al. (2012) to the discrete samples (n = 271) collected in the kelp forest, and obtained the following equation:&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;TA &amp;lt;sup&amp;gt;est &amp;lt;/sup&amp;gt;= alpha&amp;lt;sub&amp;gt;0&amp;lt;/sub&amp;gt; + alpha&amp;lt;sub&amp;gt;1&amp;lt;/sub&amp;gt; (T - T&amp;lt;sub&amp;gt;r&amp;lt;/sub&amp;gt;) + alpha&amp;lt;sub&amp;gt;2&amp;lt;/sub&amp;gt; (S - S&amp;lt;sub&amp;gt;r&amp;lt;/sub&amp;gt;) + alpha&amp;lt;sub&amp;gt;3&amp;lt;/sub&amp;gt; (T-T&amp;lt;sub&amp;gt;r&amp;lt;/sub&amp;gt;) x (S - S&amp;lt;sub&amp;gt;r&amp;lt;/sub&amp;gt;)&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;with a RMSE of ± 7.3 μmol kg-1. T&amp;lt;sub&amp;gt;r&amp;lt;/sub&amp;gt; and S&amp;lt;sub&amp;gt;r&amp;lt;/sub&amp;gt; are the mean temperature and salinity for the deployment. The estimated total alkalinity (TA&amp;lt;sub&amp;gt;est&amp;lt;/sub&amp;gt;) was combined with sensor pH to estimate DIC, pCO2, and ΩAr using equilibrium constants from Lueker et al. (2000) and CO2SYS (van Heuven et al., 2011). For a range of pH from 7.56 to 8.30 the standard uncertainty for estimated carbonate system parameters was 8.98 to 13.43 μmol kg-1 DIC, 54.22 to 9.42 μatm pCO2, and 0.0501 to 0.223 ΩAr. These uncertainties were calculated using the ‘errors’ function in seacarb (Gattuso et al., 2020, version 3.2.13 - Accessed 6 Mar 2020) with inputs of TAest and measured pH, temperature and salinity over depth inside the kelp forest.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;amp;nbsp;&amp;lt;/p&amp;gt;</gco:CharacterString>
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        <gmx:Anchor xlink:href="http://lod.bco-dmo.org/id/award/748777.rdf" xlink:title="OCE-1737096" xlink:actuate="onRequest">Funding provided by NSF Division of Ocean Sciences (NSF OCE) Award Number: OCE-1737096 Award URL: https://www.nsf.gov/awardsearch/show-award?AWD_ID=1737096</gmx:Anchor>
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        <gmx:Anchor xlink:href="http://lod.bco-dmo.org/id/award/748781.rdf" xlink:title="OCE-1737176" xlink:actuate="onRequest">Funding provided by NSF Division of Ocean Sciences (NSF OCE) Award Number: OCE-1737176 Award URL: https://www.nsf.gov/awardsearch/show-award?AWD_ID=1737176</gmx:Anchor>
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Kelp forest ecosystems are of ecological and economic importance globally and provide habitat for a diversity of fish, invertebrates, and other algal species. In addition, they may also modify the chemistry of surrounding waters. Uptake of carbon dioxide (CO2) by giant kelp, Macrocystis pyrifera, may play a role in ameliorating the effects of increasing ocean acidity on nearshore marine communities driven by rising atmospheric CO2. Predicting the capacity for kelp forests to alter seawater chemistry requires understanding of the oceanographic and biological mechanisms that drive variability in seawater chemistry. The project will identify specific conditions that could lead to decreases in seawater CO2 by studying 4 sites within the southern Monterey Bay in Central California. An interdisciplinary team will examine variations in ocean chemistry in the context of the oceanographic and ecological characteristics of kelp forest habitats. This project will support an early career researcher, as well as train and support a postdoctoral researcher, PhD student, thesis master's student, and up to six undergraduate students. The PIs will actively recruit students from underrepresented groups to participate in this project through Stanford University's Summer Research in Geosciences and Engineering (SURGE) program and the Society for Advancement of Hispanics/Chicanos and Native Americans in Science (SACNAS). In addition, the PIs and students will actively engage with the management community (Monterey Bay National Marine Sanctuary and California Department of Fish and Wildlife) to advance products based on project data that will assist the development of management strategies for kelp forest habitats in a changing ocean.&lt;/p&gt;
