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            <gco:CharacterString>Cite this dataset as: Bell, L. E., Kroeker, K. J. (2021) Environmental data from experimental aquaria during a laboratory experiment testing the effects of pH, light availability and biotic interaction on coralline algae calcification and productivity at the Sitka Sound Science Center in 2017. Biological and Chemical Oceanography Data Management Office (BCO-DMO). (Version 1) Version Date 2021-07-30 [if applicable, indicate subset used]. doi:10.26008/1912/bco-dmo.856902.1 [access date]</gco:CharacterString>
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        <gco:CharacterString>Environmental data from experimental aquaria (“tanks”) during a laboratory experiment testing the effects of pH, light availability and biotic interaction on coralline algae calcification and productivity. Dataset Description: &amp;lt;p&amp;gt;Environmental data from experimental aquaria (“tanks”) during a laboratory experiment testing the effects of pH, light availability and biotic interaction on coralline algae calcification and productivity.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;amp;nbsp;&amp;lt;/p&amp;gt; Methods and Sampling: &amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Methodology:&amp;amp;nbsp;&amp;lt;/strong&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Sampling and analytical procedures: &amp;lt;/strong&amp;gt;To test the response of the coralline algae Crusticorallina spp. and Bossiella orbigniana to future OA scenarios, we used an 18-aquaria indoor experimental system with flow-through seawater at the Sitka Sound Science Center to simulate three static pH&amp;lt;sub&amp;gt;T&amp;lt;/sub&amp;gt; levels (current summer = 8.0, future summer/current winter = 7.7, future winter = 7.4) under two seasonal light regimes simulated with full-spectrum aquarium lights (AI Prime HD) (summer = PPFD 55μmol m&amp;lt;sup&amp;gt;-2&amp;lt;/sup&amp;gt; s&amp;lt;sup&amp;gt;-1&amp;lt;/sup&amp;gt;, 13h d&amp;lt;sup&amp;gt;-1&amp;lt;/sup&amp;gt;, winter = PPFD 40μmol m&amp;lt;sup&amp;gt;-2&amp;lt;/sup&amp;gt; s&amp;lt;sup&amp;gt;-1&amp;lt;/sup&amp;gt;, 6h d&amp;lt;sup&amp;gt;-1&amp;lt;/sup&amp;gt;). We had a total of 3 aquaria for each of the 6 treatment combinations. A full description of the pH control for this system can be found in Kroeker et al. 2021, but in short: pH was regulated using a relay system that controlled mixing of pre-equilibrated low-pH seawater (formed by bubbling pure CO&amp;lt;sub&amp;gt;2 &amp;lt;/sub&amp;gt;gas into seawater: pH6.0) and ambient pH seawater into 9 header buckets (n=3 headers per pH treatment) that then flowed into the experimental aquaria. Each header bucket was equipped with a pH sensor (DuraFET, Honeywell) communicating with a controller (UDA 2152, Honeywell) to regulate flow of the low pH water through solenoid valves to maintain pre-programmed pH setpoints. Experimental pH levels were chosen to reflect current seasonal minimums of coastal pH measured at Harris Is. (57.032N, 135.277W) from 2016-2017, as well as end-of-century projections for Gulf of Alaska pH levels based on RCP 8.5 (-0.3 pH&amp;lt;sub&amp;gt;T&amp;lt;/sub&amp;gt; from current levels). Experimental light regimes were defined using seasonal averages for day length and measured irradiance level at 10m depth at Harris Is.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Within each pH level and light treatment combination, half of the individual Crusticorallina spp. and B. orbigniana were randomly assigned to be paired in close proximity with the fleshy red alga Cryptopleura ruprechtiana (n=6 species treatment&amp;lt;sup&amp;gt;-1&amp;lt;/sup&amp;gt;). All algal individuals were collected on Aug 5, 2017 at Harris Is. Total experimental duration was 45d (Aug 7-Sept 21, 2017). To monitor treatment conditions, we used a handheld meter (YSI) to take daily temperature readings in the replicate aquaria and measure salinity of incoming seawater daily just upstream of our experimental system. Additionally, discrete water samples were collected from replicate aquaria at four timepoints (Aug 18, 22, 25, and Sept 15) for determination of pH (total scale) and total alkalinity (TA). Discrete samples were collected without aeration in amber glass bottles, immediately poisoned with saturated HgCl&amp;lt;sub&amp;gt;2&amp;lt;/sub&amp;gt; (0.025% volume&amp;lt;sup&amp;gt;-1&amp;lt;/sup&amp;gt;), and capped to prevent air exchange.