http://lod.bco-dmo.org/id/dataset/1002581
eng; USA
utf8
dataset
Highest level of data collection, from a common set of sensors or instrumentation, usually within the same research project
Biological and Chemical Oceanography Data Management Office (BCO-DMO)
Unavailable
508-289-2009
WHOI MS#36
Woods Hole
MA
02543
USA
info@bco-dmo.org
http://www.bco-dmo.org
Monday - Friday 8:00am - 5:00pm
For questions regarding this resource, please contact BCO-DMO via the email address provided.
pointOfContact
2026-07-15
ISO 19115-2 Geographic Information - Metadata - Part 2: Extensions for Imagery and Gridded Data
ISO 19115-2:2009(E)
GP17-ANT carbonate system data from the GP17-OCE and GP17-ANT Inorganic Carbon,GP17-ANT projects of the U.S. GEOTRACES program
2026-07-21
publication
2026-07-21
revision
BCO-DMO Linked Data URI
2026-07-21
creation
http://lod.bco-dmo.org/id/dataset/1002581
Ryan J. Woosley
Massachusetts Institute of Technology
principalInvestigator
Biological and Chemical Oceanography Data Management Office (BCO-DMO)
Unavailable
508-289-2009
WHOI MS#36
Woods Hole
MA
02543
USA
info@bco-dmo.org
http://www.bco-dmo.org
Monday - Friday 8:00am - 5:00pm
For questions regarding this resource, please contact BCO-DMO via the email address provided.
publisher
Cite this dataset as: Woosley, R. J., Bruno, J. A., Neithardt, D., Lahn, L. (2026) GP17-ANT carbonate system data. Biological and Chemical Oceanography Data Management Office (BCO-DMO). (Version 1) Version Date 2026-07-21 [if applicable, indicate subset used]. http://lod.bco-dmo.org/id/dataset/1002581 [access date]
GP17-ANT carbonate system data Dataset Description: Methods and Sampling: <p>All samples were collected and analyzed following best practices guidelines (Dickeson et al. 2007). Dissolved inorganic carbon (DIC) was collected in 250-milliliter (mL) borosilicate glass reagent bottles and sealed using Apiezon L grease and a rubber band held in place with a plastic hose clamp. The total alkalinity (TA) and pH<sub>T</sub> were collected in 150 mL borosilicate glass serum bottles and sealed with a butyl-rubber cap and aluminum seal. All bottles were filled in the same manner. A silicone tube was attached to the Niskin valve. A small amount of water was added to the bottle, and the bottle was swirled to cover all surfaces and dumped out. This rinse was repeated a total of three times. Then the tube was placed near the bottom of the bottle and filled. The tube was tapped against the bottom to dislodge any bubbles, and care was taken to overflow any bubbles. Once full, the water was allowed to overflow for at least half the volume of the bottle (as estimated by time to fill the bottle) and all visible bubbles were gone. Overflow water was used to rinse the caps. With the water still flowing, the tube was gently, but quickly, removed leaving the bottle full to the brim. A pipette was then used to remove a precise amount of water, leaving ~1% headspace once the bottle was capped. After removing the water for headspace, a saturated mercuric chloride solution was added to a total volume of 0.04% of the sample. The DIC was then capped with a glass stopper with Apiezon L grease, twisting the cap to ensure even distribution of grease, creating an airtight seal. A rubber band and hose clamp were then placed on the cap to keep it in place. For TA and pHt, the rubber stopper was inserted and an aluminum seal was crimped on top. Once sealed, all bottles were gently inverted several times in order to mix the mercuric chloride. The entire collection process was completed as quickly as possible, but with care, to minimize any gas exchange. After collection, DIC/TA bottles were placed in plastic crates with protective foam and stored in a refrigerated shipping van until arrival in port. The samples were shipped back to the laboratory without temperature control and stored in the laboratory at room temperature until analysis. The pH<sub>T</sub> samples were immediately placed in a 20-degree Celsius (°C) water bath to equilibrate the temperature before analysis.</p>
