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          <gmd:keyword>
            <gmx:Anchor xlink:href="https://www.ncei.noaa.gov/archive/archive-management-system/OAS/bin/prd/jquery/datatype/details/223" xlink:actuate="onRequest">NITRATE</gmx:Anchor>
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          <gmd:keyword>
            <gmx:Anchor xlink:href="https://www.ncei.noaa.gov/archive/archive-management-system/OAS/bin/prd/jquery/datatype/details/226" xlink:actuate="onRequest">NITRITE</gmx:Anchor>
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          <gmd:keyword>
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          <gmd:keyword>
            <gmx:Anchor xlink:href="https://www.ncei.noaa.gov/archive/archive-management-system/OAS/bin/prd/jquery/datatype/details/257" xlink:actuate="onRequest">pH</gmx:Anchor>
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          <gmd:keyword>
            <gmx:Anchor xlink:href="https://www.ncei.noaa.gov/archive/archive-management-system/OAS/bin/prd/jquery/datatype/details/263" xlink:actuate="onRequest">phosphate</gmx:Anchor>
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          <gmd:keyword>
            <gmx:Anchor xlink:href="https://www.ncei.noaa.gov/archive/archive-management-system/OAS/bin/prd/jquery/datatype/details/307" xlink:actuate="onRequest">SALINITY</gmx:Anchor>
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          <gmd:keyword>
            <gmx:Anchor xlink:href="https://www.ncei.noaa.gov/archive/archive-management-system/OAS/bin/prd/jquery/datatype/details/573" xlink:actuate="onRequest">SIGMA-THETA</gmx:Anchor>
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          <gmd:keyword>
            <gmx:Anchor xlink:href="https://www.ncei.noaa.gov/archive/archive-management-system/OAS/bin/prd/jquery/datatype/details/333" xlink:actuate="onRequest">silicate</gmx:Anchor>
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          <gmd:keyword>
            <gmx:Anchor xlink:href="https://www.ncei.noaa.gov/archive/archive-management-system/OAS/bin/prd/jquery/datatype/details/5" xlink:actuate="onRequest">total alkalinity</gmx:Anchor>
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          <gmd:keyword>
            <gmx:Anchor xlink:href="https://www.ncei.noaa.gov/archive/archive-management-system/OAS/bin/prd/jquery/datatype/details/373" xlink:actuate="onRequest">WATER TEMPERATURE</gmx:Anchor>
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          <gmd:keyword>
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          <gmd:keyword>
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          <gmd:keyword>
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          <gmd:keyword>
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                <gco:CharacterString>NODC OBSERVATION TYPES THESAURUS</gco:CharacterString>
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          <gmd:keyword>
            <gmx:Anchor xlink:href="https://cmr.earthdata.nasa.gov/kms/concept/d9b4f30d-bddd-4888-b66b-07d2dc09708b" xlink:actuate="onRequest">EARTH SCIENCE &gt; OCEANS &gt; OCEAN CHEMISTRY &gt; INORGANIC CARBON</gmx:Anchor>
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          <gmd:keyword>
            <gmx:Anchor xlink:href="https://cmr.earthdata.nasa.gov/kms/concept/4fde380a-38c5-4d46-bc80-4f2515a43983" xlink:actuate="onRequest">EARTH SCIENCE &gt; OCEANS &gt; OCEAN CHEMISTRY &gt; NITRATE</gmx:Anchor>
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          <gmd:keyword>
            <gmx:Anchor xlink:href="https://cmr.earthdata.nasa.gov/kms/concept/941410da-0b7f-4ec6-a718-212194ced13f" xlink:actuate="onRequest">EARTH SCIENCE &gt; OCEANS &gt; OCEAN CHEMISTRY &gt; NITRITE</gmx:Anchor>
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          <gmd:keyword>
            <gmx:Anchor xlink:href="https://cmr.earthdata.nasa.gov/kms/concept/90aa8838-79bd-4b28-b518-8217e863c385" xlink:actuate="onRequest">EARTH SCIENCE &gt; OCEANS &gt; OCEAN CHEMISTRY &gt; OXYGEN</gmx:Anchor>
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          <gmd:keyword>
            <gmx:Anchor xlink:href="https://cmr.earthdata.nasa.gov/kms/concept/4433600b-f323-458a-b295-352f939aab6b" xlink:actuate="onRequest">EARTH SCIENCE &gt; OCEANS &gt; OCEAN CHEMISTRY &gt; PH</gmx:Anchor>
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          <gmd:keyword>
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            <gco:CharacterString>STATION_NO</gco:CharacterString>
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            <gco:CharacterString>TIME_LOCAL</gco:CharacterString>
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            <gco:CharacterString>TIME_UTC</gco:CharacterString>
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            <gco:CharacterString>fCO2_inSitu_Lueker, fCO2_inSitu_Waters, pCO2_inSitu_Lueker, and pCO2_inSitu_Waters</gco:CharacterString>
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                <gco:CharacterString>Provider Variable Abbreviations</gco:CharacterString>
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          <gmd:keyword>
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            <gmd:MD_KeywordTypeCode codeList="https://data.noaa.gov/resources/iso19139/schema/resources/Codelist/gmxCodelists.xml#MD_KeywordTypeCode" codeListValue="instrument">instrument</gmd:MD_KeywordTypeCode>
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                        <gmd:CI_OnlineResource>
                          <gmd:linkage>
                            <gmd:URL>https://forum.earthdata.nasa.gov/app.php/tag/GCMD%2BKeywords</gmd:URL>
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                            <gco:CharacterString>HTTPS</gco:CharacterString>
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  <gmd:dataQualityInfo>
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        <gmd:DQ_Scope>
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              <gmd:description>
                <gco:CharacterString>Parameter or Variable: Dissolved Inorganic Carbon;
Abbreviation: DIC_UMOL_KG;
Unit: micromoles per kilogram of seawater (umol/kg-SW);
Observation type: Discrete measurements from samples collected on CTD casts;
In-situ / Manipulation / Response variable: in-situ observation;
Measured or calculated: Measured;
Calculation method and parameters: Not applicable;
Sampling instrument: Niskin bottle;
Analyzing instrument: Two systems consisting of a coulometer (UIC, Inc.) coupled with a SOMMA (Single Operator Multiparameter Metabolic Analyzer) inlet system developed by K.M. Johnson (Johnson et al., 1985, 1987, 1993, 1999; Johnson,1992) of Brookhaven National Laboratory (BNL).;
