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            <gmx:Anchor xlink:href="http://lod.bco-dmo.org/id/dataset/660489.rdf" xlink:actuate="onRequest">SSU rRNA gene sequences from marine sediments, marine subseafloor, and deep seawater sampled from the Juan de Fuca Ridge Flank from various R/V Atlantis cruises from 2008-2011 (microJdFR project)</gmx:Anchor>
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            <gco:CharacterString>Cite this dataset as: Rappé, M. S. (2016) SSU rRNA gene sequences from marine sediments, marine subseafloor, and deep seawater sampled from the Juan de Fuca Ridge Flank from various R/V Atlantis cruises from 2008-2011 (microJdFR project). Biological and Chemical Oceanography Data Management Office (BCO-DMO). Version Date 2016-10-07 [if applicable, indicate subset used]. http://lod.bco-dmo.org/id/dataset/660489 [access date]</gco:CharacterString>
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        <gco:CharacterString>SSU rRNA gene sequences from marine sediments, marine subseafloor, and deep seawater Dataset Description: &amp;lt;p&amp;gt;This dataset includes SSU rRNA gene sequence accession identifiers&amp;amp;nbsp;from marine sediments, marine subseafloor, and deep seawater along with quantities of various elements&amp;amp;nbsp;and&amp;amp;nbsp;compounds including&amp;amp;nbsp;(oxygen, ammonium, methane, hydrogen, total dissolved nitrogen, calcium, nitrate, nitrate, and total iron). &amp;amp;nbsp;Also included in this dataset are microbial cell abundance, pH, latitude and longitude. &amp;amp;nbsp;The sampling area in Northeast Pacific Ocean waters&amp;amp;nbsp;include&amp;amp;nbsp;long-term borehole observatories (CORKs) in the&amp;amp;nbsp;Juan de Fuca (JdF) Ridge Flank region from R/V Atlantis cruises AT15-35, AT15-55, AT15-66 and AT18-07..&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;These data have been published in the following references:&amp;lt;/strong&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Jungbluth, Sean P., et al. &amp;quot;Data report: microbial diversity in sediment near Grizzly Bare Seamount in Holes U1363B and U1363G.&amp;quot;&amp;amp;nbsp;&amp;lt;em&amp;gt;Proc. IODP&amp;amp;nbsp;Volume&amp;lt;/em&amp;gt;. Vol. 327. 2013.&amp;amp;nbsp;&amp;lt;a href=&amp;quot;http://dx.doi.org/10.2204/iodp.proc.327.201.2013&amp;quot;&amp;gt;http://dx.doi.org/10.2204/iodp.proc.327.201.2013&amp;lt;/a&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Jungbluth, Sean P., et al. &amp;quot;Novel microbial assemblages inhabiting crustal fluids within mid-ocean ridge flank subsurface basalt.&amp;quot;&amp;amp;nbsp;&amp;lt;em&amp;gt;The ISME journal&amp;amp;nbsp;&amp;lt;/em&amp;gt;(2016).&amp;amp;nbsp;&amp;lt;a href=&amp;quot;http://dx.doi.org/10.1038/ismej.2015.248&amp;quot;&amp;gt;dx.doi.org/10.1038/ismej.2015.248&amp;lt;/a&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Lin, H-T, Hsieh, C-C, Cowen, JP,&amp;amp;nbsp;Rappe, MS (2015). Data report: dissolved and particulate organic carbon in the deep sediments of IODP Site U1363 near Grizzly Bare seamount.&amp;amp;nbsp;&amp;lt;em&amp;gt;Proceedings of the Integrated Ocean Drilling Program&amp;amp;nbsp;&amp;lt;/em&amp;gt;327: 1-16. &amp;amp;nbsp;&amp;lt;a href=&amp;quot;http://dx.doi.org/10.2204/iodp.proc.327.202.2015&amp;quot;&amp;gt;dx.doi.org/10.2204/iodp.proc.327.202.2015&amp;lt;/a&amp;gt;&amp;lt;/p&amp;gt; Methods and Sampling: &amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Sampling Methodology:&amp;lt;/strong&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Sediment coring was performed by the IODP (described in Expedition 327 Scientists, 2011; &amp;lt;em&amp;gt;Integrated Ocean Drilling Program&amp;lt;/em&amp;gt;). SSU rRNA genes were obtained as described in Jungbluth et al., 2013; &amp;lt;em&amp;gt;Proceedings of the Integrated Ocean Drilling Program&amp;lt;/em&amp;gt; (see &amp;lt;a href=&amp;quot;http://www.nature.com/ismej/journal/v7/n1/extref/ismej201273x7.doc&amp;quot;&amp;gt;Supplementary Information Document&amp;lt;/a&amp;gt;(.DOC)&amp;amp;nbsp;for this publication).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;CORK borehole fluids were sampled using a custom-built water sampler (described in Cowen et al., 2012). For a detailed description of the pump system&amp;amp;nbsp;see&amp;amp;nbsp;&amp;lt;a href=&amp;quot;http://dx.doi.org/10.1016/j.gca.2012.02.017&amp;quot;&amp;gt;Lin, et al. 2012&amp;lt;/a&amp;gt;.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Pore water&amp;amp;nbsp;dissolved organic carbon (&amp;lt;/strong&amp;gt;from&amp;amp;nbsp;Lin et al., 2015&amp;lt;em&amp;gt;&amp;amp;nbsp;&amp;lt;/em&amp;gt;&amp;lt;a href=&amp;quot;http://publications.iodp.org/proceedings/327/202/202_3.htm&amp;quot;&amp;gt;Materials and Methods&amp;amp;nbsp;&amp;lt;/a&amp;gt;).