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            <gmx:Anchor xlink:href="http://lod.bco-dmo.org/id/dataset/856663.rdf" xlink:actuate="onRequest">Wet and buoyant weight measurements of macroalgae at the Sitka Sound Science Center (SSSC) from August to September 2017 (High latitude kelp dynamics project)</gmx:Anchor>
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            <gco:CharacterString>Cite this dataset as: Bell, L. E., Kroeker, K. J. (2021) Wet and buoyant weight measurements of macroalgae at the Sitka Sound Science Center (SSSC) from August to September 2017 (High latitude kelp dynamics project). Biological and Chemical Oceanography Data Management Office (BCO-DMO). (Version 1) Version Date 2021-07-27 [if applicable, indicate subset used]. doi:10.26008/1912/bco-dmo.856663.1 [access date]</gco:CharacterString>
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        <gco:CharacterString>Wet weight and buoyant weight measurements of macroalgae taken at the beginning and end of 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;Wet weight and buoyant weight measurements of macroalgae taken at the beginning and end of a laboratory experiment testing the effects of pH, light availability and biotic interaction on coralline algae calcification and productivity.&amp;lt;/p&amp;gt; Methods and Sampling: &amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Methodology: &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;&amp;lt;/p&amp;gt;

&amp;lt;p&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).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;The effects of each experimental pH and light treatment combination and fleshy red algal association on coralline net calcification rate were assessed using the buoyant weight technique (Jokiel et al. 1978), as well as the alkalinity anomaly technique. To determine total relative change in calcified mass over the experimental period, each coralline algae’s buoyant weight was measured to the nearest 0.0001g at the beginning and end of the experiment on a balanced platform suspended below a microbalance in a temperature-monitored seawater bath. To ensure precision, buoyant weights were repeated for each individual until measurements differed by less than ±0.005g, and then an average was taken of the measurements falling in this range of precision. Initial and final buoyant weights (BW; g) were used to calculate relative net calcification rate (RCR&amp;lt;sub&amp;gt;net&amp;lt;/sub&amp;gt;; g g&amp;lt;sup&amp;gt;-1 &amp;lt;/sup&amp;gt;d&amp;lt;sup&amp;gt;-1&amp;lt;/sup&amp;gt;) of each individual alga using the equation: RCR&amp;lt;sub&amp;gt;net&amp;lt;/sub&amp;gt; = (log(BW&amp;lt;sub&amp;gt;final&amp;lt;/sub&amp;gt;/BW&amp;lt;sub&amp;gt;initial&amp;lt;/sub&amp;gt;)*100)/Δt where Δt (d) is the total days elapsed between the beginning and end of the experiment.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Growth rates of &amp;lt;em&amp;gt;C. ruprechtiana&amp;lt;/em&amp;gt; reared in association with coralline algae in the different treatment conditions were quantified by measuring tissue wet weights (WW; g) at the beginning and end of the experiment. Thalli were removed from seawater, patted uniformly dry, and immediately weighed on a standard microbalance to the nearest 0.0001g. Relative growth rate (RGR&amp;lt;sub&amp;gt;net&amp;lt;/sub&amp;gt;; g g&amp;lt;sup&amp;gt;-1 &amp;lt;/sup&amp;gt;d&amp;lt;sup&amp;gt;-1&amp;lt;/sup&amp;gt;) of each individual alga was calculated using the equation: RGR&amp;lt;sub&amp;gt;net&amp;lt;/sub&amp;gt; = (log(WW&amp;lt;sub&amp;gt;final&amp;lt;/sub&amp;gt;/WW&amp;lt;sub&amp;gt;initial&amp;lt;/sub&amp;gt;)*100)/Δt&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;where Δt (d) is the total days elapsed between the beginning and end of the experiment.&amp;lt;/p&amp;gt;

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

&amp;lt;p&amp;gt;When processing these data for analysis and publication, we filtered out any individual with a weighing flag (weighing_flag = “y”), and any individuals in Poor condition at the end of the experiment (quality_code = “P”)&amp;lt;/p&amp;gt;</gco:CharacterString>
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        <gmx:Anchor xlink:href="http://lod.bco-dmo.org/id/award/756734.rdf" xlink:title="OCE-1752600" xlink:actuate="onRequest">Funding provided by NSF Division of Ocean Sciences (NSF OCE) Award Number: OCE-1752600 Award URL: https://www.nsf.gov/awardsearch/show-award?AWD_ID=1752600</gmx:Anchor>
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                <gco:CharacterString>&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Methodology: &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;&amp;lt;/p&amp;gt;