Detailed sampling and analyzing information: PLEASE NOTE: DIC may be referred to as TCO2, TCARBN, or C(sub)T in other data sets. All of these abbreviations refer to the total dissolved inorganic carbon concentration (i.e., the combined concentration of dissolved CO2, bicarbonate ion, and carbonate ion). Inorganic carbon samples were collected from Niskins after oxygen samples. A combined sample for dissolved inorganic carbon (DIC) and total alkalinity (TA) measurements was drawn into ~540 mL borosilicate glass flasks using silicone tubing according to procedures outlined in the Guide to Best Practices for Ocean CO2 Measurements (SOP 1, Dickson et al. 2007). Briefly, flasks were rinsed once and filled from the bottom with care not to entrain any bubbles, overflowing by at least one-half volume. The sample tube was pinched and withdrawn, creating a small headspace, and 0.2 mL of saturated mercuric chloride (HgCl2) solution was added as a preservative. Sample bottles were then sealed with glass stoppers lightly covered with Apiezon-L grease. Stoppers were held in place until analysis with a thick rubber band over the stopper attached to a plastic clamp around the neck of the sample flask. Sample bottles were inverted several times to ensure mixing of the HgCl2 throughout the sample. DIC samples were collected from variety of depths, with approximately 5% of samples drawn in duplicate (or occasionally triplicate). All samples were stored under cool, dark conditions until analysis. DIC concentrations were measured at PMEL on analytical systems consisting of a coulometer (UIC Inc.) coupled with a Single Operator Multiparameter Metabolic Analyzer (SOMMA). The SOMMA was developed to extract DIC from seawater by Ken Johnson and colleagues (Johnson et al. 1985, 1987, 1993, and 1999; Johnson 1992) of Brookhaven National Laboratory. Each coulometer was calibrated at the beginning of each analysis day, when a fresh coulometric cell was prepared, by injecting aliquots of pure CO2 (99.999%) by way of an eight-port valve (Wilke et al., 1993) outfitted with two calibrated sample loops of different sizes (~1 mL and ~2 mL). Roughly 20–25 samples were typically analyzed per coulometric cell.;
Replicate information: Duplicate samples were collected from approximately 5% of the Niskins sampled, as a check of our precision. These replicate samples were interspersed throughout the station analysis for quality assurance and integrity of the coulometer cell solutions. The average absolute difference from the mean of these replicates is 1.5 µmol/kg. No systematic differences between the replicates were observed.;
Standardization description: Each coulometer was calibrated by injecting aliquots of pure CO2 (99.999%) by means of an 8-port valve (Wilke et al., 1993) outfitted with two calibrated sample loops of different sizes (~1 mL and ~2 mL. The instruments were each separately calibrated at the beginning of each cell with a minimum of two sets of these gas loop injections and then again at the end of each cell to ensure no drift during the life of the cell.;
Standardization frequency: 1) Gas loops were run at the beginning and end of each cell; 2) CRM’s supplied by Dr. A. Dickson of SIO, were measured near the beginning; and 3) Duplicate samples were typically run throughout the life of the cell solution.;
CRM manufacturer: Dr. Andrew Dickson (Scripps Institution of Oceanography);
CRM batch number: Various;
Preservation method: Mercuric Chloride Solution (saturated HgCl2);
Preservative volume: 0.2 mL;
Preservative correction: The DIC values were corrected for dilution by 0.2 mL of saturated HgCl2 used for sample preservation. The total water volume of the sample bottles was ~540 mL. The correction factor used for dilution was 1.00037.;
Uncertainty: ±0.1%;
Quality flag convention: DIC_FLAG_W, WOCE water sample quality codes are used: 2 = acceptable measurement, 3 = questionable measurement, 4 = bad measurement, 5 = not reported, 6 = mean of replicate measurements, 9 = sample not drawn for measurement from this Niskin bottle. These QC codes were initially assigned on the basis of the observed quality of laboratory analysis. These codes do not account for field sampling aberrations. Adjustments to quality codes were made after careful inspection of the data set after data processing. Where sample values were observed to be strong outliers in cross-plots with other variables, the quality codes have been updated from a 2 to a 3 or 4 after close inspection of the profile at that station, including other parameters. Those flagged 3 represent values that are questionable due to being out of expected ranges or having inverted profile values from what would normally be expected in this region. Those flagged 4 are either values that clearly represent a Niskin misfire at an unknown depth or were flagged 4 due to analytical problems. Measurements with quality codes of 4 have been expunged and replaced with quality codes of 5 prior to submission.;
Method reference: Dickson, A.G., C.L. Sabine, and J.R. Christian (eds.). 2007. Guide to best practices for ocean CO2 measurements. PICES Special Publication 3, 191 pp. Johnson, K.M., A.E. King, and J. McN. Sieburth. 1985. Coulometric DIC analyses for marine studies: An introduction. Mar. Chem., 16, 61–82. Johnson, K.M., P.J. Williams, L. Brandstrom, and J. McN. Sieburth. 1987. Coulometric total carbon analysis for marine studies: Automation and calibration. Mar. Chem., 21, 117–133. Johnson, K.M. 1992. Operator’s manual: Single operator multiparameter metabolic analyzer (SOMMA) for total carbon dioxide (CT) with coulometric detection. Brookhaven National Laboratory, Brookhaven, N.Y., 70 pp. Johnson, K.M., K.D. Wills, D.B. Butler, W.K. Johnson, and C.S. Wong. 1993. Coulometric total carbon dioxide analysis for marine studies: Maximizing the performance of an automated continuous gas extraction system and coulometric detector. Mar. Chem., 44, 167–189. Johnson, K.M., Kortzinger, A.; Mintrop, L.; Duinker, J.C.; and Wallace, D.W.R. 1999. Coulometric total carbon dioxide analysis for marine studies: Measurement and internal consistency of underway surface TCO2 concentrations. Marine Chemistry 67(1):123-144.;
Researcher name: Dana Greeley; PIs: Simone Alin and Richard Feely;
Researcher institution: Pacific Marine Environmental Laboratory, National Oceanic and Atmospheric Administration</gco:CharacterString>
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          </gmd:processStep>
          <gmd:processStep>
            <gmi:LE_ProcessStep>
              <gmd:description>
                <gco:CharacterString>Parameter or Variable: Total alkalinity;
Abbreviation: TA_UMOL_KG;
Unit: micromoles per kilogram of seawater (umol/kg-SW);
Observation type: Discrete measurements from samples collected on CTD casts;
In-situ / Manipulation / Response variable: in-situ observation;
Measured or calculated: Measured;
Calculation method and parameters: Not applicable;
Sampling instrument: Niskin bottle;
Analyzing instrument: Custom instrument, built by Dr. Andrew Dickson's laboratory at Scripps Oceanographic Institution.;
Type of titration: Two-stage, potentiometric, open-cell titration using coulometrically analyzed hydrochloric acid;
Cell type (open or closed): Open;
Curve fitting method: Non-linear least squares;
Detailed sampling and analyzing information: Seawater samples for total alkalinity were drawn directly from Niskin bottles into 250-500mL borosilicate glass (Corning Pyrex/Schott Duran) bottles as described in SOP1 of “The Guide to Best Practices for Ocean CO2 Measurements” (Dickson A.G., Sabine L.S. and Christian J.R, Eds., 2007), using silicone tubing. The bottles were then sealed with glass stoppers lightly coated with Apiezon-L grease. The flasks were rinsed once and filled from the bottom with care not to entrain any bubbles, overflowing by at least one full volume. The sample tube was pinched off and withdrawn, creating a ~1% headspace and preserved with small vol. of a saturated mercuric chloride solution (0.12-0.24mL) and the final alkalinity concentration corrected for this addition. The samples were subsequently analyzed according to SOP3b of “The Guide to Best Practices for Ocean CO2 Measurements”, using an open cell titration system built by the Dickson Lab in 2016 at Scripps Institution of Oceanography, University of California San Diego. Sample and instrument temperature was controlled and sample size was measured gravimetrically. The instrument was controlled and alkalinity determined by software developed by the Dickson Lab. Instrument accuracy and precision was monitored at regular intervals using Certified Reference Materials (CRMs), consisting of filtered and UV irradiated seawater supplied by the Dickson Lab (SIO-UCSD).;