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Sedimentary pore water DOC concentrations were measured by high-temperature combustion using a Shimadzu TOC-VCSH analyzer. The combustion temperature was set at 720C to ensure complete oxidation of organic matter. Samples were acidified to pH &amp;amp;lt;2 by the addition of 45 uL of 2 M HCl to 3 mL samples. No acid contamination was observed based on monitoring the DOC value of low-carbon deionized water. Samples were purged with nitrogen gas within the autosampler syringe for 2 min in order to remove inorganic carbon. An injection volume of 150 uL was used, with five or six injections per sample. The reproducibility between replicate injections was &amp;amp;lt;1 uM. Analytical reference materials (ARM) supplied by Dr. Dennis Hansell (RSMAS, University of Miami) were measured before, between, and after analysis of environmental samples (Sharp et al., 2002; Dickson et al., 2007). At least one ARM was measured every five samples. The average measured concentration of the ARM was 42 plus or minus 2 uM (n&amp;amp;nbsp;= 44); the reported value was 41–43 uM. Our detection limit for DOC concentrations was ~2 uM.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Sediment organic carbon and nitrogen &amp;amp;nbsp;(&amp;lt;/strong&amp;gt;relevant text extracted from&amp;amp;nbsp;Lin et al., 2015&amp;lt;em&amp;gt;&amp;amp;nbsp;&amp;lt;/em&amp;gt;&amp;lt;a href=&amp;quot;http://publications.iodp.org/proceedings/327/202/202_3.htm&amp;quot;&amp;gt;Materials and Methods&amp;amp;nbsp;&amp;lt;/a&amp;gt;).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Whole sediment samples were analyzed for concentration of total carbon, organic carbon, and total nitrogen using an elemental combustion system (Costech ECS 4010) connected inline to an isotope-ratio mass spectrometer (Thermo Finnigan Delta XP). The amount of powdered sediment used for the analyses was optimized to provide sufficient carbon and nitrogen for isotopic composition analysis and varied between 26 and 425 mg. A subset of samples was acidified by fuming with concentrated HCl (Hedges and Stern, 1984) in order to remove inorganic carbon and quantify the particulate organic carbon (POC) content. Acid fuming did not remove inorganic nitrogen, resulting in insignificant differences between whole and acid-fumed total particulate nitrogen (PN) concentrations.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Analytical methods for&amp;amp;nbsp;geochemistry &amp;lt;/strong&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Text below extracted from &amp;lt;a href=&amp;quot;http://www.nature.com/ismej/journal/v10/n8/extref/ismej2015248x1.pdf&amp;quot;&amp;gt;Supplementary Information&amp;lt;/a&amp;gt; (PDF)&amp;amp;nbsp;Junbluth et al., 2016. &amp;amp;nbsp;See reference for full description.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Major ions (Ca2+, Mg2+, K+ , Na+, Cl- , SO4 2- and Br- ) were analyzed by ion chromatography on a Dionex ICS-1100s (Sunnyvale, CA, USA). In addition, magnesium and calcium concentrations were also analyzed by EDTA (colorimetric) and EGTA (electrometric) titration (Grasshoff et al., 1999), or inductively coupled plasma optical emission spectroscopy (ICP-OES) (Lin et al., 2012).&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Silicate, nitrate, nitrite, phosphate, dissolved sulfide and dissolved manganese concentrations were measured by colorimetry (Brewer and Spencer, 1971; Phillips et al., 1997; Grasshoff et al., 1999).&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;amp;nbsp;Ammonium concentrations were measured by a flow injection-fluorometric method (Jones, 1991). The detection limit was ~2 µM for ammonium in basement fluids and the analytical uncertainty is 0.5 µM.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Ferrous iron was measured directly by a Ferrozine colorimetry method (Stookey, 1970; Gibbs, 1976).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;For total iron analysis, samples were first reduced with ascorbic acid and analyzed as ferrous iron. The detection limit for both ferrous iron and total iron was 0.1 µM.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Dissolved organic carbon (DOC) was measured by high-temperature combustion using a TOC-VCSH analyzer (Sharp et al., 2002a; Dickson et al., 2007) (Shimadzu Corp., Kyoto, Japan).&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Total dissolved nitrogen (TDN) was measured with a chemiluminescence detector in-line with a Shimadzu TOC-VCSH analyzer (Sharp et al., 2002b).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Alkalinity was determined by acid titration. Acid (0.1N HCl) was standardized with CO2 certified reference materials (CRMs) purchased from the office of Andrew Dickson at Scripps Institution of Oceanography.