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            <gco:CharacterString>Cite this dataset as: Saley, A., Gaylord, B. (2024) Lab incubations of mussels (Mytilus californianus) examining the influence of simulated abrasion of periostracum on external shell dissolution at Marshall Gulch Beach, CA from August 2021 to March 2022. Biological and Chemical Oceanography Data Management Office (BCO-DMO). (Version 1) Version Date 2024-12-28 [if applicable, indicate subset used]. doi:10.26008/1912/bco-dmo.935480.1 [access date]</gco:CharacterString>
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        <gco:CharacterString>Methods and Sampling: &amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Overview: &amp;lt;/strong&amp;gt;We performed dissolution assays to explore the consequences of two levels of abrasion, used to remove the periostracum, on shell dissolution rates using dead shells of sacrificed adult&amp;amp;nbsp;&amp;lt;em&amp;gt;Mytilus californianus&amp;lt;/em&amp;gt;&amp;amp;nbsp;mussels. For the current study, adult mussels (42 - 64 mm in length) were collected from Marshall Gulch, California (38.369738 °N, -123.073921 °W) between August 2021 and March 2022 and transported immediately to the University of California Davis’ Bodega Marine Laboratory (&amp;amp;lt; 30 min distance), in Bodega Bay, California. Mussels were held in filtered, flow-through seawater and fed ad libitum until used in experiments. Because we were interested in the effects of the periostracum in protecting the exterior surface of the shell, we sealed the inner, nacre layer of the shell with silicone (Loctite marine silicone sealant) to prevent its contact with seawater.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Mussel valve preparation:&amp;lt;/strong&amp;gt; To prepare mussel valves for the incubation, shell periostracum was abraded using sanding sponges (Gator brand) of two levels of grit coarseness (P50-60: coarse (n = 11), and P120-150: fine (n = 12)). We included control mussel valves (15% of daily sample size), collected with no periostracum cover, to compare dissolution rates between abraded and periostracum that was removed naturally in the field.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Dissolution Incubations and Analysis:&amp;lt;/strong&amp;gt; We incubated each mussel valve in a sealed 250 mL Nalgene bottle filled with modified seawater for 48 hours in a temperature-controlled room, recording seawater properties in each bottle before and at the end of each incubation, including temperature, salinity, and pH (Yellow Springs Instruments Professional Plus Sonde). YSI sonde pH values were calibrated to the total scale based on pH spectrophotometric measurements of m-cresol dye absorbance at the incubation temperature. Incubation bottles were agitated gently once every 8 hours over the course of the incubations to reduce the establishment of strong chemical gradients of their fluid contents. We took discrete seawater samples at the onset and end of each incubation for determination of total alkalinity concentration (TA); these “before-after” measurements of TA enabled quantification of the increase in alkalinity within each bottle over the duration of the incubation, and thereby the rate of dissolution of calcium carbonate (CaCO3) shell material for individual valves of known periostracum cover. Shell dissolution rates were quantified using standard alkalinity anomaly techniques (analyzing seawater samples in triplicate and selecting median TA for dissolution quantification), which relate calcium carbonate shell loss to an increase in the total alkalinity (TA) of surrounding seawater, per unit time. Across the dissolution trials, control incubations (15% of daily sample size) of modified seawater were conducted to verify minimal background changes in TA.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Seawater manipulation:&amp;lt;/strong&amp;gt; We used direct chemical modification to the seawater carbonate system in order to create seawater treatments (pH = 7.4). To modify, equimolar additions of 1 M sodium bicarbonate (NaHCO3) and 1 M hydrochloric acid (HCl) were added to filtered seawater, capped, and were well mixed. This method results in an increase of dissolved inorganic carbon (DIC) and reduction of seawater pH without changing total alkalinity (TA).&amp;lt;/p&amp;gt;</gco:CharacterString>
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        <gmx:Anchor xlink:href="http://lod.bco-dmo.org/id/award/886710.rdf" xlink:title="OCE-2129942" xlink:actuate="onRequest">Funding provided by NSF Division of Ocean Sciences (NSF OCE) Award Number: OCE-2129942 Award URL: https://www.nsf.gov/awardsearch/show-award?AWD_ID=2129942</gmx:Anchor>
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	Name: INDEX
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http://lod.bco-dmo.org/id/dataset-parameter/947317.rdf
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	Description: &lt;p&gt;Initial pH of seawater (total scale) measured by spectrophotometer using m-cresol dye calibration&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/947324.rdf
	Name: temp_0
	Units: Degrees Celsius (°C)
	Description: &lt;p&gt;Initial seawater temperature&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/947325.rdf
	Name: sal_0
	Units: unitless
	Description: &lt;p&gt;Initial seawater salinity&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/947326.rdf
	Name: peri_percent
	Units: percentage (%)
	Description: &lt;p&gt;Periostracum cover: percent cover of intact periostracum over mussel valve&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/947327.rdf
	Name: shell_A
	Units: milimeters squared (mm^2)
	Description: &lt;p&gt;Mussel valve area measurement (ImageJ)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/947328.rdf
	Name: shell_L
	Units: milimeter (mm)
	Description: &lt;p&gt;Longest measured length of valve (ImageJ)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/947329.rdf
	Name: shell_W
	Units: milimeter (mm)
	Description: &lt;p&gt;Widest measured width of mussel valve (ImageJ)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/947330.rdf
	Name: incub_day
	Units: day
	Description: &lt;p&gt;Length of incubation in days&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/947331.rdf
	Name: incub_hr
	Units: hour
	Description: &lt;p&gt;Length of incubation in hours&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/947332.rdf
	Name: incub_min
	Units: minute