Replicate information: Duplicate samples were collected from approximately 10% of the Niskins sampled as a check of our precision.;
Standardization description: Analytical accuracy was assessed by routine analysis of Certified Reference Materials (CRMs). CRMs were analyzed approximately every 10 to 24 samples. The average offset for samples run on our analytical systems is &lt;2 µmol/kg.;
Standardization frequency: All values were directly measured with reference to Certified Reference Material (Dickson, SIO);
CRM manufacturer: Dr. Andrew Dickson (Scripps Institution of Oceanography);
CRM batch number: Various;
Preservation method: Mercuric Chloride Solution;
Preservative volume: 0.12-0.24 ml;
Preservative correction: The TA values were corrected for dilution by 0.12-0.24 ml of saturated HgCl2 used for sample preservation.;
TA blank correction: Not applicable;
Uncertainty: The precision of this method is better than 0.1% and accuracy is 0.1%.;
Quality flag convention: TA_FLAG_W, WOCE water sample quality codes are used: 2 = acceptable measurement, 3 = questionable measurement, 4 = bad measurement, 5 = not reported, 6 = mean of replicate measurements, 9 = sample not drawn for measurement from this Niskin bottle. These QC codes were initially assigned on the basis of the observed quality of laboratory analysis. These codes do not account for field sampling aberrations. Adjustments to quality codes were made after careful inspection of the data set after data processing. Where sample values were observed to be strong outliers in cross-plots with other variables, the quality codes have been updated from a 2 to a 3 or 4 after close inspection of the profile at that station, including other parameters. Those flagged 3 represent values that are questionable due to being out of expected ranges, having inverted profile values from what would normally be expected in this region, or being strong outliers in TA vs. S cross-plot and regression analyses. Those flagged 4 are either values that clearly represent a Niskin misfire at an unknown depth or were flagged 4 due to analytical problems. Measurements with quality codes of 4 have been expunged and replaced with quality codes of 5 prior to submission.;
Method reference: • Bates, R.G. Determination of pH. Theory and Practice. A Wiley-Interscience Publication, Second Edition. • Dickson A.G. (1981). An exact definition of total alkalinity, and a procedure for the estimation of alkalinity and total inorganic carbon from titration data. Deep-Sea Res. 28, 609-623. • Dickson A.G. (1992). The development of the alkalinity concept in marine chemistry. Marine chemistry 40:1-21-2, 49-63. • Dickson, A. G., Afghan, J. D., Anderson, G. C. (2003). Reference materials for oceanic CO2 analysis: A method for the certification of total alkalinity. Marine Chemistry 80, 185–197 • Gran G. (1952). Determination of the equivalence point in potentiometric titrations. Part II. The analyst, 77, 661-671. • Wolf-Gladrow, D.A. et al. (2007). Total alkalinity: The explicit conservative expression and its application to biogeochemical process.;
Researcher name: Julian Herndon; PIs: Simone Alin and Richard Feely;
Researcher institution: Pacific Marine Environmental Laboratory, National Oceanic and Atmospheric Administration</gco:CharacterString>
              </gmd:description>
            </gmi:LE_ProcessStep>
          </gmd:processStep>
          <gmd:processStep>
            <gmi:LE_ProcessStep>
              <gmd:description>
                <gco:CharacterString>Parameter or Variable: pH;
Abbreviation: pH_total_Lueker and pH_total_Waters;
pH scale: total;
Observation type: pH values calculated from DIC_UMOL_KG and TA_UMOL_KG;
Measured or calculated: CALCULATED;
Calculation method and parameters: Calculations were done using two different dissociation constant coefficients, Lueker et al. (2000) and Waters et al. (2014), as described in the abstract for this data product. The resulting values are differentiated by "_Lueker" and "_Waters" in the variable names and column headers.;
Temperature of pH measurement: in-situ temperature;
Uncertainty: ±3.0% for [H+] per Orr et al. 2018, including both input variable uncertainties and uncertainties associated with dissociation constants;
Quality flag convention: All data flags for input parameters used for calculating pH were QC 2 ("acceptable"). Therefore, the calculated pH values should also have QC flags of 2.;
Method reference: Gattuso et al. (2023);
Researcher name: Simone Alin;
Researcher institution: NOAA Pacific Marine Environmental Laboratory</gco:CharacterString>
              </gmd:description>
            </gmi:LE_ProcessStep>
          </gmd:processStep>
          <gmd:processStep>
            <gmi:LE_ProcessStep>
              <gmd:description>
                <gco:CharacterString>Parameter or Variable: pCO2 (fCO2) autonomous;
Abbreviation: fCO2_inSitu_Lueker, fCO2_inSitu_Waters, pCO2_inSitu_Lueker, and pCO2_inSitu_Waters;
Unit: Microatmospheres (µatm);
Observation type: pCO2 and fCO2 values calculated from DIC_UMOL_KG and TA_UMOL_KG at in situ temperatures and pressures;
Measured or calculated: CALCULATED;
Calculation method and parameters: Calculations were done using two different dissociation constant coefficients, Lueker et al. (2000) and Waters et al. (2014), as described in the abstract for this data product. The resulting values are differentiated by "_Lueker" and "_Waters" in the variable names and column headers.;
At what temperature was pCO2 reported: in-situ temperature;
Uncertainty: ±3.5% for pCO2 per Orr et al. 2018, including both input variable uncertainties and uncertainties associated with dissociation constants;
Quality flag convention: All data flags for input parameters used for calculating fCO2 and pCO2 were QC 2 ("acceptable"). Therefore, the calculated fCO2 and pCO2 values should also have QC flags of 2.;
Method reference: Gattuso et al. (2023);
Researcher name: Simone Alin;
Researcher institution: NOAA Pacific Marine Environmental Laboratory</gco:CharacterString>
              </gmd:description>
            </gmi:LE_ProcessStep>
          </gmd:processStep>
          <gmd:processStep>
            <gmi:LE_ProcessStep>
              <gmd:description>
                <gco:CharacterString>Parameter or Variable: Hydrostatic pressure recorded from CTD at the depth where the sample is taken;
Abbreviation: CTDPRS_DBAR;
Unit: dbars (=decibars);
Observation type: Water column profile;
In-situ / Manipulation / Response variable: in-situ observation;
Measured or calculated: Measured;
Calculation method and parameters: Not applicable;
Sampling instrument: Sea-Bird Scientific SBE CTD (various models--see each cruise for details if needed);
Detailed sampling and analyzing information: This file contains the up cast data collected using the CTD package and any additional sensors attached to a rosette cage deployed on a research vessel. The up cast data correspond to when the bottles on the rosette cage were fired and water samples were collected. All up casts during the cruise are contained in this file and are sorted by station. CTD data were processed using Sea-Bird's proprietary data processing software using the Data Conversion and Bottle Summary modules. Data Conversion converts raw data from the CTD to engineering units, storing the converted data in a .ros file. Bottle Summary reads the .ros file created by Data Conversion, derives dependent variables and writes a bottle data summary to a .btl file.;
Uncertainty: Pressure: initial accuracy = +/- 0.015% of full scale range; typical stability = 0.02% of full scale per year; master clock error contribution = Pressure 0.3 dbar (for 6800 meter depth-rated sensor).;