&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;An Orion 911600 Semi-micro pH electrode (ThermoFisher Scientific, Waltham, MA, USA) was used to measure the pH and electrode potential during the titration process. The Gran function plot method was used to evaluate titration end-points and calculate sample alkalinity (Dickson et al., 2007). The analytical reproducibility for alkalinity measurements was &amp;amp;lt;0.02 mM.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;SSU rRNA gene cloning and sequencing&amp;amp;nbsp;&amp;lt;/strong&amp;gt;(from&amp;amp;nbsp;&amp;lt;a href=&amp;quot;http://www.nature.com/ismej/journal/v7/n1/extref/ismej201273x7.doc&amp;quot;&amp;gt;Supplementary Information Document&amp;lt;/a&amp;gt;(DOC)&amp;amp;nbsp;for Junbluth et al., 2013).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Small subunit ribosomal RNA (SSU rRNA) gene fragments were amplified via the polymerase chain reaction (PCR) using the universal oligonucleotide forward and reverse primers 519F (5’-CAGCMGCCGCGGTAATWC-3’) and 1406R (5’-ACGGGCGGTGTGTRC-3’), respectively. Each 20 ul PCR reaction contained 0.25 U of PicoMaxx high fidelity DNA polymerase (Stratagene, La Jolla, CA), 1x PicoMaxx reaction buffer, 200 uM of each of the four deoxynucleoside triphosphates (dNTPs), 200 nM of both forward and reverse primer, and ~3-4 ng of environmental DNA template. PCR cycling conditions consisted of an initial denaturation step at 95C for 4 minutes, followed by 35 to 38 cycles of 95C denaturation for 30 sec, 55C annealing for 1 min, 72C extension for 2 min, and a final extension step at 72C for 20 min. For the 2008 borehole fluid sample, a 3-cycle reconditioning PCR was performed in order to help eliminate heteroduplexes (Thompson et al., 2002). Amplification products of the anticipated length were excised from an agarose gel and subsequently purified using the QIAquick gel extraction kit (Qiagen, Valencia, CA). Products were cloned using either the pGEM-T Easy kit (Promega, Madison, WI) or the TOPO TA Cloning kit (Invitrogen, Carlsbad, CA) following the manufacturer’s instructions. Clones were sequenced unidirectionally on an ABI 3730XL DNA Analyzer&amp;amp;nbsp;(Applied Biosystems, Carlsbad, CA).&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Fluorescence Microscopy:&amp;amp;nbsp;microbial cell counts&amp;lt;em&amp;gt;&amp;amp;nbsp;&amp;lt;/em&amp;gt;&amp;amp;nbsp;&amp;lt;/strong&amp;gt;(from&amp;amp;nbsp;&amp;lt;a href=&amp;quot;http://www.nature.com/ismej/journal/v7/n1/extref/ismej201273x7.doc&amp;quot;&amp;gt;Supplementary Information Document&amp;lt;/a&amp;gt;(DOC)&amp;amp;nbsp;for Junbluth et al., 2016).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Sample preparation for microscopy and fluorescence microscopy Fluid samples for microscopy collected in 2011 were prepared in similar fashion to those collected in sampling years 2008-2010 and described previously (Jungbluth et al., 2013). Briefly, 40 to 120 ml sub-samples were fixed with a final concentration of 3% of 0.2 um-filtered formaldehyde for 2 to 4 hours at 4C, and subsequently filtered through 0.2 um pore-sized polycarbonate membranes (Whatman, Maidstone, United Kingdom). After air-drying, membranes were stored desiccated at -80ºC until microscopic analysis. Filter sections were prepared for fluorescence microscopy using a mix of Citifluor/VectaShield/PBS/DAPI as described previously (Jungbluth et al., 2013a). Stained filter sections were inspected with a Leica DM5000B epifluorescence microscope (Leica Microsystems, Wetzlar, Germany) (samples: SSF1-2, SSF4, MIX1-4, SW1-5, SW9-11, SW14-15) or an Eclipse 90i (Nikon Corp., Tokyo, Japan) epifluorescence microscope (all other samples). Both microscopes were equipped with 100x objectives and filter sets appropriate for DAPI fluorescence.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;References:&amp;lt;/strong&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Brewer P, Spencer D (1971). Colorimetric determination of manganese in anoxic waters. Limnol Oceanogr 16: 107-110. doi: 10.4319/lo.1971.16.1.0107&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Cowen, James P., et al. &amp;quot;Advanced instrument system for real-time and time-series microbial geochemical sampling of the deep (basaltic) crustal biosphere.&amp;quot;&amp;amp;nbsp;&amp;lt;em&amp;gt;Deep Sea Research Part I: Oceanographic Research Papers&amp;lt;/em&amp;gt;&amp;amp;nbsp;61 (2012): 43-56. &amp;amp;nbsp;&amp;lt;a href=&amp;quot;http://dx.doi.org/10.1016/j.dsr.2011.11.004&amp;quot;&amp;gt;http://dx.doi.org/10.1016/j.dsr.2011.11.004&amp;lt;/a&amp;gt;&amp;lt;/p&amp;gt;