<p>The pH<sub>T</sub> at 20°C was analyzed within 6 hours of collection. The samples were allowed a minimum of 2 hours for temperature equilibration before analysis was started. The pH<sub>T</sub> was then measured spectrophotometrically with purified metacresol purple (mCP) dye (Woosley lab batch 4) obtained from the laboratory of Robert H. Byrne (University of South Florida), using a custom-designed automated system similar to that of Carter et al. (2013). The instrument uses a 10 mL Kloehn syringe pump to draw the sample from the bottle, rinse the flow-through 10-centimeter (cm) quartz micro-volume spectrophotometric cell (Starna, Inc.), add and mix the mCP indicator, and finally rinse the cell after analysis. An Agilent 8454 UV/VIS spectrophotometer was used to take the blank, and full spectra with mCP. The absorbances at 434, 578, 730, and 488 nanometers (nm) were used for calculations. The equations of Liu et al. (2011) were used to calculate pH<sub>T</sub>, and the isobestic absorbance at 488 nm was used to determine the indicator perturbation adjustment following the method described in Carter et al. (2013). The dye perturbation slope and intercept were -0.0649 and 0.0781, respectively. Duplicate samples, Certified reference material provided by the laboratory of Andrew G. Dickson (University of California, San Diego), and TRIS buffers prepared according to Paulsen and Dickson (2020) were used to check precision and "accuracy". The mean absolute difference between duplicate samples was 0.0013 ± 0.0008 (N=27). The mean and standard deviation of CRM (Batch 199) were 7.9115 ± 0.0013 (N =15), and for TRIS (Woosley Lab Batch 5) 8.21514 ± 0.0016 (N = 17).</p>
<p>The DIC/TA samples were stored in a refrigerated van on deck after collection, and shipped (without temperature control) to the land-based laboratory at MIT (via USAP in Port Hueneme, California), and then stored at room temperature in a closet until analysis. Analyses were performed between 8 and 20 months after the end of the cruise. All TA samples were analyzed first. Then DIC was analyzed with several analyses of TA being performed immediately afterwards from the DIC bottle as a check on the sample collected for TA.</p>
<p>DIC was analyzed using a custom-designed DIC extractor (DICE) built by NOAA PMEL (Pacific Marine Environmental Laboratory). It is a modern version of the original SOMMA system (Johnson 1992) and follows the methods described in Dickson et al. (2007) in SOP 2. Analysis is performed at 20°C. The instrument uses a calibrated pipette to precisely dispense the volume of sample into a stripper chamber where 8.5% phosphoric acid had been added. The acid converted all the DIC to CO<sub>2</sub> gas. A pure N<sub>2</sub> carrier gas then carried the evolved CO<sub>2</sub> through a condensor to remove water vapor followed by a silica gel (Orbo Tube, Millipore-Sigma, Inc.) to remove any organic acids and finally into the coulometer (UIC, Inc.) for detection. The instrument was calibrated at the start of each coulometer cell (1 per day) with a blank, 2 pure (99.999% CO<sub>2</sub>) gas loops, each run at least twice, and certified reference material (CRM) provided by the laboratory of Andrew G. Dickson (University of California, San Diego). Sample values were adjusted to the CRM value for that day using a constant offset from the certified value. Two duplicates per station were analyzed to assess precision. The mean and standard deviation of the absolute difference between duplicates was 1.6 ± 1.1 (N = 29). CRM Batch 216 was used, the overall mean difference from the certified (measured - certified) value was -2.55 ± 1.47 (N = 51).</p>