Quality flag convention: No data flags were applied to CTD data;
Method reference: Sea-Bird Scientific web site: http://www.seabird.com/sbe911plus-ctd;
Researcher name: Jan Newton;
Researcher institution: University of Washington Applied Physics Laboratory</gco:CharacterString>
              </gmd:description>
            </gmi:LE_ProcessStep>
          </gmd:processStep>
          <gmd:processStep>
            <gmi:LE_ProcessStep>
              <gmd:description>
                <gco:CharacterString>Parameter or Variable: CTD temperature, ITS-90 scale;
Abbreviation: CTDTMP_ITS90_DEG_C;
Unit: degrees celsius, ITS-90 scale;
Observation type: Water column profile;
In-situ / Manipulation / Response variable: in-situ observation;
Measured or calculated: Measured;
Sampling instrument: Sea-Bird Scientific SBE CTD (various models--see each cruise for details if needed);
Detailed sampling and analyzing information: This file contains the up cast data collected using the CTD package and any additional sensors attached to a rosette cage deployed on a research vessel. The up cast data correspond to when the bottles on the rosette cage were fired and water samples were collected. All up casts during the cruise are contained in this file and are sorted by station. CTD data were processed using Sea-Bird's proprietary data processing software using the Data Conversion and Bottle Summary modules. Data Conversion converts raw data from the CTD to engineering units, storing the converted data in a .ros file. Bottle Summary reads the .ros file created by Data Conversion, derives dependent variables and writes a bottle data summary to a .btl file.;
Uncertainty: Temperature: initial accuracy = +/- 0.001 degrees Celsius; typical stability = 0.0002 degrees Celsius per month; master clock error contribution = 0.00016 degrees Celsius;
Quality flag convention: CTDTMP_FLAG_W, WOCE CTDO data quality codes are used: 1 = not calibrated, 2 = acceptable measurement, 3 = questionable measurement, 4 = bad measurement, 5 = not reported, 6 = interpolated over a pressure interval larger than 2 dbar, 7 = despiked, 9 = not sampled. We note that during data processing with Sea Bird software, data alignment is improved to prevent spiking. All data quality codes contained in this data set were assigned after data processing and were given a value of 2 by default. Those flagged 3 represent values that are questionable due to being out of expected ranges or having inverted profile values from what would normally be expected in this region. Adjustments to quality codes were made after careful inspection of the data set after data processing.;
Method reference: Sea-Bird Scientific web site: http://www.seabird.com/sbe911plus-ctd;
Researcher name: Jan Newton;
Researcher institution: University of Washington Applied Physics Laboratory</gco:CharacterString>
              </gmd:description>
            </gmi:LE_ProcessStep>
          </gmd:processStep>
          <gmd:processStep>
            <gmi:LE_ProcessStep>
              <gmd:description>
                <gco:CharacterString>Parameter or Variable: CTD salinity;
Abbreviation: CTDSAL_PSS78;
Unit: 1978 Practical Salinity Scale;
Observation type: Water column profile;
In-situ / Manipulation / Response variable: in-situ observation;
Measured or calculated: Calculated from conductivity measurements.;
Sampling instrument: Sea-Bird Scientific SBE 4 Conductivity Sensor;
Detailed sampling and analyzing information: This file contains the up cast data collected using the CTD package and any additional sensors attached to a rosette cage deployed on a research vessel. The up cast data correspond to when the bottles on the rosette cage were fired and water samples were collected. All up casts during the cruise are contained in this file and are sorted by station. CTD data were processed using Sea-Bird's proprietary data processing software using the Data Conversion and Bottle Summary modules. Data Conversion converts raw data from the CTD to engineering units, storing the converted data in a .ros file. Bottle Summary reads the .ros file created by Data Conversion, derives dependent variables and writes a bottle data summary to a .btl file.;
Uncertainty: Conductivity: initial accuracy = +/- 0.0003 S/m; typical stability = 0.0003 S/m per month; master clock error contribution = 0.00005 S/m;
Quality flag convention: CTDSAL_FLAG_W, WOCE CTDO data quality codes are used: 1 = not calibrated, 2 = acceptable measurement, 3 = questionable measurement, 4 = bad measurement, 5 = not reported, 6 = interpolated over a pressure interval larger than 2 dbar, 7 = despiked, 9 = not sampled. We note that during data processing with Sea Bird software, data alignment is improved to prevent spiking. All data quality codes contained in this data set were assigned after data processing and were given a value of 2 by default. Those flagged 3 represent values that are questionable due to being out of expected ranges, having inverted profile values from what would normally be expected in this region, or being outliers on TA-S plots where TA values look as expected. Adjustments to quality codes were made after careful inspection of the data set after data processing.;
Method reference: Sea-Bird Scientific web site: http://www.seabird.com/sbe911plus-ctd;
Researcher name: Jan Newton;
Researcher institution: University of Washington Applied Physics Laboratory</gco:CharacterString>
              </gmd:description>
            </gmi:LE_ProcessStep>
          </gmd:processStep>
          <gmd:processStep>
            <gmi:LE_ProcessStep>
              <gmd:description>
                <gco:CharacterString>Parameter or Variable: Concentration of phosphate (PO4--) measured from discrete bottles;
Abbreviation: PHOSPHATE_UMOL_L;
Unit: micromoles per liter of seawater (umol/L or uM);
Observation type: Discrete measurements from samples collected in Niskin bottles on CTD casts;
In-situ / Manipulation / Response variable: in-situ observation;
Measured or calculated: Measured;
Calculation method and parameters: To convert units from umol per L to umol per kg, we divided PHOSPHATE_UMOL_L by the value of sigma theta (potential density anomaly, kg per m3) calculated for laboratory conditions (i.e. using laboratory temperature [22 degrees C] and sample salinity) and multiplied by 1000 L per m3. The content is also provided in umol per kg units, under the column header PHOSPHATE_UMOL_KG.;
Sampling instrument: Niskin bottle;
Analyzing instrument: Seal Analytical AA3;
Detailed sampling and analyzing information: From the Niskin bottle, seawater was drawn into 60 mL HDPE sample bottles to rinse the bottle and cap twice. Plungers were removed from 60 mL syringes with Nalgene filters attached (surfactant-free cellulose, 25 mm, 0.45 micron pore size) and rinsed twice with seawater from the Niskin. The syringe was filled with sample water from the Niskin. The plunger was inserted, the syringe inverted, and the filter removed to remove the air bubble. With the filter re-attached, about 5 mL of of sample water was filtered into sample bottle to rinse and then discarded. 45-50 mL of sample was filtered into sample bottle, such that it was less than 2/3 full. The cap was secured and the bottle frozen upright in a -10 degree Celsius freezer until analyzed. Analyses and calibration followed the protocols of the WOCE Hydrographic Program using a Seal Analytical AA3 (UNESCO 1994).;
Replicate information: No replicate samples were collected or analyzed.;
Uncertainty: Accreditation codes and detection limits: EPA 365.5_1.4_1997, NELAC Code WM920270, MDLs 0.014uM, 0.0004mg/L (from https://www.ocean.washington.edu/story/Marine+Chemistry+Laboratory).;