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Discrete water samples for laboratory measurements of pH and/or TA were transported to UCSC for analysis within 8 months of collection. We measured pH spectrophotometrically (Shimadzu, UV-1800) using m-cresol purple dye following best practices (Dickson et al. 2017), with an average standard error of ± 0.0013 pH units among sample triplicates. TA measurements were performed using open cell titration (Metrohm, 905 Titrandro) and corrected against certified reference materials of CO&amp;lt;sub&amp;gt;2&amp;lt;/sub&amp;gt; in seawater (Dickson laboratory, Scripps Institution of Oceanography), with an average standard error of ±0.933μmol kg&amp;lt;sup&amp;gt;-1&amp;lt;/sup&amp;gt; SW&amp;lt;sup&amp;gt;-1&amp;lt;/sup&amp;gt; among sample triplicates. To calculate pH&amp;lt;sub&amp;gt;T&amp;lt;/sub&amp;gt; in the replicate aquaria at the time of water sampling, we used our measurements of spectrophotometric pH, TA, temperature, and salinity, as well as the dissociation constants as inputs to the program CO2SYS. This dataset reflects all of the above-described data, including final carbonate chemistry calculations from CO2SYS.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Problem report: &amp;lt;/strong&amp;gt;&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Discrete water samples had to be stored and shipped from Southeast Alaska to Santa Cruz, CA for analysis, and some samples were broken in transit and unusable. Additionally, we recognize that the delay between collection and laboratory analysis of water sample spec pH and TA may have resulted in a measurable amount of drift in these parameters, but we were unable to quantify any drift that may have occurred and thus these values are uncorrected. Lastly, calculated parameters for certain samples did not follow expected relationships (e.g., among spec pH and pCO2) and thus were flagged for potentially poor quality, which may have been caused by biological contamination in bottle samples.&amp;lt;/p&amp;gt;</gco:CharacterString>
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http://lod.bco-dmo.org/id/dataset-parameter/857125.rdf
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http://lod.bco-dmo.org/id/dataset-parameter/857126.rdf
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	Units: parts per thousand (ppt)
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http://lod.bco-dmo.org/id/dataset-parameter/857127.rdf
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http://lod.bco-dmo.org/id/dataset-parameter/857128.rdf
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http://lod.bco-dmo.org/id/dataset-parameter/857129.rdf
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http://lod.bco-dmo.org/id/dataset-parameter/857130.rdf
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http://lod.bco-dmo.org/id/dataset-parameter/857131.rdf
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	Units: µatm
	Description: &lt;p&gt;calculated fugacity of carbon dioxide&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/857132.rdf
	Name: CO2SYS_pCO2
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http://lod.bco-dmo.org/id/dataset-parameter/857133.rdf
	Name: CO2SYS_HCO3
	Units: µmol/kgSW
	Description: &lt;p&gt;calculated bicarbonate concentration&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/857134.rdf
	Name: CO2SYS_CO3
	Units: µmol/kgSW
	Description: &lt;p&gt;calculated carbonate concentration&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/857135.rdf
	Name: CO2SYS_CO2
	Units: µmol/kgSW
	Description: &lt;p&gt;calculated carbon diozide concentration&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/857136.rdf
	Name: CO2SYS_B
	Units: µmol/kgSW
	Description: &lt;p&gt;calculated boron concentration&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/857137.rdf
	Name: CO2SYS_OH
	Units: µmol/kgSW
	Description: &lt;p&gt;calculated hydroxide concentration&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/857138.rdf
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	Units: unitless
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                <gco:CharacterString>&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Methodology:&amp;amp;nbsp;&amp;lt;/strong&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Sampling and analytical procedures: &amp;lt;/strong&amp;gt;To test the response of the coralline algae Crusticorallina spp. and Bossiella orbigniana to future OA scenarios, we used an 18-aquaria indoor experimental system with flow-through seawater at the Sitka Sound Science Center to simulate three static pH&amp;lt;sub&amp;gt;T&amp;lt;/sub&amp;gt; levels (current summer = 8.0, future summer/current winter = 7.7, future winter = 7.4) under two seasonal light regimes simulated with full-spectrum aquarium lights (AI Prime HD) (summer = PPFD 55μmol