<p>TA was analyzed using an instrument custom-designed and built by the laboratory of Andrew G. Dickson (UCSD) and described in Dickson et al. (2003, 2007). Analysis was performed at 20°C. A sample of approximately 100 to 130 grams (g) is weighed and added to a clean, dry water-jacketed beaker with a stir bar, and a cap with an Ecotrode electrode (Metrohm, AG), thermometer, acid line, and air line is placed on top. A computer-controlled dosimat then adds enough acid to reach a pH of ~3.5. The sample is then stirred (450 rpm) and bubbled with lab air for 300 seconds to drive off evolved CO<sub>2</sub>. Then 15-20 fine additions of 50 microliters (µL) of acid are added and voltages and temperatures recorded. Once complete, a non-linear least squares fitting method is used to calculate the TA as well as calibrate the E<sup>0</sup> of the electrode. The fitting method is described in Dickson et al. (2003). A CRM was analyzed at the beginning and end of each day. Sample values were NOT adjusted to the certified value. Two duplicates per station were analyzed to assess precision. In addition, several bottles collected for DIC were also analyzed for TA as a check and to provide additional duplicate measurements. These samples were analyzed immediately after analyzing DIC (generally within 15-20 minutes). The acid was ~0.1 N HCl prepared in ~0.6 M NaCl to match the approximate ionic strength of seawater. The exact concentration was calibrated by borax titration following the method of Kolthoff (1926). The mean and standard deviation of the absolute difference between duplicates was 2.43 ± 1.65 (N = 153). The mean and standard deviation of the CRM Batch 216 difference from the certified value (measured - certified) was -0.10 ± 2.09 (N = 116).</p>
Funding provided by NSF Division of Ocean Sciences (NSF OCE) Award Number: OCE-2148468 Award URL: https://www.nsf.gov/awardsearch/show-award?AWD_ID=2148468
onGoing
Ryan J. Woosley
Massachusetts Institute of Technology
617-253-1984
77 Massachusetts Ave Bldg. 54-1414
Cambridge
MA
02139
USA
rwoosley@mit.edu
pointOfContact
asNeeded
Dataset Version: 1
Unknown
Station_ID
Event_ID
Gear_ID
Start_Date_UTC
Start_Time_UTC
Start_ISO_DateTime_UTC
Start_Latitude
Start_Longitude
Rosette_Position
Sample_ID
Sample_Depth
PH_TMP_BOTTLE_ivhgkg
SD1_PH_TMP_BOTTLE_ivhgkg
Flag_PH_TMP_BOTTLE_ivhgkg
DIC_D_CONC_BOTTLE_2nk2fs
SD1_DIC_D_CONC_BOTTLE_2nk2fs
Flag_DIC_D_CONC_BOTTLE_2nk2fs
TALK_D_CONC_BOTTLE_bjyhik
SD1_TALK_D_CONC_BOTTLE_bjyhik
Flag_TALK_D_CONC_BOTTLE_bjyhik
PH_TOT_BOTTLE_5rqziy
SD1_PH_TOT_BOTTLE_5rqziy
Flag_PH_TOT_BOTTLE_5rqziy
custom-designed DIC extractor (DICE)
Niskin bottles
Agilent 8454 UV/VIS spectrophotometer
custom-built open-cell potentiometric titrator
theme
None, User defined
station
event
instrument
date
time of day
ISO_DateTime_UTC
latitude
longitude
bottle
sample identification
depth
temperature of sample or a generic measurement (not in-situ water temp)
quality flag
dissolved inorganic Carbon
total alkalinity (TA)
pH
featureType
BCO-DMO Standard Parameters
CO2 Coulometer
Niskin bottle
Spectrophotometer
Titrator
instrument
BCO-DMO Standard Instruments
NBP2401
service
Deployment Activity
Punta Arenas, Chile to Lyttelton, New Zealand
place
Locations
otherRestrictions
otherRestrictions
Access Constraints: none. Use Constraints: Please follow guidelines at: http://www.bco-dmo.org/terms-use Distribution liability: Under no circumstances shall BCO-DMO be liable for any direct, incidental, special, consequential, indirect, or punitive damages that result from the use of, or the inability to use, the materials in this data submission. If you are dissatisfied with any materials in this data submission your sole and exclusive remedy is to discontinue use.
U.S. GEOTRACES
http://www.geotraces.org/
U.S. GEOTRACES
GEOTRACES is a SCOR sponsored program; and funding for program infrastructure development is provided by the U.S. National Science Foundation.