Quality flag convention: NUTRIENTS_FLAG_W, WOCE water sample quality codes are used: 2 = acceptable measurement, 3 = questionable measurement, 4 = bad measurement, 5 = not reported, 6 = mean of replicate measurements, 9 = sample not drawn for measurement from this Niskin bottle. Laboratory quality assurance procedures were followed, as detailed in UNESCO (1994). These QC codes were assigned values of 2 by default initially. However, where sample measurements were observed to be outliers in cross-plots with other variables or in transect depth profiles, the quality codes have been updated from a 2 to a 3 or 4 after close inspection of the profile at that station, including other parameters.;
Method reference: UNESCO (1994). Protocols for the joint global ocean flux study (JGOFS) core measurements. Vol. 29.;
Researcher name: Kathy Krogsland (for questions, contact Jan Newton);
Researcher institution: University of Washington School of Oceanography</gco:CharacterString>
              </gmd:description>
            </gmi:LE_ProcessStep>
          </gmd:processStep>
          <gmd:processStep>
            <gmi:LE_ProcessStep>
              <gmd:description>
                <gco:CharacterString>Parameter or Variable: Concentration of silicate (Si(OH)4, H4SiO4, SiO2, Sil) measured from discrete bottles;
Abbreviation: SILICATE_UMOL_L;
Unit: micromoles per liter of seawater (umol/L or uM);
Observation type: Discrete measurements from samples collected in Niskin bottles on CTD casts;
In-situ / Manipulation / Response variable: in-situ observation;
Measured or calculated: Measured;
Calculation method and parameters: To convert units from umol per L to umol per kg, we divided SILICATE_UMOL_L by the value of sigma theta (potential density anomaly, kg per m3) calculated for laboratory conditions (i.e. using laboratory temperature [22 degrees C] and sample salinity) and multiplied by 1000 L per m3. The content is also provided in umol per kg units, under the column header SILICATE_UMOL_KG.;
Sampling instrument: Niskin bottle;
Analyzing instrument: Seal Analytical AA3;
Detailed sampling and analyzing information: From the Niskin bottle, seawater was drawn into 60 mL HDPE sample bottles to rinse the bottle and cap twice. Plungers were removed from 60 mL syringes with Nalgene filters attached (surfactant-free cellulose, 25 mm, 0.45 micron pore size) and rinsed twice with seawater from the Niskin. The syringe was filled with sample water from the Niskin. The plunger was inserted, the syringe inverted, and the filter removed to remove the air bubble. With the filter re-attached, about 5 mL of of sample water was filtered into sample bottle to rinse and then discarded. 45-50 mL of sample was filtered into sample bottle, such that it was less than 2/3 full. The cap was secured and the bottle frozen upright in a -10 degree Celsius freezer until analyzed. Analyses and calibration followed the protocols of the WOCE Hydrographic Program using a Seal Analytical AA3 (UNESCO 1994).;
Replicate information: No replicate samples were collected or analyzed.;
Uncertainty: Accreditation codes and detection limits: EPA 366, NELAC Code WM920240, MDLs 0.23uM, 0.0063mg/L (from https://www.ocean.washington.edu/story/Marine+Chemistry+Laboratory).;
Quality flag convention: NUTRIENTS_FLAG_W, WOCE water sample quality codes are used: 2 = acceptable measurement, 3 = questionable measurement, 4 = bad measurement, 5 = not reported, 6 = mean of replicate measurements, 9 = sample not drawn for measurement from this Niskin bottle. Laboratory quality assurance procedures were followed, as detailed in UNESCO (1994). These QC codes were assigned values of 2 by default initially. However, where sample measurements were observed to be outliers in cross-plots with other variables or in transect depth profiles, the quality codes have been updated from a 2 to a 3 or 4 after close inspection of the profile at that station, including other parameters.;
Method reference: UNESCO (1994). Protocols for the joint global ocean flux study (JGOFS) core measurements. Vol. 29.;
Researcher name: Kathy Krogsland (for questions, contact Jan Newton);
Researcher institution: University of Washington School of Oceanography</gco:CharacterString>
              </gmd:description>
            </gmi:LE_ProcessStep>
          </gmd:processStep>
          <gmd:processStep>
            <gmi:LE_ProcessStep>
              <gmd:description>
                <gco:CharacterString>Parameter or Variable: Concentration of nitrate (NO3-) measured from discrete bottles;
Abbreviation: NITRATE_UMOL_L;
Unit: micromoles per liter of seawater (umol/L or uM);
Observation type: Discrete measurements from samples collected in Niskin bottles on CTD casts;
In-situ / Manipulation / Response variable: in-situ observation;
Measured or calculated: Measured;
Calculation method and parameters: To convert units from umol per L to umol per kg, we divided NITRATE_UMOL_L by the value of sigma theta (potential density anomaly, kg per m3) calculated for laboratory conditions (i.e. using laboratory temperature [22 degrees C] and sample salinity) and multiplied by 1000 L per m3. The content is also provided in umol per kg units, under the column header NITRATE_UMOL_KG.;
Sampling instrument: Niskin bottle;
Analyzing instrument: Analyses and calibration follow the protocols of the WOCE Hydrographic Program using a Seal Analytical AA3.;
Detailed sampling and analyzing information: From the Niskin bottle, seawater was drawn into 60 mL HDPE sample bottles to rinse the bottle and cap twice. Plungers were removed from 60 mL syringes with Nalgene filters attached (surfactant-free cellulose, 25 mm, 0.45 micron pore size) and rinsed twice with seawater from the Niskin. The syringe was filled with sample water from the Niskin. The plunger was inserted, the syringe inverted, and the filter removed to remove the air bubble. With the filter re-attached, about 5 mL of of sample water was filtered into sample bottle to rinse and then discarded. 45-50 mL of sample was filtered into sample bottle, such that it was less than 2/3 full. The cap was secured and the bottle frozen upright in a -10 degree Celsius freezer until analyzed. Analyses and calibration followed the protocols of the WOCE Hydrographic Program using a Seal Analytical AA3 (UNESCO 1994).;
Replicate information: No replicate samples were collected or analyzed.;
Uncertainty: Accreditation codes and detection limits: EPA 353.4_2_1997, NELAC Code 10068209, MDLs 0.288uM, 0.0040mg/L (from https://www.ocean.washington.edu/story/Marine+Chemistry+Laboratory).;
Quality flag convention: NUTRIENTS_FLAG_W, WOCE water sample quality codes are used: 2 = acceptable measurement, 3 = questionable measurement, 4 = bad measurement, 5 = not reported, 6 = mean of replicate measurements, 9 = sample not drawn for measurement from this Niskin bottle. Laboratory quality assurance procedures were followed, as detailed in UNESCO (1994). These QC codes were assigned values of 2 by default initially. However, where sample measurements were observed to be outliers in cross-plots with other variables or in transect depth profiles, the quality codes have been updated from a 2 to a 3 or 4 after close inspection of the profile at that station, including other parameters.;
Method reference: UNESCO (1994). Protocols for the joint global ocean flux study (JGOFS) core measurements. Vol. 29.;
Researcher name: Kathy Krogsland (for questions, contact Jan Newton);
Researcher institution: University of Washington School of Oceanography</gco:CharacterString>
              </gmd:description>
            </gmi:LE_ProcessStep>
          </gmd:processStep>