&amp;lt;p&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).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;The effects of each experimental pH and light treatment combination and fleshy red algal association on coralline net calcification rate were assessed using the buoyant weight technique (Jokiel et al. 1978), as well as the alkalinity anomaly technique. To determine total relative change in calcified mass over the experimental period, each coralline algae’s buoyant weight was measured to the nearest 0.0001g at the beginning and end of the experiment on a balanced platform suspended below a microbalance in a temperature-monitored seawater bath. To ensure precision, buoyant weights were repeated for each individual until measurements differed by less than ±0.005g, and then an average was taken of the measurements falling in this range of precision. Initial and final buoyant weights (BW; g) were used to calculate relative net calcification rate (RCR&amp;lt;sub&amp;gt;net&amp;lt;/sub&amp;gt;; g g&amp;lt;sup&amp;gt;-1 &amp;lt;/sup&amp;gt;d&amp;lt;sup&amp;gt;-1&amp;lt;/sup&amp;gt;) of each individual alga using the equation: RCR&amp;lt;sub&amp;gt;net&amp;lt;/sub&amp;gt; = (log(BW&amp;lt;sub&amp;gt;final&amp;lt;/sub&amp;gt;/BW&amp;lt;sub&amp;gt;initial&amp;lt;/sub&amp;gt;)*100)/Δt where Δt (d) is the total days elapsed between the beginning and end of the experiment.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Growth rates of &amp;lt;em&amp;gt;C. ruprechtiana&amp;lt;/em&amp;gt; reared in association with coralline algae in the different treatment conditions were quantified by measuring tissue wet weights (WW; g) at the beginning and end of the experiment. Thalli were removed from seawater, patted uniformly dry, and immediately weighed on a standard microbalance to the nearest 0.0001g. Relative growth rate (RGR&amp;lt;sub&amp;gt;net&amp;lt;/sub&amp;gt;; g g&amp;lt;sup&amp;gt;-1 &amp;lt;/sup&amp;gt;d&amp;lt;sup&amp;gt;-1&amp;lt;/sup&amp;gt;) of each individual alga was calculated using the equation: RGR&amp;lt;sub&amp;gt;net&amp;lt;/sub&amp;gt; = (log(WW&amp;lt;sub&amp;gt;final&amp;lt;/sub&amp;gt;/WW&amp;lt;sub&amp;gt;initial&amp;lt;/sub&amp;gt;)*100)/Δt&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;where Δt (d) is the total days elapsed between the beginning and end of the experiment.&amp;lt;/p&amp;gt;

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

&amp;lt;p&amp;gt;When processing these data for analysis and publication, we filtered out any individual with a weighing flag (weighing_flag = “y”), and any individuals in Poor condition at the end of the experiment (quality_code = “P”)&amp;lt;/p&amp;gt;</gco:CharacterString>
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                <gco:CharacterString>&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Processing notes from researcher:&amp;amp;nbsp;&amp;lt;/strong&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;When processing these data for analysis and publication, we filtered out any individual with a weighing flag (weighing_flag = “y”), and any individuals in Poor condition at the end of the experiment (quality_code = “P”)&amp;lt;/p&amp;gt;

&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 fields &amp;quot;tank.rep&amp;quot;, &amp;quot;alg.ID&amp;quot;, and &amp;quot;assoc.&amp;quot; to meet BCO-DMO naming conventions&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;- Converted date to YYYY-MM-DD format&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;- Rounded numerical fields&amp;lt;/p&amp;gt;</gco:CharacterString>
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    <gmx:Anchor xlink:href="http://lod.bco-dmo.org/id/affiliation/191.rdf" xlink:actuate="onRequest">Biological and Chemical Oceanography Data Management Office (BCO-DMO)</gmx:Anchor>
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				    <gco:CharacterString>WHOI MS#36</gco:CharacterString>
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				    <gco:CharacterString>Woods Hole</gco:CharacterString>
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				    <gco:CharacterString>USA</gco:CharacterString>
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				    <gco:CharacterString>info@bco-dmo.org</gco:CharacterString>
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                <gmx:Anchor xlink:href="http://lod.bco-dmo.org/id/instrument/711.rdf" xlink:title="Aquarium" xlink:actuate="onRequest">18-aquaria indoor experimental system</gmx:Anchor>
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            <gco:CharacterString>PI Supplied Instrument Name: 18-aquaria indoor experimental system PI Supplied Instrument Description: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 pHT 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-2 s-1, 13h d-1, winter = PPFD 40μmol m-2 s-1, 6h d-1). We had a total of 3 aquaria for each of the 6 treatment combinations. Instrument Name: Aquarium Instrument Short Name:Aquarium   Instrument Description: Aquarium - a vivarium consisting of at least one transparent side in which water-dwelling plants or animals are kept</gco:CharacterString>
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            <gco:CharacterString>PI Supplied Instrument Name: Honeywell DuraFET pH sensor 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>
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                <gmx:Anchor xlink:href="http://lod.bco-dmo.org/id/instrument/714.rdf" xlink:title="scale or balance" xlink:actuate="onRequest">Sartorius Entris 224-1S Microbalance</gmx:Anchor>
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