GEOTRACES gained momentum following a special symposium, S02: Biogeochemical cycling of trace elements and isotopes in the ocean and applications to constrain contemporary marine processes (GEOSECS II), at a 2003 Goldschmidt meeting convened in Japan. The GEOSECS II acronym referred to the Geochemical Ocean Section Studies To determine full water column distributions of selected trace elements and isotopes, including their concentration, chemical speciation, and physical form, along a sufficient number of sections in each ocean basin to establish the principal relationships between these distributions and with more traditional hydrographic parameters;
* To evaluate the sources, sinks, and internal cycling of these species and thereby characterize more completely the physical, chemical and biological processes regulating their distributions, and the sensitivity of these processes to global change; and
* To understand the processes that control the concentrations of geochemical species used for proxies of the past environment, both in the water column and in the substrates that reflect the water column.
GEOTRACES will be global in scope, consisting of ocean sections complemented by regional process studies. Sections and process studies will combine fieldwork, laboratory experiments and modelling. Beyond realizing the scientific objectives identified above, a natural outcome of this work will be to build a community of marine scientists who understand the processes regulating trace element cycles sufficiently well to exploit this knowledge reliably in future interdisciplinary studies.
Expand "Projects" below for information about and data resulting from individual US GEOTRACES research projects.
U.S. GEOTRACES
largerWorkCitation
program
US GEOTRACES GP17-OCE and GP17-ANT: Inorganic Carbon Cycling in the South Pacific and Southern Oceans by Direct Measurement
https://osprey.bco-dmo.org/project/890561
US GEOTRACES GP17-OCE and GP17-ANT: Inorganic Carbon Cycling in the South Pacific and Southern Oceans by Direct Measurement
<p><em><strong>NSF Award Abstract</strong></em><br />
The oceans help to slow climate change by absorbing about a quarter of the carbon dioxide (CO2) produced by burning of fossil fuels and other human activities. The Pacific and Southern Oceans are known to take up and store significant amounts of anthropogenic CO2, but many questions regarding the amount, variability, and biogeochemical and ecological impacts remain unanswered. This research will focus on answering some of those questions in two areas of the Pacific by analyzing samples for total CO2, total alkalinity, and pH on two GEOTRACES cruises, GP17-OCE and GP17-ANT. The project will support several undergraduate student researchers and create educational modules on ocean acidification for general public and K-12 students.</p>
<p>On the GP17-OCE expedition in the south Pacific, sub-decadal scale variability in the uptake of CO2 and resulting decrease in pH (termed ocean acidification) will be examined by comparing data collected on this expedition with data from prior occupations of the line in 1991, 2005 and 2014. An extended multilinear regression technique will be used to separate natural variability from human induced changes. The second expedition, GP17-ANT, covers the Amundsen Sea, an area with few prior carbon measurements. This sea is perennially ice-covered with several seasonal polynyas (areas of open water surrounded by sea ice) and exhibits complex water circulation making the contribution to the global carbon cycle uncertain. The data collected from this expedition will examine several hypotheses regarding how carbon is taken up, mixed, and recirculated in the region, how glacial ice melt, sea ice, and biological productivity influence the carbon cycle, and provide baseline measurements against future data to determine changes in the carbon cycle of the region over time. Both expeditions will leverage the myriad of other parameters being measured, particularly trace metals such as iron and zinc, to examine how cycling of carbon and trace metals are interlinked through pH.</p>
<p>This award reflects NSF's statutory mission and has been deemed worthy of support through evaluation using the Foundation's intellectual merit and broader impacts review criteria.</p>
GP17-OCE and GP17-ANT Inorganic Carbon
largerWorkCitation
project
US GEOTRACES GP17 Section: Amundsen Sea Sector of the Antarctic Continental Margin (GP17-ANT)
https://www.geotraces.org/
US GEOTRACES GP17 Section: Amundsen Sea Sector of the Antarctic Continental Margin (GP17-ANT)
<p>U.S. GEOTRACES extended its meridional transect, initiated on the 2018 GP15 Alaska-Tahiti expedition, south to the Antarctic ice edge and then east to Chile with GP17-OCE (December 2022 - January 2023). Because of the potentially important trace elements and isotopes (TEIs) inputs and transformations occurring in Antarctic waters and shelves, GP17 also had a second leg, GP17-ANT (November 29, 2023 - January 30, 2024) into coastal and shelf waters of Antarctica’s Amundsen Sea. Further information is available on the <a href="https://usgeotraces.ldeo.columbia.edu/content/gp17-ant" target="_blank">US GEOTRACES website</a>.</p>