          <gmd:processStep>
            <gmi:LE_ProcessStep>
              <gmd:description>
                <gco:CharacterString>Parameter or Variable: Concentration of nitrite (NO2-) measured from discrete bottles.;
Abbreviation: NITRITE_UMOL_L;
Unit: micromoles per liter of seawater (umol/L or uM);
Observation type: Discrete measurements from samples collected in Niskin bottles on CTD casts;
In-situ / Manipulation / Response variable: in-situ observation;
Measured or calculated: Measured;
Calculation method and parameters: To convert units from umol per L to umol per kg, we divided NITRITE_UMOL_L by the value of sigma theta (potential density anomaly, kg per m3) calculated for laboratory conditions (i.e. using laboratory temperature [22 degrees C] and sample salinity) and multiplied by 1000 L per m3. The content is also provided in umol per kg units, under the column header NITRITE_UMOL_KG.;
Sampling instrument: Niskin bottle;
Analyzing instrument: Seal Analytical AA3;
Detailed sampling and analyzing information: From the Niskin bottle, seawater was drawn into 60 mL HDPE sample bottles to rinse the bottle and cap twice. Plungers were removed from 60 mL syringes with Nalgene filters attached (surfactant-free cellulose, 25 mm, 0.45 micron pore size) and rinsed twice with seawater from the Niskin. The syringe was filled with sample water from the Niskin. The plunger was inserted, the syringe inverted, and the filter removed to remove the air bubble. With the filter re-attached, about 5 mL of of sample water was filtered into sample bottle to rinse and then discarded. 45-50 mL of sample was filtered into sample bottle, such that it was less than 2/3 full. The cap was secured and the bottle frozen upright in a -10 degree Celsius freezer until analyzed. Analyses and calibration followed the protocols of the WOCE Hydrographic Program using a Seal Analytical AA3 (UNESCO 1994).;
Replicate information: No replicate samples were collected or analyzed.;
Uncertainty: Accreditation codes and detection limits: EPA 353.4_2_1997, NELAC Code 10068209, MDLs 0.011uM, 0.0002mg/L (from https://www.ocean.washington.edu/story/Marine+Chemistry+Laboratory).;
Quality flag convention: NUTRIENTS_FLAG_W, WOCE water sample quality codes are used: 2 = acceptable measurement, 3 = questionable measurement, 4 = bad measurement, 5 = not reported, 6 = mean of replicate measurements, 9 = sample not drawn for measurement from this Niskin bottle. Laboratory quality assurance procedures were followed, as detailed in UNESCO (1994). These QC codes were assigned values of 2 by default initially. However, where sample measurements were observed to be outliers in cross-plots with other variables or in transect depth profiles, the quality codes have been updated from a 2 to a 3 or 4 after close inspection of the profile at that station, including other parameters.;
Method reference: UNESCO (1994). Protocols for the joint global ocean flux study (JGOFS) core measurements. Vol. 29.;
Researcher name: Kathy Krogsland (for questions, contact Jan Newton);
Researcher institution: University of Washington School of Oceanography</gco:CharacterString>
              </gmd:description>
            </gmi:LE_ProcessStep>
          </gmd:processStep>
          <gmd:processStep>
            <gmi:LE_ProcessStep>
              <gmd:description>
                <gco:CharacterString>Parameter or Variable: Concentration of ammonium (NH4+) measured from discrete bottles;
Abbreviation: AMMONIUM_UMOL_L;
Unit: micromoles per liter of seawater (umol/L or uM);
Observation type: Discrete measurements from samples collected in Niskin bottles on CTD casts;
In-situ / Manipulation / Response variable: in-situ observation;
Measured or calculated: Measured;
Calculation method and parameters: To convert units from umol per L to umol per kg, we divided AMMONIUM_UMOL_L by the value of sigma theta (potential density anomaly, kg per m3) calculated for laboratory conditions (i.e. using laboratory temperature [22 degrees C] and sample salinity) and multiplied by 1000 L per m3. The ammonium content is also provided in umol per kg units, under the column header AMMONIUM_UMOL_KG.;
Sampling instrument: Niskin bottle;
Analyzing instrument: Seal Analytical AA3;
Detailed sampling and analyzing information: From the Niskin bottle, seawater was drawn into 60 mL HDPE sample bottles to rinse the bottle and cap twice. Plungers were removed from 60 mL syringes with Nalgene filters attached (surfactant-free cellulose, 25 mm, 0.45 micron pore size) and rinsed twice with seawater from the Niskin. The syringe was filled with sample water from the Niskin. The plunger was inserted, the syringe inverted, and the filter removed to remove the air bubble. With the filter re-attached, about 5 mL of of sample water was filtered into sample bottle to rinse and then discarded. 45-50 mL of sample was filtered into sample bottle, such that it was less than 2/3 full. The cap was secured and the bottle frozen upright in a -10 degree Celsius freezer until analyzed. Analyses and calibration followed the protocols of the WOCE Hydrographic Program using a Seal Analytical AA3 (UNESCO 1994).;
Replicate information: No replicate samples were collected or analyzed.;
Uncertainty: Accreditation codes and detection limits: EPA 349, NELAC Code WM920220, MDLs 0.047uM, 0.0007mg/L (from https://www.ocean.washington.edu/story/Marine+Chemistry+Laboratory).;
Quality flag convention: NUTRIENTS_FLAG_W, WOCE water sample quality codes are used: 2 = acceptable measurement, 3 = questionable measurement, 4 = bad measurement, 5 = not reported, 6 = mean of replicate measurements, 9 = sample not drawn for measurement from this Niskin bottle. Laboratory quality assurance procedures were followed, as detailed in UNESCO (1994). These QC codes were assigned values of 2 by default initially. However, where sample measurements were observed to be outliers in cross-plots with other variables or in transect depth profiles, the quality codes have been updated from a 2 to a 3 or 4 after close inspection of the profile at that station, including other parameters.;
Method reference: UNESCO (1994). Protocols for the joint global ocean flux study (JGOFS) core measurements. Vol. 29.;
Researcher name: Kathy Krogsland (for questions, contact Jan Newton);
Researcher institution: University of Washington School of Oceanography</gco:CharacterString>
              </gmd:description>
            </gmi:LE_ProcessStep>
          </gmd:processStep>
          <gmd:processStep>
            <gmi:LE_ProcessStep>
              <gmd:description>
                <gco:CharacterString>Parameter or Variable: Potential density anomaly, also known as sigma theta, referenced to 0 db pressure;
Abbreviation: SIGMATHETA_KG_M3;
Unit: kilograms per meter cubed (kg/m3);
Observation type: Water column profile;
In-situ / Manipulation / Response variable: in-situ observation;
Measured or calculated: Calculated;
Calculation method and parameters: Calculated within Sea-Bird Scientific's SeaSAVE or SBE Data Processing software using TEOS-10 equations for cruises after 2013 and EOS-80 equations prior to 2013 (per web site: http://www.seabird.com/software/sbe-data-processing).;
Method reference: http://www.oc.nps.edu/nom/day1/parta.html, http://www.seabird.com/software/sbe-data-processing;
Researcher name: Jan Newton;
Researcher institution: University of Washington Applied Physics Laboratory</gco:CharacterString>
              </gmd:description>
            </gmi:LE_ProcessStep>
          </gmd:processStep>
          <gmd:processStep>
            <gmi:LE_ProcessStep>
              <gmd:description>
                <gco:CharacterString>Parameter or Variable: Longitude in decimal degrees East (negative for Western Hemisphere);