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&amp;lt;p&amp;gt;Gibbs C (1976). Characterization and application of ferrozine iron reagent as a ferrous iron indicator. Anal Chem 48: 1197-1201. doi: 10.1021/ac50002a034&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Grasshoff K, Kremling K, Ehrhardt M (eds) (1999) Methods of seawater analysis. Wiley: Weinheim. doi: 10.1002/9783527613984&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Hedges, J.I., and Stern, J.H., 1984. Carbon and nitrogen determinations of carbonate-containing solids.&amp;amp;nbsp;Limnol. Oceanogr.,&amp;amp;nbsp;29(3):657–663.doi:10.4319/lo.1984.29.3.0657&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Jones RD (1991). An improved fluorescence method for the determination of nanomolar concentrations of ammonium in natural-waters. Limnol Oceanogr 36: 814-819. doi: 10.4319/lo.1991.36.4.0814&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Jungbluth, Sean P., et al. &amp;quot;Data report: microbial diversity in sediment near Grizzly Bare Seamount in Holes U1363B and U1363G.&amp;quot;&amp;amp;nbsp;&amp;lt;em&amp;gt;Proc. IODP&amp;amp;nbsp;Volume&amp;lt;/em&amp;gt;. Vol. 327. 2013.&amp;amp;nbsp;&amp;lt;a href=&amp;quot;http://dx.doi.org/10.2204/iodp.proc.327.201.2013&amp;quot;&amp;gt;http://dx.doi.org/10.2204/iodp.proc.327.201.2013&amp;lt;/a&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Jungbluth, Sean P., et al. &amp;quot;Novel microbial assemblages inhabiting crustal fluids within mid-ocean ridge flank subsurface basalt.&amp;quot;&amp;amp;nbsp;&amp;lt;em&amp;gt;The ISME journal&amp;amp;nbsp;&amp;lt;/em&amp;gt;(2016).&amp;amp;nbsp;&amp;lt;a href=&amp;quot;http://dx.doi.org/10.1038/ismej.2015.248&amp;quot;&amp;gt;dx.doi.org/10.1038/ismej.2015.248&amp;lt;/a&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Lin, H-T, Hsieh, C-C, Cowen, JP,&amp;amp;nbsp;Rappe, MS (2015). Data report: dissolved and particulate organic carbon in the deep sediments of IODP Site U1363 near Grizzly Bare seamount.&amp;amp;nbsp;&amp;lt;em&amp;gt;Proceedings of the Integrated Ocean Drilling Program&amp;amp;nbsp;&amp;lt;/em&amp;gt;327: 1-16. &amp;amp;nbsp;&amp;lt;a href=&amp;quot;http://dx.doi.org/10.2204/iodp.proc.327.202.2015&amp;quot;&amp;gt;dx.doi.org/10.2204/iodp.proc.327.202.2015&amp;lt;/a&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Lin, Huei-Ting, et al. &amp;quot;Inorganic chemistry, gas compositions and dissolved organic carbon in fluids from sedimented young basaltic crust on the Juan de Fuca Ridge flanks.&amp;quot;&amp;amp;nbsp;&amp;lt;em&amp;gt;Geochimica et Cosmochimica Acta&amp;lt;/em&amp;gt;&amp;amp;nbsp;85 (2012): 213-227.&amp;amp;nbsp;&amp;lt;a class=&amp;quot;S_C_ddDoi&amp;quot; href=&amp;quot;http://dx.doi.org/10.1016/j.gca.2012.02.017&amp;quot; id=&amp;quot;ddDoi&amp;quot; target=&amp;quot;doilink&amp;quot;&amp;gt;http://dx.doi.org/10.1016/j.gca.2012.02.017&amp;lt;/a&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Phillips BM, Anderson BS, Hunt JW (1997). Measurement and distribution of interstitial and overlying water ammonia and hydrogen sulfide in sediment toxicity tests. Mar Environ Res 44: 117-126. doi: 10.1016/S0141-1136(96)00087-6&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Sharp JH, Carlson CA, Peltzer ET, Castle-Ward DM, Savidge KB, Rinker KR (2002a). Final dissolved organic carbon broad community intercalibration and preliminary use of DOC reference materials. Mar Chem 77: 239-253. doi: 10.1016/S0304- 4203(02)00002-6&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Sharp JH, Rinker KR, Savidge KB, Abell J, Yves Benaim J, Bronk DA et al. (2002b). A preliminary methods comparison for measurement of dissolved organic nitrogen in seawater. Mar Chem 78: 171-184. doi: 10.1016/S0304-4203(02)00020-8&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Stookey LL (1970). Ferrozine- a new spectrophotometric reagent for iron. Anal Chem 42: 779-781. doi: 10.1021/ac60289a016&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Thompson JR, Marcelino LA, Polz MF. (2002). Heteroduplexes in mixed-template amplifications: formation, consequence and elimination by 'reconditioning PCR'. &amp;lt;em&amp;gt;Nucleic Acids Res&amp;lt;/em&amp;gt; &amp;lt;strong&amp;gt;30:&amp;lt;/strong&amp;gt; 2083-2088.&amp;lt;/p&amp;gt;</gco:CharacterString>
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(1) coordinate, integrate, support, and extend the research associated with four major programs—Juan de Fuca Ridge flank (JdF), South Pacific Gyre (SPG), North Pond (NP), and Dorado Outcrop (DO)—and other field sites;
(2) make substantial investments of resources to support field, laboratory, analytical, and modeling studies of the deep subseafloor ecosystems;
(3) facilitate and encourage synthesis and thematic understanding of submarine microbiological processes, through funding of scientific and technical activities, coordination and hosting of meetings and workshops, and support of (mostly junior) researchers and graduate students; and
(4) entrain, educate, inspire, and mentor an interdisciplinary community of researchers and educators, with an emphasis on undergraduate and graduate students and early-career scientists.
Note: Katrina Edwards was a former PI of C-DEBI; James Cowen is a former co-PI.
