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            <gmx:Anchor xlink:href="http://lod.bco-dmo.org/id/dataset/868047.rdf" xlink:actuate="onRequest">Proximate biochemistry of sponge species collected in 2017 and 2018 across the Caribbean Basin in Curacao, Belize, Grand Cayman, St. Croix</gmx:Anchor>
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            <gco:CharacterString>Cite this dataset as: Slattery, M., Gochfeld, D. J. (2022) Proximate biochemistry of sponge species collected in 2017 and 2018 across the Caribbean Basin in Curacao, Belize, Grand Cayman, St. Croix. Biological and Chemical Oceanography Data Management Office (BCO-DMO). (Version 1) Version Date 2022-01-14 [if applicable, indicate subset used]. doi:10.26008/1912/bco-dmo.868047.1 [access date]</gco:CharacterString>
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        <gco:CharacterString>Methods and Sampling: &amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Sample collection&amp;lt;/strong&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;amp;nbsp;&amp;amp;nbsp;&amp;amp;nbsp;&amp;amp;nbsp;&amp;amp;nbsp;&amp;amp;nbsp;&amp;amp;nbsp;&amp;amp;nbsp;&amp;amp;nbsp;&amp;amp;nbsp;&amp;amp;nbsp; To assess the effect of the environment on sponge biochemical and energetic content, individuals (n = 2-21) of &amp;lt;em&amp;gt;Agelas conifera, Agelas tubulata, Amphimedon compressa, Aplysina cauliformis, Niphates amorpha, Niphates erecta, &amp;lt;/em&amp;gt;and&amp;lt;em&amp;gt; Xestospongia muta &amp;lt;/em&amp;gt;were collected at 15 m depth from 2-4 sites at each of 4 locations across the broader Caribbean Basin: Belize (May 2017), Curaçao (March 2017) , Grand Cayman (January 2018), St. Croix (August 2018).&amp;amp;nbsp; Although not every species was found in every region, target species were generally common and were selected to represent a range of antipredator chemical defenses (defended, undefended, variably defended), relative microbial abundance (HMA=high microbial abundance, LMA=low microbial abundance) and relative abundance of photoautotrophic symbionts (high, intermediate, low).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;amp;nbsp;&amp;amp;nbsp;&amp;amp;nbsp;&amp;amp;nbsp;&amp;amp;nbsp;&amp;amp;nbsp;&amp;amp;nbsp;&amp;amp;nbsp;&amp;amp;nbsp;&amp;amp;nbsp;&amp;amp;nbsp; Tissue samples were excised from individual sponges &amp;lt;em&amp;gt;in situ &amp;lt;/em&amp;gt;using scissors, placed into individual resealable plastic bags, kept submerged in seawater in a shaded cooler, and returned to shore where they were frozen at -20°C for transport.&amp;amp;nbsp; In the lab, sample wet mass and volume were recorded, and samples were freeze dried to determine dry mass, and ground to a powder.&amp;amp;nbsp;&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;Proximate Biochemical Analysis&amp;lt;/strong&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;The proximate biochemical composition (PBC) of sponge tissue was quantified as described in Clayshulte Abraham et al. (in press). Briefly, carbohydrates were extracted from 10 mg of ground freeze-dried tissue in 5% trichloroacetic acid (TCA) and concentration was determined using the phenol-sulfuric acid method in microplate format, as described in Masuko et al. (2005). Absorbance was measured using a BioTek Synergy HT Multi-Detection Microplate Reader.&amp;amp;nbsp; The concentration of carbohydrates in samples was calculated relative to a glucose standard curve.&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Protein was extracted from ground freeze-dried tissue in 1 M sodium hydroxide (NaOH) and the soluble protein concentration was analyzed using the Bradford Method (Bradford, 1976). Absorbance was measured using an Eppendorf Biophotometer.&amp;amp;nbsp; Soluble protein concentration in sponge samples was calculated relative to a standard curve using Bovine Serum Albumin (BSA).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Lipids were extracted using a modified version of the protocol described by Freeman et al. (1957).&amp;amp;nbsp; Briefly, ground freeze-dried tissue was sonicated, chloroform:methanol solution, and filtered into a conical tube containing distilled water.&amp;amp;nbsp; The organic layer was then pipetted into a pre-weighed vial, and this process was repeated three times. The organic solvent was then evaporated via vacuum centrifugation, and the final mass of dry lipid was recorded.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Ash was measured using methods in McClintock et al. (1991).&amp;amp;nbsp; Briefly, ground freeze-dried sponge tissue was placed into a pre-weighed foil pan, ashed at 500°C in a muffle furnace for 5 h, and the final mass of ash was recorded.