&lt;p&gt;This project builds upon an extensive preliminary data set and will link kelp forest community attributes and hydrodynamic properties to kelp forest biogeochemistry (including the carbon system and dissolved oxygen) to understand mechanistically how giant kelp modifies surrounding waters and affects water chemistry using unique high-resolution measurement capabilities that have provided important insights in coral reef biogeochemistry. The project sites are characterized by different oceanographic settings and kelp forest characteristics that will allow examination of relationships between kelp forest inhabitants and water column chemistry. Continuous measurements of water column velocity, temperature, dissolved oxygen, pH, and photosynthetically active radiation will be augmented by twice-weekly measurements of dissolved inorganic carbon, total alkalinity, and nutrients as well as periods of high frequency sampling of all carbonate system parameters. Quantifying vertical gradients in carbonate system chemistry within kelp forests will lead to understanding of its dependence on seawater residence time and water column stratification. Additional biological sampling of kelp, benthic communities, and phytoplankton will be used to 1) determine contributions of understory algae and calcifying species to bottom water chemistry, 2) determine contributions of kelp canopy growth and phytoplankton to surface water chemistry, and 3) quantify the spatial extent of surface chemistry alteration by kelp forests. The physical, biological, and chemical data collected across multiple forests will allow development of a statistical model for predictions of kelp forest carbonate system chemistry alteration in different locations and under future climate scenarios. Threshold values of oceanographic conditions and kelp forest characteristics that lead to alteration of water column chemistry will be identified for use by managers in mitigation strategies such as targeted protection or restoration.&lt;/p&gt;</gco:CharacterString>
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                <gco:CharacterString>&amp;lt;p&amp;gt;In order to estimate other carbonate parameters from sensor pH data, we require an additional carbonate parameter. To accomplish this, we created a local empirical relationship to estimate total alkalinity (TA) based on discrete samples, and combined this with sensor data to calculate DIC, pCO2, and aragonite saturation state (ΩAr).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;TA was estimated using a multiple linear regression (MLR) approach, with temperature (T) and salinity (S) as inputs (Alin et al., 2012; Carter et al., 2018). This approach has been demonstrated to be effective in the open ocean (Carter et al., 2018) and along the California Coast below 50 m depth (Alin et al., 2012). Takeshita et al. (2015) demonstrated that this MLR approach can be extended to nearshore environments and showed TA could be estimated to ± 6 μmol kg-1 (RMSE) inside a kelp forest in Southern California by applying an offset to the equations from Alin et al. (2012).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Here, we fit an equation of the form used in Alin et al. (2012) to the discrete samples (n = 271) collected in the kelp forest, and obtained the following equation:&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;TA &amp;lt;sup&amp;gt;est &amp;lt;/sup&amp;gt;= alpha&amp;lt;sub&amp;gt;0&amp;lt;/sub&amp;gt; + alpha&amp;lt;sub&amp;gt;1&amp;lt;/sub&amp;gt; (T - T&amp;lt;sub&amp;gt;r&amp;lt;/sub&amp;gt;) + alpha&amp;lt;sub&amp;gt;2&amp;lt;/sub&amp;gt; (S - S&amp;lt;sub&amp;gt;r&amp;lt;/sub&amp;gt;) + alpha&amp;lt;sub&amp;gt;3&amp;lt;/sub&amp;gt; (T-T&amp;lt;sub&amp;gt;r&amp;lt;/sub&amp;gt;) x (S - S&amp;lt;sub&amp;gt;r&amp;lt;/sub&amp;gt;)&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;with a RMSE of ± 7.3 μmol kg-1. T&amp;lt;sub&amp;gt;r&amp;lt;/sub&amp;gt; and S&amp;lt;sub&amp;gt;r&amp;lt;/sub&amp;gt; are the mean temperature