Data Management:
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	Name: database
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	Description: &lt;p&gt;Database to which the accession_id belongs to&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661226.rdf
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	Units: unitless
	Description: &lt;p&gt;Identification number for GenBank; SRA; or IMG databases&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661227.rdf
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	Units: unitless
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http://lod.bco-dmo.org/id/dataset-parameter/661228.rdf
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	Units: unitless
	Description: &lt;p&gt;Identifier for BioSample at NCBI.  A BioSample corresponds to descriptions of biological source materials used in experimental assays.&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661229.rdf
	Name: BioProjectID
	Units: unitless
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http://lod.bco-dmo.org/id/dataset-parameter/661230.rdf
	Name: description
	Units: unitless
	Description: &lt;p&gt;Description of sample and source material origin&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661231.rdf
	Name: sample_title
	Units: unitless
	Description: &lt;p&gt;Project-specific sample title&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661232.rdf
	Name: sample_name
	Units: unitless
	Description: &lt;p&gt;Descriptive sample title&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661233.rdf
	Name: organism
	Units: unitless
	Description: &lt;p&gt;Type of organism(s) sampled&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661234.rdf
	Name: collection_date
	Units: unitless
	Description: &lt;p&gt;Date of sample collection in format dd-mmm-yy.&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661235.rdf
	Name: depth
	Units: meters
	Description: &lt;p&gt;Depth of sample. Sea-water sample depths are reported as positive values. For sediment and borehole samples, elevation was set equal to the depth of the seafloor (all values negative) and depths into the seafloor are reported as positive values.&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661236.rdf
	Name: elev
	Units: meters
	Description: &lt;p&gt;Elevation of sample.  Sea-water samples are set to sea-level (0) . For sediment and borehole samples, elevation was set equal to the depth of the seafloor (all values negative).&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661237.rdf
	Name: env_biome
	Units: unitless
	Description: &lt;p&gt;Biome of sample site&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661238.rdf
	Name: env_feature
	Units: unitless
	Description: &lt;p&gt;Environmental features of sample site&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661239.rdf
	Name: env_material
	Units: unitless
	Description: &lt;p&gt;Environmental material of sample site&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661240.rdf
	Name: geo_loc_name
	Units: unitless
	Description: &lt;p&gt;Geolocation name of sample site&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661241.rdf
	Name: lat
	Units: decimal degrees
	Description: &lt;p&gt;latitutde&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661242.rdf
	Name: lon
	Units: decimal degrees
	Description: &lt;p&gt;longitude; west is negative&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661243.rdf
	Name: ph
	Units: pH scale
	Description: &lt;p&gt;pH&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661244.rdf
	Name: oxygen
	Units: micromoles per liter
	Description: &lt;p&gt;oxygen (O2)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661245.rdf
	Name: calcium
	Units: millimoles per liter
	Description: &lt;p&gt;calcium (Ca)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661246.rdf
	Name: magnesium
	Units: millimoles per liter
	Description: &lt;p&gt;magnesium (Mg)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661247.rdf
	Name: potassium
	Units: millimoles per liter
	Description: &lt;p&gt;potassium (K)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661248.rdf
	Name: sodium
	Units: millimoles per liter
	Description: &lt;p&gt;sodium (Na)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661249.rdf
	Name: chloride
	Units: millimoles per liter
	Description: &lt;p&gt;chloride (Cl-)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661250.rdf
	Name: bromide
	Units: millimoles per liter
	Description: &lt;p&gt;bromide (Br-)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661251.rdf
	Name: silicate
	Units: micromoles per liter
	Description: &lt;p&gt;silicon dioxide (SiO2)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661252.rdf
	Name: ammonium
	Units: micromoles per liter
	Description: &lt;p&gt;ammonium (NH4)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661253.rdf
	Name: phosphate
	Units: micromoles per liter
	Description: &lt;p&gt;phosphate (PO4)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661254.rdf
	Name: nitrite
	Units: micromoles per liter
	Description: &lt;p&gt;nitrite (NO2)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661255.rdf
	Name: nitrate
	Units: micromoles per liter
	Description: &lt;p&gt;nitrate (NO3)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661256.rdf
	Name: nitrate_and_nitrate
	Units: micromoles per liter
	Description: &lt;p&gt;combined nitrate and nitrate (NO3 and NO2)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661257.rdf
	Name: sulfate
	Units: millimoles per liter
	Description: &lt;p&gt;sulfate (SO4)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661258.rdf
	Name: dissolved_iron
	Units: micromoles per liter
	Description: &lt;p&gt;dissolved iron (dFe)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661259.rdf
	Name: total_iron
	Units: micromoles per liter
	Description: &lt;p&gt;total iron (Fe)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661260.rdf