	Description: &lt;p&gt;Length of incubation in minutes&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/947333.rdf
	Name: alk_t0
	Units: micromole per kg (umol/kg)
	Description: &lt;p&gt;Initial alkalinity: measured alkalinity of seawater prior to incubation&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/947334.rdf
	Name: alk_t1
	Units: micromole per kg (umol/kg)
	Description: &lt;p&gt;Final alkalinity: measured alkalinity of seawater after completion of incubation&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/947335.rdf
	Name: alk_t0_t1
	Units: micromole per kg (umol/kg)
	Description: &lt;p&gt;Alkalinity change: change in alkalinity from initial measurement to final measurement (negative value indicates an increase in alkalinity)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/947336.rdf
	Name: alk_t0_t1_norm
	Units: micromole per kg per hour (umol kg-1 hr-1)
	Description: &lt;p&gt;Alkalinity change per hour: measured change in alkalinity normalized per hour of incubation&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/947337.rdf
	Name: diss
	Units: micromole per kg per hour (umol kg-1 hr-1)
	Description: &lt;p&gt;Dissoluton rate: inverse of alkalinity change measurement&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/947338.rdf
	Name: diss_diff
	Units: micromole per kg per hr per milimeter squared (umol kg-1 hr-1 mm-2)
	Description: &lt;p&gt;Normalized difference in Dissolution rate: dissolution rate normalized to individual shell area measurements and subtracted from control valve dissolution rates&lt;/p&gt; 
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                <gco:CharacterString>&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Overview: &amp;lt;/strong&amp;gt;We performed dissolution assays to explore the consequences of two levels of abrasion, used to remove the periostracum, on shell dissolution rates using dead shells of sacrificed adult&amp;amp;nbsp;&amp;lt;em&amp;gt;Mytilus californianus&amp;lt;/em&amp;gt;&amp;amp;nbsp;mussels. For the current study, adult mussels (42 - 64 mm in length) were collected from Marshall Gulch, California (38.369738 °N, -123.073921 °W) between August 2021 and March 2022 and transported immediately to the University of California Davis’ Bodega Marine Laboratory (&amp;amp;lt; 30 min distance), in Bodega Bay, California. Mussels were held in filtered, flow-through seawater and fed ad libitum until used in experiments. Because we were interested in the effects of the periostracum in protecting the exterior surface of the shell, we sealed the inner, nacre layer of the shell with silicone (Loctite marine silicone sealant) to prevent its contact with seawater.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Mussel valve preparation:&amp;lt;/strong&amp;gt; To prepare mussel valves for the incubation, shell periostracum was abraded using sanding sponges (Gator brand) of two levels of grit coarseness (P50-60: coarse (n = 11), and P120-150: fine (n = 12)). We included control mussel valves (15% of daily sample size), collected with no periostracum cover, to compare dissolution rates between abraded and periostracum that was removed naturally in the field.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Dissolution Incubations and Analysis:&amp;lt;/strong&amp;gt; We incubated each mussel valve in a sealed 250 mL Nalgene bottle filled with modified seawater for 48 hours in a temperature-controlled room, recording seawater properties in each bottle before and at the end of each incubation, including temperature, salinity, and pH (Yellow Springs Instruments Professional Plus Sonde). YSI sonde pH values were calibrated to the total scale based on pH spectrophotometric measurements of m-cresol dye absorbance at the incubation temperature. Incubation bottles were agitated gently once every 8 hours over the course of the incubations to reduce the establishment of strong chemical gradients of their fluid contents. We took discrete seawater samples at the onset and end of each incubation for determination of total alkalinity concentration (TA); these “before-after” measurements of TA enabled quantification of the increase in alkalinity within each bottle over the duration of the incubation, and thereby the rate of dissolution of calcium carbonate (CaCO3) shell material for individual valves of known periostracum cover. Shell dissolution rates were quantified using standard alkalinity anomaly techniques (analyzing seawater samples in triplicate and selecting median TA for dissolution quantification), which relate calcium carbonate shell loss to an increase in the total alkalinity (TA) of surrounding seawater, per unit time. Across the dissolution trials, control incubations (15% of daily sample size) of modified seawater were conducted to verify minimal background changes in TA.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Seawater manipulation:&amp;lt;/strong&amp;gt; We used direct chemical modification to the seawater carbonate system in order to create seawater treatments (pH = 7.4). To modify, equimolar additions of 1 M sodium bicarbonate (NaHCO3) and 1 M hydrochloric acid (HCl) were added to filtered seawater, capped, and were well mixed. This method results in an increase of dissolved inorganic carbon (DIC) and reduction of seawater pH without changing total alkalinity (TA).&amp;lt;/p&amp;gt;</gco:CharacterString>
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                <gco:CharacterString>&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Data analysis:&amp;lt;/strong&amp;gt; We performed computations with R statistical software, RStudio version 2023.06.2. We performed carbonate system calculations using the package seacarb. To understand whether abrasion from sand of differing coarseness might influence dissolution, we computed the difference between dissolution rates of mussel valves in abrasion treatments, and those of unsanded control (collected with &amp;amp;lt; 5% periostracum cover) valves exposed to similar low-pH conditions. We then used a Welch’s independent sample t-test to determine whether differences in average dissolution existed between the sanding treatments. Assumptions of normality and homogeneity of variances were assessed visually using QQ-plots.&amp;lt;/p&amp;gt;</gco:CharacterString>
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                  <gco:CharacterString>1) Processed the submitted file named sanddat_PUB.csv with the BCO-DMO tool Laminar.