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Refractory material was calculated by subtracting the combined masses of all of the measured components (carbohydrates, soluble protein, lipids, and ash) from the total sponge tissue mass to obtain ash-free dry weight (AFDW).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;The proportion of each biochemical constituent was calculated by dividing each constituent’s mass by the sample’s AFDW.&amp;amp;nbsp; The total sponge tissue energetic content was calculated by multiplying the proportional dry mass of each biochemical constituent by the kilojoule (kJ) coefficients detailed in Gnaiger &amp;amp;amp; Bitterlich (1984). For purposes of energetic calculations, refractory material was assumed to consist predominantly of insoluble protein.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;To quantify the concentration of total sponge extract obtained from each sample, ground freeze-dried sponge tissue was extracted in methanol:methylene chloride and sonicated.&amp;amp;nbsp; This was repeated twice, and the three extracts were combined in a pre-weighed vial.&amp;amp;nbsp; The solvent was removed via vacuum centrifugation to yield extract dry mass.&amp;amp;nbsp; Natural extract concentrations were calculated by based on initial volume to dry mass relationships for each sample.&amp;amp;nbsp;&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/649061.rdf" xlink:title="OCE-1638289" xlink:actuate="onRequest">Funding provided by NSF Division of Ocean Sciences (NSF OCE) Award Number: OCE-1638289 Award URL: https://www.nsf.gov/awardsearch/show-award?AWD_ID=1638289</gmx:Anchor>
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	Name: Genus
	Units: unitless
	Description: &lt;p&gt;Sponge genus&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/868064.rdf
	Name: Species
	Units: unitless
	Description: &lt;p&gt;Sponge species&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/868065.rdf
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http://lod.bco-dmo.org/id/dataset-parameter/868066.rdf
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http://lod.bco-dmo.org/id/dataset-parameter/868067.rdf
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http://lod.bco-dmo.org/id/dataset-parameter/868073.rdf
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	Units: milligrams per gram (mg/g)
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http://lod.bco-dmo.org/id/dataset-parameter/868075.rdf
	Name: ash
	Units: milligrams per gram (mg/g)
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http://lod.bco-dmo.org/id/dataset-parameter/868076.rdf
	Name: refractory_material_AFDW
	Units: milligrams per gram (mg/g)
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http://lod.bco-dmo.org/id/dataset-parameter/868077.rdf
	Name: total_energetic_content
	Units: kilojoules per gram (kJ/g)
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http://lod.bco-dmo.org/id/dataset-parameter/868078.rdf
	Name: total_energetic_content_AFDW
	Units: kilojoules per gram (kJ/g)
	Description: &lt;p&gt;Total energetic content (AFDW = ash-free dry weight). kilojoules per gram of ash free dry weight of sponge.&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/868079.rdf
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http://lod.bco-dmo.org/id/dataset-parameter/868080.rdf
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&amp;lt;p&amp;gt;&amp;amp;nbsp;&amp;amp;nbsp;&amp;amp;nbsp;&amp;amp;nbsp;&amp;amp;nbsp;&amp;amp;nbsp;&amp;amp;nbsp;&amp;amp;nbsp;&amp;amp;nbsp;&amp;amp;nbsp;&amp;amp;nbsp; To assess the effect of the environment on sponge biochemical and energetic content, individuals (n = 2-21) of &amp;lt;em&amp;gt;Agelas conifera, Agelas tubulata, Amphimedon compressa, Aplysina cauliformis, Niphates amorpha, Niphates erecta, &amp;lt;/em&amp;gt;and&amp;lt;em&amp;gt; Xestospongia muta &amp;lt;/em&amp;gt;were collected at 15 m depth from 2-4 sites at each of 4 locations across the broader Caribbean Basin: Belize (May 2017), Curaçao (March 2017) , Grand Cayman (January 2018), St. Croix (August 2018).&amp;amp;nbsp; Although not every species was found in every region, target species were generally common and were selected to represent a range of antipredator chemical defenses (defended, undefended, variably defended), relative microbial abundance (HMA=high microbial abundance, LMA=low microbial abundance) and relative abundance of photoautotrophic symbionts (high, intermediate, low).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;amp;nbsp;&amp;amp;nbsp;&amp;amp;nbsp;&amp;amp;nbsp;&amp;amp;nbsp;&amp;amp;nbsp;&amp;amp;nbsp;&amp;amp;nbsp;&amp;amp;nbsp;&amp;amp;nbsp;&amp;amp;nbsp; Tissue samples were excised from individual sponges &amp;lt;em&amp;gt;in situ &amp;lt;/em&amp;gt;using scissors, placed into individual resealable plastic bags, kept submerged in seawater in a shaded cooler, and returned to shore where they were frozen at -20°C for transport.