	Name: Mn2plus
	Units: micromoles per liter
	Description: &lt;p&gt;Manganese ion (Mn2+)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661261.rdf
	Name: dissolved_hydrogen_sulfide
	Units: micromoles per liter
	Description: &lt;p&gt;dissolved hydrogen sulfide (dissolved H2S)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661262.rdf
	Name: dissolved_organic_carbon
	Units: micromoles per liter
	Description: &lt;p&gt;dissolved organic carbon (DOC)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661263.rdf
	Name: TDN
	Units: micromoles per liter
	Description: &lt;p&gt;total dissolved nitrogen (TDN)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661264.rdf
	Name: alkalinity
	Units: milliequivalents per liter
	Description: &lt;p&gt;alkalinity&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661265.rdf
	Name: methane
	Units: micromoles per liter
	Description: &lt;p&gt;methane (CH4)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661266.rdf
	Name: hydrogen
	Units: micromoles per liter
	Description: &lt;p&gt;hydrogen (H)&lt;/p&gt; 
http://lod.bco-dmo.org/id/dataset-parameter/661267.rdf
	Name: microbial_cell_abundance
	Units: cells per milliliter
	Description: &lt;p&gt;microbial cell abundance&lt;/p&gt; 
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&amp;lt;p&amp;gt;Sediment coring was performed by the IODP (described in Expedition 327 Scientists, 2011; &amp;lt;em&amp;gt;Integrated Ocean Drilling Program&amp;lt;/em&amp;gt;). SSU rRNA genes were obtained as described in Jungbluth et al., 2013; &amp;lt;em&amp;gt;Proceedings of the Integrated Ocean Drilling Program&amp;lt;/em&amp;gt; (see &amp;lt;a href=&amp;quot;http://www.nature.com/ismej/journal/v7/n1/extref/ismej201273x7.doc&amp;quot;&amp;gt;Supplementary Information Document&amp;lt;/a&amp;gt;(.DOC)&amp;amp;nbsp;for this publication).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;CORK borehole fluids were sampled using a custom-built water sampler (described in Cowen et al., 2012). For a detailed description of the pump system&amp;amp;nbsp;see&amp;amp;nbsp;&amp;lt;a href=&amp;quot;http://dx.doi.org/10.1016/j.gca.2012.02.017&amp;quot;&amp;gt;Lin, et al. 2012&amp;lt;/a&amp;gt;.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Pore water&amp;amp;nbsp;dissolved organic carbon (&amp;lt;/strong&amp;gt;from&amp;amp;nbsp;Lin et al., 2015&amp;lt;em&amp;gt;&amp;amp;nbsp;&amp;lt;/em&amp;gt;&amp;lt;a href=&amp;quot;http://publications.iodp.org/proceedings/327/202/202_3.htm&amp;quot;&amp;gt;Materials and Methods&amp;amp;nbsp;&amp;lt;/a&amp;gt;).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Sedimentary pore water DOC concentrations were measured by high-temperature combustion using a Shimadzu TOC-VCSH analyzer. The combustion temperature was set at 720C to ensure complete oxidation of organic matter. Samples were acidified to pH &amp;amp;lt;2 by the addition of 45 uL of 2 M HCl to 3 mL samples. No acid contamination was observed based on monitoring the DOC value of low-carbon deionized water. Samples were purged with nitrogen gas within the autosampler syringe for 2 min in order to remove inorganic carbon. An injection volume of 150 uL was used, with five or six injections per sample. The reproducibility between replicate injections was &amp;amp;lt;1 uM. Analytical reference materials (ARM) supplied by Dr. Dennis Hansell (RSMAS, University of Miami) were measured before, between, and after analysis of environmental samples (Sharp et al., 2002; Dickson et al., 2007). At least one ARM was measured every five samples. The average measured concentration of the ARM was 42 plus or minus 2 uM (n&amp;amp;nbsp;= 44); the reported value was 41–43 uM. Our detection limit for DOC concentrations was ~2 uM.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Sediment organic carbon and nitrogen &amp;amp;nbsp;(&amp;lt;/strong&amp;gt;relevant text extracted from&amp;amp;nbsp;Lin et al., 2015&amp;lt;em&amp;gt;&amp;amp;nbsp;&amp;lt;/em&amp;gt;&amp;lt;a href=&amp;quot;http://publications.iodp.org/proceedings/327/202/202_3.htm&amp;quot;&amp;gt;Materials and Methods&amp;amp;nbsp;&amp;lt;/a&amp;gt;).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Whole sediment samples were analyzed for concentration of total carbon, organic carbon, and total nitrogen using an elemental combustion system (Costech ECS 4010) connected inline to an isotope-ratio mass spectrometer (Thermo Finnigan Delta XP). The amount of powdered sediment used for the analyses was optimized to provide sufficient carbon and nitrogen for isotopic composition analysis and varied between 26 and 425 mg. A subset of samples was acidified by fuming with concentrated HCl (Hedges and Stern, 1984) in order to remove inorganic carbon and quantify the particulate organic carbon (POC) content. Acid fuming did not remove inorganic nitrogen, resulting in insignificant differences between whole and acid-fumed total particulate nitrogen (PN) concentrations.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Analytical methods for&amp;amp;nbsp;geochemistry &amp;lt;/strong&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Text below extracted from &amp;lt;a href=&amp;quot;http://www.nature.com/ismej/journal/v10/n8/extref/ismej2015248x1.pdf&amp;quot;&amp;gt;Supplementary Information&amp;lt;/a&amp;gt; (PDF)&amp;amp;nbsp;Junbluth et al., 2016. &amp;amp;nbsp;See reference for full description.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Major ions (Ca2+, Mg2+, K+ , Na+, Cl- , SO4 2- and Br- ) were analyzed by ion chromatography on a Dionex ICS-1100s (Sunnyvale, CA, USA). In addition, magnesium and calcium concentrations were also analyzed by EDTA (colorimetric) and EGTA (electrometric) titration (Grasshoff et al., 1999), or inductively coupled plasma optical emission spectroscopy (ICP-OES) (Lin et al., 2012).