Abbreviation: LONGITUDE_DEC;
Measured or calculated:</gco:CharacterString>
              </gmd:description>
            </gmi:LE_ProcessStep>
          </gmd:processStep>
          <gmd:processStep>
            <gmi:LE_ProcessStep>
              <gmd:description>
                <gco:CharacterString>Parameter or Variable: Latitude in decimal degrees North (negative for Southern Hemisphere);
Abbreviation: LATITUDE_DEC;
Measured or calculated:</gco:CharacterString>
              </gmd:description>
            </gmi:LE_ProcessStep>
          </gmd:processStep>
          <gmd:processStep>
            <gmi:LE_ProcessStep>
              <gmd:description>
                <gco:CharacterString>Parameter or Variable: Station number, corresponds to the numerical value after the P in PRISM Station numbers found at http://nvs.nanoos.org/CruiseSalish;
Abbreviation: STATION_NO;
Measured or calculated:</gco:CharacterString>
              </gmd:description>
            </gmi:LE_ProcessStep>
          </gmd:processStep>
          <gmd:processStep>
            <gmi:LE_ProcessStep>
              <gmd:description>
                <gco:CharacterString>Parameter or Variable: Niskin bottle number. The sequence of trip depths starts with deepest bottle trip = 1.;
Abbreviation: NISKIN_NO;
Measured or calculated:</gco:CharacterString>
              </gmd:description>
            </gmi:LE_ProcessStep>
          </gmd:processStep>
          <gmd:processStep>
            <gmi:LE_ProcessStep>
              <gmd:description>
                <gco:CharacterString>Parameter or Variable: Date (mm/dd/yyyy) in Coordinated Universal Time (UTC);
Abbreviation: DATE_UTC;
Measured or calculated:</gco:CharacterString>
              </gmd:description>
            </gmi:LE_ProcessStep>
          </gmd:processStep>
          <gmd:processStep>
            <gmi:LE_ProcessStep>
              <gmd:description>
                <gco:CharacterString>Parameter or Variable: Time (HH:mm:ss) in Coordinated Universal Time (UTC). NB: time for Station 128 reflects CTD system power up, not individual Niskin bottle fire times.;
Abbreviation: TIME_UTC;
Measured or calculated:</gco:CharacterString>
              </gmd:description>
            </gmi:LE_ProcessStep>
          </gmd:processStep>
          <gmd:processStep>
            <gmi:LE_ProcessStep>
              <gmd:description>
                <gco:CharacterString>Parameter or Variable: DATE_LOCAL;
Abbreviation: DATE_LOCAL;
Measured or calculated:</gco:CharacterString>
              </gmd:description>
            </gmi:LE_ProcessStep>
          </gmd:processStep>
          <gmd:processStep>
            <gmi:LE_ProcessStep>
              <gmd:description>
                <gco:CharacterString>Parameter or Variable: Time (HH:mm:ss) in Local Time. NB: time for Station 128 reflects CTD system power up, not individual Niskin bottle fire times.;
Abbreviation: TIME_LOCAL;
Measured or calculated:</gco:CharacterString>
              </gmd:description>
            </gmi:LE_ProcessStep>
          </gmd:processStep>
          <gmd:processStep>
            <gmi:LE_ProcessStep>
              <gmd:description>
                <gco:CharacterString>Parameter or Variable: Recommended oxygen content;
Abbreviation: RECOMMENDED_OXYGEN_UMOL_KG;
Unit: micromoles per kilogram of seawater (umol/kg-SW);
Observation type: Water column profile;
In-situ / Manipulation / Response variable: in-situ observation;
Measured or calculated: Measured;
Calculation method and parameters: This is a merged parameter consisting of all high-quality OXYGEN_UMOL_KG data (i.e., those with QC flags of 2), with gaps filled by high-quality CTDOXY_UMOL_KG_ADJ measurements.;
Method reference: Alin, S. R., Newton, J. A., Feely, R. A., Greeley, D., Curry, B., Herndon, J., &amp; Warner, M. (2024). A decade-long cruise time series (2008–2018) of physical and biogeochemical conditions in the southern Salish Sea, North America. In Earth System Science Data (Vol. 16, Issue 2, pp. 837–865). Copernicus GmbH. https://doi.org/10.5194/essd-16-837-2024;
Researcher name: Simone Alin;
Researcher institution: NOAA Pacific Marine Environmental Laboratory</gco:CharacterString>
              </gmd:description>
            </gmi:LE_ProcessStep>
          </gmd:processStep>
          <gmd:processStep>
            <gmi:LE_ProcessStep>
              <gmd:description>
                <gco:CharacterString>Parameter or Variable: Aragonite and calcite saturation state values (OmegaAragonite and OmegaCalcite, respectively) calculated from DIC_UMOL_KG and TA_UMOL_KG at in situ temperatures and pressures;
Abbreviation: OmegaAragonite_Lueker,OmegaAragonite_Waters, OmegaCalcite_Lueker, and OmegaCalcite_Waters;
Measured or calculated: CALCULATED;
Calculation method and parameters: CALCULATED;
Uncertainty: ±4.9% for OmegaAragonite per Orr et al. 2018, including both input variable uncertainties and uncertainties associated with dissociation constants;
Quality flag convention: All data flags for input parameters used for calculating OmegaAragonite and OmegaCalcite were QC 2 ("acceptable"). Therefore, the calculated OmegaAragonite and OmegaCalcite values should also have QC flags of 2.;
Method reference: Gattuso et al. (2023);
Researcher name: Simone Alin;
Researcher institution: NOAA Pacific Marine Environmental Laboratory</gco:CharacterString>
              </gmd:description>
            </gmi:LE_ProcessStep>
          </gmd:processStep>
        </gmd:LI_Lineage>
      </gmd:lineage>
    </gmd:DQ_DataQuality>
  </gmd:dataQualityInfo>
  <gmd:metadataMaintenance>
    <gmd:MD_MaintenanceInformation>
      <gmd:maintenanceAndUpdateFrequency>
        <gmd:MD_MaintenanceFrequencyCode codeList="https://data.noaa.gov/resources/iso19139/schema/resources/Codelist/gmxCodelists.xml#MD_MaintenanceFrequencyCode" codeListValue="asNeeded">asNeeded</gmd:MD_MaintenanceFrequencyCode>
      </gmd:maintenanceAndUpdateFrequency>
      <gmd:maintenanceNote>
        <gco:CharacterString>Metadata are developed, maintained and distributed by NCEI. Updates are performed as needed to maintain currentness.</gco:CharacterString>
      </gmd:maintenanceNote>
      <gmd:contact>
        <gmd:CI_ResponsibleParty>
          <gmd:organisationName>
            <gco:CharacterString>NOAA National Centers for Environmental Information</gco:CharacterString>
          </gmd:organisationName>
          <gmd:role>
            <gmd:CI_RoleCode codeList="https://data.noaa.gov/resources/iso19139/schema/resources/Codelist/gmxCodelists.xml#CI_RoleCode" codeListValue="custodian">custodian</gmd:CI_RoleCode>
          </gmd:role>
        </gmd:CI_ResponsibleParty>
      </gmd:contact>
    </gmd:MD_MaintenanceInformation>
  </gmd:metadataMaintenance>
  <gmi:acquisitionInformation>
    <gmi:MI_AcquisitionInformation id="AMS">
      <gmi:instrument>
        <gmi:MI_Instrument id="inst_be58">
          <gmi:identifier>
            <gmd:MD_Identifier>
              <gmd:code>
                <gco:CharacterString>carbon dioxide (CO2) gas analyzer</gco:CharacterString>
              </gmd:code>
            </gmd:MD_Identifier>
          </gmi:identifier>
          <gmi:type>
            <gco:CharacterString>carbon dioxide (CO2) gas analyzer</gco:CharacterString>
          </gmi:type>
          <gmi:description>
            <gco:CharacterString>measures gaseous carbon dioxide

Carbon dioxide gas analyzer has often been referred to as LI-COR, because a lot of researchers choose to use products manufactured by LI-COR incorporation for their carbon dioxide measurement. The main component of a carbon dioxide analyzer is a nondispersive infrared (NDIR) spectroscopic sensors to detect CO2 in a gaseous environment by its characteristic absorption.