<p><em>NSF Project Title:</em> Collaborative Research: Management and Implementation of US GEOTRACES GP17 Section: Amundsen Sea Sector of the Antarctic Continental Margin (GP17-ANT)</p>
<p><em>NSF Award Abstract:</em><br />
This project will support the management and implementation of a 60-day research cruise to the Amundsen Sea sector of the Antarctic continental margin to collect samples for measurements of a broad suite of trace elements and isotopes ('TEIs'), as part of the U.S. GEOTRACES program. GEOTRACES is a global effort in the field of Chemical Oceanography, the goal of which is to understand the distributions of trace elements and their isotopes in the ocean. Determining the distributions of these elements and isotopes will increase the understanding of processes that shape their distributions and also the processes that depend on these elements. Key TEIs include essential micronutrients such as iron and zinc; 'tracers' such as aluminum, manganese, and isotopes of nitrogen, thorium and neodymium that can be used to investigate modern and ancient ocean processes; and elements such as lead that are indicative of human activities. In the Southern Ocean, the Antarctic continental margins are important as sources of micronutrient trace elements such as iron, which is required to support biological production and carbon export over the Antarctic shelf and in offshore waters of the Antarctic Circumpolar Current. Moreover, these regions are experiencing rapid environmental changes that are expected to impact oceanic circulation and biogeochemical cycles, for which TEIs provide crucial data needed to test and refine numerical models of the Earth system. The Amundsen Sea sector holds particular interest because of the pronounced, decadal-scale increases in the melting rates of glacial ice shelves that border the region, driven by intrusions of warm Circumpolar Deep Water onto the continental shelf. This melting has potentially major impacts on global sea level, on the formation of Antarctic Bottom Water in the Ross Sea, and on the regional ecosystem.</p>
<p>The cruise will comprise essential sampling operations (collection and shipboard processing) and ancillary measurements (hydrography, nutrients, algal pigments) in support of multiple, individual science projects, following the successful model of previous U.S. GEOTRACES cruises in the Atlantic, Pacific and Arctic ocean basins. The cruise will sample the ocean region between 100°W and 135°W, with stations ranging from 67°S in the Antarctic Circumpolar Current southward to the Amundsen Sea continental shelf, including stations adjacent to several rapidly melting ice shelves and in highly-productive shelf polynyas. Water column samples will be collected using conventional and trace-metal clean CTD-rosette systems, in-situ high-volume pumps, and a towed fish sampler or small boat, using established methods. Sampling time will also be provided for collection of sea ice, floating glacial ice, and seafloor sediments. To facilitate coordination with a complementary open-ocean cruise and ensure access to the study region to document the impact of biological processes, the cruise is planned for late austral summer (late January-late March). Beyond the disciplinary contributions, the proposed research will contribute knowledge concerning the cryosphere and its impacts on global sea level and ocean circulation, regional ecosystems and biological processes, ocean-atmosphere interactions, and past and future environmental change. The project will contribute to STEM education and outreach through the participation of an NSF-funded PolarTREC education professional, and a K-12 STEM program for students from underserved and underrepresented schools run by Rutgers University education specialists. To foster public engagement, the investigators will partner with the UCSC Science Communication Program to engage freelance science journalists to profile research in this spectacular and harsh Antarctic environment.</p>
GP17-ANT
largerWorkCitation
project
eng; USA
oceans
Punta Arenas, Chile to Lyttelton, New Zealand
-133.02988
-78.85842
-74.38078
-65.2341
2023-12-05
2024-01-13
From projects that focused on the following 2 locations: 1. South Pacific and Amundsen Sea 2. Amundsen Sea Sector of the Antarctic Continental Margin
0
BCO-DMO catalogue of parameters from GP17-ANT carbonate system data from the GP17-OCE and GP17-ANT Inorganic Carbon,GP17-ANT projects of the U.S. GEOTRACES program
Biological and Chemical Oceanography Data Management Office (BCO-DMO)
Unavailable
508-289-2009
WHOI MS#36
Woods Hole
MA
02543
USA
info@bco-dmo.org
http://www.bco-dmo.org
Monday - Friday 8:00am - 5:00pm
For questions regarding this resource, please contact BCO-DMO via the email address provided.