m&amp;lt;sup&amp;gt;-2&amp;lt;/sup&amp;gt; s&amp;lt;sup&amp;gt;-1&amp;lt;/sup&amp;gt;, 13h d&amp;lt;sup&amp;gt;-1&amp;lt;/sup&amp;gt;, winter = PPFD 40μmol m&amp;lt;sup&amp;gt;-2&amp;lt;/sup&amp;gt; s&amp;lt;sup&amp;gt;-1&amp;lt;/sup&amp;gt;, 6h d&amp;lt;sup&amp;gt;-1&amp;lt;/sup&amp;gt;). We had a total of 3 aquaria for each of the 6 treatment combinations. A full description of the pH control for this system can be found in Kroeker et al. 2021, but in short: pH was regulated using a relay system that controlled mixing of pre-equilibrated low-pH seawater (formed by bubbling pure CO&amp;lt;sub&amp;gt;2 &amp;lt;/sub&amp;gt;gas into seawater: pH6.0) and ambient pH seawater into 9 header buckets (n=3 headers per pH treatment) that then flowed into the experimental aquaria. Each header bucket was equipped with a pH sensor (DuraFET, Honeywell) communicating with a controller (UDA 2152, Honeywell) to regulate flow of the low pH water through solenoid valves to maintain pre-programmed pH setpoints. Experimental pH levels were chosen to reflect current seasonal minimums of coastal pH measured at Harris Is. (57.032N, 135.277W) from 2016-2017, as well as end-of-century projections for Gulf of Alaska pH levels based on RCP 8.5 (-0.3 pH&amp;lt;sub&amp;gt;T&amp;lt;/sub&amp;gt; from current levels). Experimental light regimes were defined using seasonal averages for day length and measured irradiance level at 10m depth at Harris Is.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Within each pH level and light treatment combination, half of the individual Crusticorallina spp. and B. orbigniana were randomly assigned to be paired in close proximity with the fleshy red alga Cryptopleura ruprechtiana (n=6 species treatment&amp;lt;sup&amp;gt;-1&amp;lt;/sup&amp;gt;). All algal individuals were collected on Aug 5, 2017 at Harris Is. Total experimental duration was 45d (Aug 7-Sept 21, 2017). To monitor treatment conditions, we used a handheld meter (YSI) to take daily temperature readings in the replicate aquaria and measure salinity of incoming seawater daily just upstream of our experimental system. Additionally, discrete water samples were collected from replicate aquaria at four timepoints (Aug 18, 22, 25, and Sept 15) for determination of pH (total scale) and total alkalinity (TA). Discrete samples were collected without aeration in amber glass bottles, immediately poisoned with saturated HgCl&amp;lt;sub&amp;gt;2&amp;lt;/sub&amp;gt; (0.025% volume&amp;lt;sup&amp;gt;-1&amp;lt;/sup&amp;gt;), and capped to prevent air exchange.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Discrete water samples for laboratory measurements of pH and/or TA were transported to UCSC for analysis within 8 months of collection. We measured pH spectrophotometrically (Shimadzu, UV-1800) using m-cresol purple dye following best practices (Dickson et al. 2017), with an average standard error of ± 0.0013 pH units among sample triplicates. TA measurements were performed using open cell titration (Metrohm, 905 Titrandro) and corrected against certified reference materials of CO&amp;lt;sub&amp;gt;2&amp;lt;/sub&amp;gt; in seawater (Dickson laboratory, Scripps Institution of Oceanography), with an average standard error of ±0.933μmol kg&amp;lt;sup&amp;gt;-1&amp;lt;/sup&amp;gt; SW&amp;lt;sup&amp;gt;-1&amp;lt;/sup&amp;gt; among sample triplicates. To calculate pH&amp;lt;sub&amp;gt;T&amp;lt;/sub&amp;gt; in the replicate aquaria at the time of water sampling, we used our measurements of spectrophotometric pH, TA, temperature, and salinity, as well as the dissociation constants as inputs to the program CO2SYS. This dataset reflects all of the above-described data, including final carbonate chemistry calculations from CO2SYS.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Problem report: &amp;lt;/strong&amp;gt;&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Discrete water samples had to be stored and shipped from Southeast Alaska to Santa Cruz, CA for analysis, and some samples were broken in transit and unusable. Additionally, we recognize that the delay between collection and laboratory analysis of water sample spec pH and TA may have resulted in a measurable amount of drift in these parameters, but we were unable to quantify any drift that may have occurred and thus these values are uncorrected. Lastly, calculated parameters for certain samples did not follow expected relationships (e.g., among spec pH and pCO2) and thus were flagged for potentially poor quality, which may have been caused by biological contamination in bottle samples.&amp;lt;/p&amp;gt;</gco:CharacterString>