BCO-DMO parameter naming convention is for names to only include alphanumeric characters and underscores. Periods in the parameter names have been replaced with underscores.

Renamed parameters according to BCO-DMO naming convention and to clarify what the parameter represents.

ph.t.0 renamed to temp_0 to make it clear this is a temperature value and an initial one

shell.L renamed to shell_L following BCO-DMO naming convention
shell.Wrenamed to shell_W following BCO-DMO naming convention

shell.a.mm2renamed to shell_A following BCO-DMO convention of removing units from parameter names if possible. Rename it using a capitalized A to match the capitalization of the parameters shell_L and shell_W.

peri.sa renamed to peri_percent to clarify it represents a percent. 

incub.hr renamed ti incub_hr following BCO-DMO naming convention
incub.min renamed incub_min following BCO-DMO naming convention

delta.time.days renamed incub_day to match the naming format of incub_hr and incub_min since they are all incubation durations

alk.t0 renamed to alk_t0 following BCO-DMO naming convention
alk.t1 renamed to alk_t1BCO-DMO following BCO-DMO naming convention
alk.t0.t1 renamed to alk_t0_t1BCO-DMO following BCO-DMO naming convention

umol.per.hour renamed to alk_t0_t1_norm to resemble the naming of the change in alkalinity parameter alk_t0_t1 and adding the suffix _norm to indicate it is normalized. 

diss.diff renamed to diss_diff following BCO-DMO naming convention


Created new parameters time_in_UTC and time_out_UTC by converting local timezone (Pacific Daylight time) parameters time_in and time_out to UTC

Saved dataset to primary data file named 935480_v1_mussel_lab_incubations_simulated_periostracum_abrasion.csv

2) Checked species taxonomy of mussel collected, Mytilus californianus, and created a taxonomy file using information from the World Register of Marine Species (WoRMS: marinespecies.org) with columns: ScientificName, AphiaID, LSID, Authority, Kingdom, Phylum, Class, Order, Family, Genus, Species</gco:CharacterString>
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