Carbon dioxide (CO2) gas analyzer works together with carbon dioxide (CO2) equilibrator (insttypes_id 184) to measure carbon dioxide in the water.

To measure water carbon dioxide, water needs to be continuously supplied to a showerhead inside an equilibrator. As the water flows through the equilibrator chamber, dissolved carbon dioxide exchanges quickly with air in the headspace. This air is then sampled by the carbon dioxide analyzer to determine the mole fraction of CO2 in water.</gco:CharacterString>
          </gmi:description>
        </gmi:MI_Instrument>
      </gmi:instrument>
      <gmi:instrument>
        <gmi:MI_Instrument id="inst_bee7">
          <gmi:identifier>
            <gmd:MD_Identifier>
              <gmd:code>
                <gco:CharacterString>CTD</gco:CharacterString>
              </gmd:code>
            </gmd:MD_Identifier>
          </gmi:identifier>
          <gmi:type>
            <gco:CharacterString>CTD</gco:CharacterString>
          </gmi:type>
          <gmi:description>
            <gco:CharacterString>Conductivity-Temperature-Depth probe</gco:CharacterString>
          </gmi:description>
        </gmi:MI_Instrument>
      </gmi:instrument>
      <gmi:instrument>
        <gmi:MI_Instrument id="inst_be3d">
          <gmi:identifier>
            <gmd:MD_Identifier>
              <gmd:code>
                <gco:CharacterString>Niskin bottle</gco:CharacterString>
              </gmd:code>
            </gmd:MD_Identifier>
          </gmi:identifier>
          <gmi:type>
            <gco:CharacterString>Niskin bottle</gco:CharacterString>
          </gmi:type>
          <gmi:description>
            <gco:CharacterString>Device for obtaining samples of seawater at a specific depth

Why special entry for Niskin bottle but no entry for Nansen bottle?</gco:CharacterString>
          </gmi:description>
        </gmi:MI_Instrument>
      </gmi:instrument>
      <gmi:instrument>
        <gmi:MI_Instrument id="inst_bef4">
          <gmi:identifier>
            <gmd:MD_Identifier>
              <gmd:code>
                <gco:CharacterString>oxygen sensor</gco:CharacterString>
              </gmd:code>
            </gmd:MD_Identifier>
          </gmi:identifier>
          <gmi:type>
            <gco:CharacterString>oxygen sensor</gco:CharacterString>
          </gmi:type>
          <gmi:description>
            <gco:CharacterString>Any instrument that measures oxygen content in a compound.</gco:CharacterString>
          </gmi:description>
        </gmi:MI_Instrument>
      </gmi:instrument>
      <gmi:instrument>
        <gmi:MI_Instrument id="inst_bea4">
          <gmi:identifier>
            <gmd:MD_Identifier>
              <gmd:code>
                <gco:CharacterString>salinometer</gco:CharacterString>
              </gmd:code>
            </gmd:MD_Identifier>
          </gmi:identifier>
          <gmi:type>
            <gco:CharacterString>salinometer</gco:CharacterString>
          </gmi:type>
          <gmi:description>
            <gco:CharacterString>generic salinometer

use salinometer when the instrument type used is unclear but the data include salinity measurements</gco:CharacterString>
          </gmi:description>
        </gmi:MI_Instrument>
      </gmi:instrument>
      <gmi:instrument>
        <gmi:MI_Instrument id="inst_be41">
          <gmi:identifier>
            <gmd:MD_Identifier>
              <gmd:code>
                <gco:CharacterString>temperature sensor</gco:CharacterString>
              </gmd:code>
            </gmd:MD_Identifier>
          </gmi:identifier>
          <gmi:type>
            <gco:CharacterString>temperature sensor</gco:CharacterString>
          </gmi:type>
          <gmi:description>
            <gco:CharacterString>A sensor used to measure temperature.</gco:CharacterString>
          </gmi:description>
        </gmi:MI_Instrument>
      </gmi:instrument>
      <gmi:instrument>
        <gmi:MI_Instrument id="inst_be28">
          <gmi:identifier>
            <gmd:MD_Identifier>
              <gmd:code>
                <gco:CharacterString>titrator</gco:CharacterString>
              </gmd:code>
            </gmd:MD_Identifier>
          </gmi:identifier>
          <gmi:type>
            <gco:CharacterString>titrator</gco:CharacterString>
          </gmi:type>
          <gmi:description>
            <gco:CharacterString>titrator</gco:CharacterString>
          </gmi:description>
        </gmi:MI_Instrument>
      </gmi:instrument>
      <gmi:platform>
        <gmi:MI_Platform id="plat_baae">
          <gmi:identifier>
            <gmd:MD_Identifier>
              <gmd:code>
                <gco:CharacterString>VARIOUS CHARTERED VESSELS</gco:CharacterString>
              </gmd:code>
            </gmd:MD_Identifier>
          </gmi:identifier>
          <gmi:description>
            <gco:CharacterString>VARIOUS CHARTERED VESSELS</gco:CharacterString>
          </gmi:description>
          <gmi:instrument gco:nilReason="missing" />
        </gmi:MI_Platform>
      </gmi:platform>
    </gmi:MI_AcquisitionInformation>
  </gmi:acquisitionInformation>
</gmi:MI_Metadata>