and salinity for the deployment. The estimated total alkalinity (TA&amp;lt;sub&amp;gt;est&amp;lt;/sub&amp;gt;) was combined with sensor pH to estimate DIC, pCO2, and ΩAr using equilibrium constants from Lueker et al. (2000) and CO2SYS (van Heuven et al., 2011). For a range of pH from 7.56 to 8.30 the standard uncertainty for estimated carbonate system parameters was 8.98 to 13.43 μmol kg-1 DIC, 54.22 to 9.42 μatm pCO2, and 0.0501 to 0.223 ΩAr. These uncertainties were calculated using the ‘errors’ function in seacarb (Gattuso et al., 2020, version 3.2.13 - Accessed 6 Mar 2020) with inputs of TAest and measured pH, temperature and salinity over depth inside the kelp forest.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;amp;nbsp;&amp;lt;/p&amp;gt;</gco:CharacterString>
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&amp;lt;p&amp;gt;BCO-DMO processing notes:&amp;lt;/p&amp;gt;

&amp;lt;ul&amp;gt;
&amp;lt;li&amp;gt;Adjusted column headers to comply with database requirements&amp;lt;/li&amp;gt;
&amp;lt;li&amp;gt;Converted Timestamp to ISO format&amp;lt;/li&amp;gt;
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				    <gco:CharacterString>MA</gco:CharacterString>
				  </gmd:administrativeArea>
				  <gmd:postalCode>
				    <gco:CharacterString>02543</gco:CharacterString>
				  </gmd:postalCode>
				  <gmd:country>
				    <gco:CharacterString>USA</gco:CharacterString>
				  </gmd:country>
				  <gmd:electronicMailAddress>
				    <gco:CharacterString>info@bco-dmo.org</gco:CharacterString>
				  </gmd:electronicMailAddress>
		    </gmd:CI_Address>
		  </gmd:address>
      <gmd:onlineResource>
          <gmd:CI_OnlineResource>
            <gmd:linkage>
              <gmd:URL>http://www.bco-dmo.org</gmd:URL>
            </gmd:linkage>
          </gmd:CI_OnlineResource>
        </gmd:onlineResource>
		  <gmd:hoursOfService>
        <gco:CharacterString>Monday - Friday 8:00am - 5:00pm</gco:CharacterString>
      </gmd:hoursOfService>
		  <gmd:contactInstructions>
		    <gco:CharacterString>For questions regarding this resource, please contact BCO-DMO via the email address provided.</gco:CharacterString>
		  </gmd:contactInstructions>
		</gmd:CI_Contact>
  </gmd:contactInfo>
  <gmd:role>
    <gmd:CI_RoleCode codeList="http://www.isotc211.org/2005/resources/Codelist/gmxCodelists.xml#CI_RoleCode" codeListValue="pointOfContact"  codeSpace="007">pointOfContact</gmd:CI_RoleCode>
  </gmd:role>
</gmd:CI_ResponsibleParty>
      </gmd:contact>
    </gmd:MD_MaintenanceInformation>
  </gmd:metadataMaintenance>
  <gmi:acquisitionInformation>
    <gmi:MI_AcquisitionInformation>
    <gmi:instrument>
        <gmi:MI_Instrument>
          <gmi:identifier>
            <gmd:MD_Identifier>
              <gmd:code>
                <gmx:Anchor xlink:href="http://lod.bco-dmo.org/id/instrument/674.rdf" xlink:title="pH Sensor" xlink:actuate="onRequest">mFET and SeapHOx</gmx:Anchor>
              </gmd:code>
            </gmd:MD_Identifier>
          </gmi:identifier>
          <gmi:type>
            <gco:CharacterString>mFET and SeapHOx</gco:CharacterString>
          </gmi:type>
          <gmi:description>
            <gco:CharacterString>PI Supplied Instrument Name: mFET and SeapHOx PI Supplied Instrument Description:pH was directly measured (via mFET and SeapHOx) on the mooring at 6 depths (and estimated for 2 weeks at the surface based on the near-surface pH-O2 relationship). Please see metadata for kelp mooring data for additional pH details (https://www.bco-dmo.org/dataset/822549). Instrument Name: pH Sensor Instrument Short Name:pH Sensor   Instrument Description: An instrument that measures the hydrogen ion activity in solutions.

The overall concentration of hydrogen ions is inversely related to its pH.  The pH scale ranges from 0 to 14 and indicates whether acidic (more H+) or basic (less H+). </gco:CharacterString>
          </gmi:description>
        </gmi:MI_Instrument>
      </gmi:instrument>
      </gmi:MI_AcquisitionInformation>
  </gmi:acquisitionInformation>
</gmi:MI_Metadata>