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&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;BCO-DMO processing notes:&amp;lt;/strong&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Renamed field tank.rep to tank_rep in order to meet BCO-DMO field naming conventions&amp;lt;/p&amp;gt;

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            <gco:CharacterString>PI Supplied Instrument Name: YSI handheld meter PI Supplied Instrument Description:To monitor treatment conditions, we used a handheld meter (YSI) to take daily temperature readings in the replicate aquaria and measure salinity of incoming seawater daily just upstream of our experimental system. YSI handheld meter used to measure dissolved oxygen, pH, salinity, and temperature. Instrument Name: Discrete water sampler Instrument Short Name:   Instrument Description: A device that collects an in-situ discrete water sample from any depth and returns it to the surface without contamination by the waters through which it passes, such as a water bottle.</gco:CharacterString>
          </gmi:description>
        </gmi:MI_Instrument>
      </gmi:instrument>
      <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">Honeywell DuraFET and UDA 2152</gmx:Anchor>
              </gmd:code>
            </gmd:MD_Identifier>
          </gmi:identifier>
          <gmi:type>
            <gco:CharacterString>Honeywell DuraFET and UDA 2152</gco:CharacterString>
          </gmi:type>
          <gmi:description>
            <gco:CharacterString>PI Supplied Instrument Name: Honeywell DuraFET and UDA 2152 PI Supplied Instrument Description:Each header bucket was equipped with a pH sensor (DuraFET, Honeywell) communicating with a controller (UDA 2152, Honeywell) to regulate flow of the low pH water through solenoid valves to maintain pre-programmed pH setpoints. 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:instrument>
        <gmi:MI_Instrument>
          <gmi:identifier>
            <gmd:MD_Identifier>
              <gmd:code>
                <gmx:Anchor xlink:href="http://lod.bco-dmo.org/id/instrument/682.rdf" xlink:title="Titrator" xlink:actuate="onRequest">Metrohm 905 Titrandro Titrator</gmx:Anchor>
              </gmd:code>
            </gmd:MD_Identifier>
          </gmi:identifier>
          <gmi:type>
            <gco:CharacterString>Metrohm 905 Titrandro Titrator</gco:CharacterString>
          </gmi:type>
          <gmi:description>
            <gco:CharacterString>PI Supplied Instrument Name: Metrohm 905 Titrandro Titrator PI Supplied Instrument Description:Total alkalinity (TA )measurements were performed using open cell titration and corrected against certified reference materials of CO2 in seawater (Dickson laboratory, Scripps Institution of Oceanography), with an average standard error of ±0.933μmol kg-1 SW-1 among sample triplicates. Instrument Name: Titrator Instrument Short Name:Titrator   Instrument Description: Titrators are instruments that incrementally add quantified aliquots of a reagent to a sample until the end-point of a chemical reaction is reached. Community Standard Description: http://vocab.nerc.ac.uk/collection/L05/current/LAB12/</gco:CharacterString>
          </gmi:description>
        </gmi:MI_Instrument>
      </gmi:instrument>
      <gmi:instrument>
        <gmi:MI_Instrument>
          <gmi:identifier>
            <gmd:MD_Identifier>
              <gmd:code>
                <gmx:Anchor xlink:href="http://lod.bco-dmo.org/id/instrument/595.rdf" xlink:title="UV Spectrophotometer-Shimadzu" xlink:actuate="onRequest">Shimadzu UV-1800 spectrophotometer</gmx:Anchor>
              </gmd:code>
            </gmd:MD_Identifier>
          </gmi:identifier>
          <gmi:type>
            <gco:CharacterString>Shimadzu UV-1800 spectrophotometer</gco:CharacterString>
          </gmi:type>
          <gmi:description>
            <gco:CharacterString>PI Supplied Instrument Name: Shimadzu UV-1800 spectrophotometer PI Supplied Instrument Description:We measured pH spectrophotometrically (Shimadzu, UV-1800) using m-cresol purple dye following best practices (Dickson et al. 2017), with an average standard error of ± 0.0013 pH units among sample triplicates. Instrument Name: UV Spectrophotometer-Shimadzu Instrument Short Name:UV Spectrophotometer-Shimadzu   Instrument Description: The Shimadzu UV Spectrophotometer is manufactured by Shimadzu Scientific Instruments (ssi.shimadzu.com). Shimadzu manufacturers several models of spectrophotometer; refer to dataset for make/model information. Community Standard Description: http://vocab.nerc.ac.uk/collection/L05/current/LAB20/</gco:CharacterString>
          </gmi:description>
        </gmi:MI_Instrument>
      </gmi:instrument>
      </gmi:MI_AcquisitionInformation>
  </gmi:acquisitionInformation>
</gmi:MI_Metadata>