&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Silicate, nitrate, nitrite, phosphate, dissolved sulfide and dissolved manganese concentrations were measured by colorimetry (Brewer and Spencer, 1971; Phillips et al., 1997; Grasshoff et al., 1999).&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;amp;nbsp;Ammonium concentrations were measured by a flow injection-fluorometric method (Jones, 1991). The detection limit was ~2 µM for ammonium in basement fluids and the analytical uncertainty is 0.5 µM.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Ferrous iron was measured directly by a Ferrozine colorimetry method (Stookey, 1970; Gibbs, 1976).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;For total iron analysis, samples were first reduced with ascorbic acid and analyzed as ferrous iron. The detection limit for both ferrous iron and total iron was 0.1 µM.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Dissolved organic carbon (DOC) was measured by high-temperature combustion using a TOC-VCSH analyzer (Sharp et al., 2002a; Dickson et al., 2007) (Shimadzu Corp., Kyoto, Japan).&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Total dissolved nitrogen (TDN) was measured with a chemiluminescence detector in-line with a Shimadzu TOC-VCSH analyzer (Sharp et al., 2002b).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Alkalinity was determined by acid titration. Acid (0.1N HCl) was standardized with CO2 certified reference materials (CRMs) purchased from the office of Andrew Dickson at Scripps Institution of Oceanography.&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;An Orion 911600 Semi-micro pH electrode (ThermoFisher Scientific, Waltham, MA, USA) was used to measure the pH and electrode potential during the titration process. The Gran function plot method was used to evaluate titration end-points and calculate sample alkalinity (Dickson et al., 2007). The analytical reproducibility for alkalinity measurements was &amp;amp;lt;0.02 mM.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;SSU rRNA gene cloning and sequencing&amp;amp;nbsp;&amp;lt;/strong&amp;gt;(from&amp;amp;nbsp;&amp;lt;a href=&amp;quot;http://www.nature.com/ismej/journal/v7/n1/extref/ismej201273x7.doc&amp;quot;&amp;gt;Supplementary Information Document&amp;lt;/a&amp;gt;(DOC)&amp;amp;nbsp;for Junbluth et al., 2013).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Small subunit ribosomal RNA (SSU rRNA) gene fragments were amplified via the polymerase chain reaction (PCR) using the universal oligonucleotide forward and reverse primers 519F (5’-CAGCMGCCGCGGTAATWC-3’) and 1406R (5’-ACGGGCGGTGTGTRC-3’), respectively. Each 20 ul PCR reaction contained 0.25 U of PicoMaxx high fidelity DNA polymerase (Stratagene, La Jolla, CA), 1x PicoMaxx reaction buffer, 200 uM of each of the four deoxynucleoside triphosphates (dNTPs), 200 nM of both forward and reverse primer, and ~3-4 ng of environmental DNA template. PCR cycling conditions consisted of an initial denaturation step at 95C for 4 minutes, followed by 35 to 38 cycles of 95C denaturation for 30 sec, 55C annealing for 1 min, 72C extension for 2 min, and a final extension step at 72C for 20 min. For the 2008 borehole fluid sample, a 3-cycle reconditioning PCR was performed in order to help eliminate heteroduplexes (Thompson et al., 2002). Amplification products of the anticipated length were excised from an agarose gel and subsequently purified using the QIAquick gel extraction kit (Qiagen, Valencia, CA). Products were cloned using either the pGEM-T Easy kit (Promega, Madison, WI) or the TOPO TA Cloning kit (Invitrogen, Carlsbad, CA) following the manufacturer’s instructions. Clones were sequenced unidirectionally on an ABI 3730XL DNA Analyzer&amp;amp;nbsp;(Applied Biosystems, Carlsbad, CA).&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Fluorescence Microscopy:&amp;amp;nbsp;microbial cell counts&amp;lt;em&amp;gt;&amp;amp;nbsp;&amp;lt;/em&amp;gt;&amp;amp;nbsp;&amp;lt;/strong&amp;gt;(from&amp;amp;nbsp;&amp;lt;a href=&amp;quot;http://www.nature.com/ismej/journal/v7/n1/extref/ismej201273x7.doc&amp;quot;&amp;gt;Supplementary Information Document&amp;lt;/a&amp;gt;(DOC)&amp;amp;nbsp;for Junbluth et al., 2016).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Sample preparation for microscopy and fluorescence microscopy Fluid samples for microscopy collected in 2011 were prepared in similar fashion to those collected in sampling years 2008-2010 and described previously (Jungbluth et al., 2013). Briefly, 40 to 120 ml sub-samples were fixed with a final concentration of 3% of 0.2 um-filtered formaldehyde for 2 to 4 hours at 4C, and subsequently filtered through 0.2 um pore-sized polycarbonate membranes (Whatman, Maidstone, United Kingdom). After air-drying, membranes were stored desiccated at -80ºC until microscopic analysis. Filter sections were prepared for fluorescence microscopy using a mix of Citifluor/VectaShield/PBS/DAPI as described previously (Jungbluth et al., 2013a). Stained filter sections were inspected with a Leica DM5000B epifluorescence microscope (Leica Microsystems, Wetzlar, Germany) (samples: SSF1-2, SSF4, MIX1-4, SW1-5, SW9-11, SW14-15) or an Eclipse 90i (Nikon Corp., Tokyo, Japan) epifluorescence microscope (all other samples). Both microscopes were equipped with 100x objectives and filter sets appropriate for DAPI fluorescence.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;References:&amp;lt;/strong&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Brewer P, Spencer D (1971). Colorimetric determination of manganese in anoxic waters. Limnol Oceanogr 16: 107-110. doi: 10.4319/lo.1971.16.1.0107&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Cowen, James P., et al. &amp;quot;Advanced instrument system for real-time and time-series microbial geochemical sampling of the deep (basaltic) crustal biosphere.