&amp;amp;nbsp; In the lab, sample wet mass and volume were recorded, and samples were freeze dried to determine dry mass, and ground to a powder.&amp;amp;nbsp;&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;Proximate Biochemical Analysis&amp;lt;/strong&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;The proximate biochemical composition (PBC) of sponge tissue was quantified as described in Clayshulte Abraham et al. (in press). Briefly, carbohydrates were extracted from 10 mg of ground freeze-dried tissue in 5% trichloroacetic acid (TCA) and concentration was determined using the phenol-sulfuric acid method in microplate format, as described in Masuko et al. (2005). Absorbance was measured using a BioTek Synergy HT Multi-Detection Microplate Reader.&amp;amp;nbsp; The concentration of carbohydrates in samples was calculated relative to a glucose standard curve.&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Protein was extracted from ground freeze-dried tissue in 1 M sodium hydroxide (NaOH) and the soluble protein concentration was analyzed using the Bradford Method (Bradford, 1976). Absorbance was measured using an Eppendorf Biophotometer.&amp;amp;nbsp; Soluble protein concentration in sponge samples was calculated relative to a standard curve using Bovine Serum Albumin (BSA).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Lipids were extracted using a modified version of the protocol described by Freeman et al. (1957).&amp;amp;nbsp; Briefly, ground freeze-dried tissue was sonicated, chloroform:methanol solution, and filtered into a conical tube containing distilled water.&amp;amp;nbsp; The organic layer was then pipetted into a pre-weighed vial, and this process was repeated three times. The organic solvent was then evaporated via vacuum centrifugation, and the final mass of dry lipid was recorded.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Ash was measured using methods in McClintock et al. (1991).&amp;amp;nbsp; Briefly, ground freeze-dried sponge tissue was placed into a pre-weighed foil pan, ashed at 500°C in a muffle furnace for 5 h, and the final mass of ash was recorded.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Refractory material was calculated by subtracting the combined masses of all of the measured components (carbohydrates, soluble protein, lipids, and ash) from the total sponge tissue mass to obtain ash-free dry weight (AFDW).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;The proportion of each biochemical constituent was calculated by dividing each constituent’s mass by the sample’s AFDW.&amp;amp;nbsp; The total sponge tissue energetic content was calculated by multiplying the proportional dry mass of each biochemical constituent by the kilojoule (kJ) coefficients detailed in Gnaiger &amp;amp;amp; Bitterlich (1984). For purposes of energetic calculations, refractory material was assumed to consist predominantly of insoluble protein.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;To quantify the concentration of total sponge extract obtained from each sample, ground freeze-dried sponge tissue was extracted in methanol:methylene chloride and sonicated.&amp;amp;nbsp; This was repeated twice, and the three extracts were combined in a pre-weighed vial.&amp;amp;nbsp; The solvent was removed via vacuum centrifugation to yield extract dry mass.&amp;amp;nbsp; Natural extract concentrations were calculated by based on initial volume to dry mass relationships for each sample.&amp;amp;nbsp;&amp;amp;nbsp;&amp;lt;/p&amp;gt;</gco:CharacterString>
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&amp;lt;br /&amp;gt;
BCO-DMO data manager processing notes:&amp;lt;br /&amp;gt;
* Data submitted in Excel file&amp;amp;nbsp;DOB_biochemistry_to_upload.xlsx sheet 1 extracted as csv.&amp;lt;br /&amp;gt;
* Latitude and longitude rounded from 8 to 3 decimal places&amp;lt;br /&amp;gt;
* Year and month added to dataset from metadata for the regions.&amp;lt;br /&amp;gt;
* Species names checked using the World Register of Marine Species Taxa Match tool.&amp;amp;nbsp; A species list with taxonomic identifiers (AphiaID,TSN,LSID) was attached as a supplemental file. Matched all names in dataset exactly on 2022-01-14.&amp;lt;/p&amp;gt;</gco:CharacterString>
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            <gco:CharacterString>Eppendorf Biophotometer</gco:CharacterString>
          </gmi:type>
          <gmi:description>
            <gco:CharacterString>PI Supplied Instrument Name: Eppendorf Biophotometer Instrument Name: Spectrophotometer Instrument Short Name:Spectrophotometer   Instrument Description: An instrument used to measure the relative absorption of electromagnetic radiation of different wavelengths in the near infra-red, visible and ultraviolet wavebands by samples. 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>