&amp;quot;&amp;amp;nbsp;&amp;lt;em&amp;gt;Deep Sea Research Part I: Oceanographic Research Papers&amp;lt;/em&amp;gt;&amp;amp;nbsp;61 (2012): 43-56. &amp;amp;nbsp;&amp;lt;a href=&amp;quot;http://dx.doi.org/10.1016/j.dsr.2011.11.004&amp;quot;&amp;gt;http://dx.doi.org/10.1016/j.dsr.2011.11.004&amp;lt;/a&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Dickson AG, Sabine CL, Christian JR (eds) (2007). Guide to best practices for ocean CO2 measurements, 191pp. (URL: http://cdiac.ornl.gov/oceans/Handbook_2007.html)&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Expedition 327 Scientists, 2011. Methods.&amp;amp;nbsp;&amp;lt;em&amp;gt;In&amp;lt;/em&amp;gt;&amp;amp;nbsp;Fisher, A.T., Tsuji, T., Petronotis, K., and the Expedition 327 Scientists,&amp;amp;nbsp;&amp;lt;em&amp;gt;Proc. IODP,&amp;lt;/em&amp;gt;&amp;amp;nbsp;327: Tokyo (Integrated Ocean Drilling Program Management International, Inc.).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Gibbs C (1976). Characterization and application of ferrozine iron reagent as a ferrous iron indicator. Anal Chem 48: 1197-1201. doi: 10.1021/ac50002a034&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Grasshoff K, Kremling K, Ehrhardt M (eds) (1999) Methods of seawater analysis. Wiley: Weinheim. doi: 10.1002/9783527613984&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Hedges, J.I., and Stern, J.H., 1984. Carbon and nitrogen determinations of carbonate-containing solids.&amp;amp;nbsp;Limnol. Oceanogr.,&amp;amp;nbsp;29(3):657–663.doi:10.4319/lo.1984.29.3.0657&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Jones RD (1991). An improved fluorescence method for the determination of nanomolar concentrations of ammonium in natural-waters. Limnol Oceanogr 36: 814-819. doi: 10.4319/lo.1991.36.4.0814&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Jungbluth, Sean P., et al. &amp;quot;Data report: microbial diversity in sediment near Grizzly Bare Seamount in Holes U1363B and U1363G.&amp;quot;&amp;amp;nbsp;&amp;lt;em&amp;gt;Proc. IODP&amp;amp;nbsp;Volume&amp;lt;/em&amp;gt;. Vol. 327. 2013.&amp;amp;nbsp;&amp;lt;a href=&amp;quot;http://dx.doi.org/10.2204/iodp.proc.327.201.2013&amp;quot;&amp;gt;http://dx.doi.org/10.2204/iodp.proc.327.201.2013&amp;lt;/a&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Jungbluth, Sean P., et al. &amp;quot;Novel microbial assemblages inhabiting crustal fluids within mid-ocean ridge flank subsurface basalt.&amp;quot;&amp;amp;nbsp;&amp;lt;em&amp;gt;The ISME journal&amp;amp;nbsp;&amp;lt;/em&amp;gt;(2016).&amp;amp;nbsp;&amp;lt;a href=&amp;quot;http://dx.doi.org/10.1038/ismej.2015.248&amp;quot;&amp;gt;dx.doi.org/10.1038/ismej.2015.248&amp;lt;/a&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Lin, H-T, Hsieh, C-C, Cowen, JP,&amp;amp;nbsp;Rappe, MS (2015). Data report: dissolved and particulate organic carbon in the deep sediments of IODP Site U1363 near Grizzly Bare seamount.&amp;amp;nbsp;&amp;lt;em&amp;gt;Proceedings of the Integrated Ocean Drilling Program&amp;amp;nbsp;&amp;lt;/em&amp;gt;327: 1-16. &amp;amp;nbsp;&amp;lt;a href=&amp;quot;http://dx.doi.org/10.2204/iodp.proc.327.202.2015&amp;quot;&amp;gt;dx.doi.org/10.2204/iodp.proc.327.202.2015&amp;lt;/a&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Lin, Huei-Ting, et al. &amp;quot;Inorganic chemistry, gas compositions and dissolved organic carbon in fluids from sedimented young basaltic crust on the Juan de Fuca Ridge flanks.&amp;quot;&amp;amp;nbsp;&amp;lt;em&amp;gt;Geochimica et Cosmochimica Acta&amp;lt;/em&amp;gt;&amp;amp;nbsp;85 (2012): 213-227.&amp;amp;nbsp;&amp;lt;a class=&amp;quot;S_C_ddDoi&amp;quot; href=&amp;quot;http://dx.doi.org/10.1016/j.gca.2012.02.017&amp;quot; id=&amp;quot;ddDoi&amp;quot; target=&amp;quot;doilink&amp;quot;&amp;gt;http://dx.doi.org/10.1016/j.gca.2012.02.017&amp;lt;/a&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Phillips BM, Anderson BS, Hunt JW (1997). Measurement and distribution of interstitial and overlying water ammonia and hydrogen sulfide in sediment toxicity tests. Mar Environ Res 44: 117-126. doi: 10.1016/S0141-1136(96)00087-6&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Sharp JH, Carlson CA, Peltzer ET, Castle-Ward DM, Savidge KB, Rinker KR (2002a). Final dissolved organic carbon broad community intercalibration and preliminary use of DOC reference materials. Mar Chem 77: 239-253. doi: 10.1016/S0304- 4203(02)00002-6&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Sharp JH, Rinker KR, Savidge KB, Abell J, Yves Benaim J, Bronk DA et al. (2002b). A preliminary methods comparison for measurement of dissolved organic nitrogen in seawater. Mar Chem 78: 171-184. doi: 10.1016/S0304-4203(02)00020-8&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Stookey LL (1970). Ferrozine- a new spectrophotometric reagent for iron. Anal Chem 42: 779-781. doi: 10.1021/ac60289a016&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Thompson JR, Marcelino LA, Polz MF. (2002). Heteroduplexes in mixed-template amplifications: formation, consequence and elimination by 'reconditioning PCR'. &amp;lt;em&amp;gt;Nucleic Acids Res&amp;lt;/em&amp;gt; &amp;lt;strong&amp;gt;30:&amp;lt;/strong&amp;gt; 2083-2088.&amp;lt;/p&amp;gt;

from Cruise: AT15-35 &lt;p&gt;R/V Atlantis – AT15-35 – HOV Alvin II dive 4432&lt;/p&gt;


from Cruise: AT15-55 &lt;p&gt;R/V Atlantis - AT15-51 - HOV Alvin II dives 4532, 4533, 4434, 4536, &amp;amp; 4537&lt;/p&gt;


from Cruise: AT15-66 &lt;p&gt;R/V Atlantis - AT15-66 - ROV Jason II dives J2-497, J2-498, J2-499, J2-502, J2-503, &amp;amp; J2-505, J2-500&lt;/p&gt;


from Cruise: AT18-07 &lt;p&gt;R/V Atlantis - AT18-07 - ROV Jason II dives J2-566, J2-569, J2-571, &amp;amp; J2-573&lt;/p&gt;</gco:CharacterString>
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      <gmx:Anchor xlink:href="http://lod.bco-dmo.org/id/platform/54003.rdf" xlink:title="R/V Atlantis" xlink:actuate="onRequest">vessel</gmx:Anchor>
    </gmi:description>
    <gmi:instrument gco:nilReason="unknown"/>
  </gmi:MI_Platform>
</gmi:platform>
          </gmi:MI_AcquisitionInformation>
  </gmi:acquisitionInformation>
</gmi:MI_Metadata>