pointOfContact
http://lod.bco-dmo.org/id/dataset-parameter/1002626.rdf
Name: Station_ID
Units: unitless
Description: <p>Station number</p>
http://lod.bco-dmo.org/id/dataset-parameter/1002627.rdf
Name: Event_ID
Units: unitless
Description: <p>Cruise event number</p>
http://lod.bco-dmo.org/id/dataset-parameter/1002628.rdf
Name: Gear_ID
Units: unitless
Description: <p>Sampling instrument (ODF rosette bottle ID)</p>
http://lod.bco-dmo.org/id/dataset-parameter/1002629.rdf
Name: Start_Date_UTC
Units: unitless
Description: <p>Date (UTC) at start of event</p>
http://lod.bco-dmo.org/id/dataset-parameter/1002630.rdf
Name: Start_Time_UTC
Units: unitless
Description: <p>Time (UTC) at start of event</p>
http://lod.bco-dmo.org/id/dataset-parameter/1002631.rdf
Name: Start_ISO_DateTime_UTC
Units: unitless
Description: <p>Date and time (UTC) at start of event in ISO 8601 format</p>
http://lod.bco-dmo.org/id/dataset-parameter/1002633.rdf
Name: Start_Latitude
Units: decimal degrees
Description: <p>Latitude at start of event</p>
http://lod.bco-dmo.org/id/dataset-parameter/1002635.rdf
Name: Start_Longitude
Units: decimal degrees
Description: <p>Longitude at start of event</p>
http://lod.bco-dmo.org/id/dataset-parameter/1002637.rdf
Name: Rosette_Position
Units: unitless
Description: <p>Rosette position</p>
http://lod.bco-dmo.org/id/dataset-parameter/1002638.rdf
Name: Sample_ID
Units: unitless
Description: <p>GETORACES sample ID number</p>
http://lod.bco-dmo.org/id/dataset-parameter/1002639.rdf
Name: Sample_Depth
Units: meters
Description: <p>Sample depth</p>
http://lod.bco-dmo.org/id/dataset-parameter/1002641.rdf
Name: PH_TMP_BOTTLE_ivhgkg
Units: degrees Celsius
Description: <p>Temperature at which pH was determined</p>
http://lod.bco-dmo.org/id/dataset-parameter/1002642.rdf
Name: SD1_PH_TMP_BOTTLE_ivhgkg
Units: degrees Celsius
Description: <p>standard deviation of PH_TMP_BOTTLE_ivhgkg</p>
http://lod.bco-dmo.org/id/dataset-parameter/1002643.rdf
Name: Flag_PH_TMP_BOTTLE_ivhgkg
Units: unitless
Description: <p>Quality Flag for PH_TMP_BOTTLE_ivhgkg</p>
http://lod.bco-dmo.org/id/dataset-parameter/1002644.rdf
Name: DIC_D_CONC_BOTTLE_2nk2fs
Units: micromoles per kilogram of seawater (umol/kg)
Description: <p>Concentration of dissolved inorganic carbon</p>
http://lod.bco-dmo.org/id/dataset-parameter/1002645.rdf
Name: SD1_DIC_D_CONC_BOTTLE_2nk2fs
Units: micromoles per kilogram of seawater (umol/kg)
Description: <p>standard deviation of DIC_D_CONC_BOTTLE_2nk2fs</p>
http://lod.bco-dmo.org/id/dataset-parameter/1002646.rdf
Name: Flag_DIC_D_CONC_BOTTLE_2nk2fs
Units: unitless
Description: <p>Quality Flag for DIC_D_CONC_BOTTLE_2nk2fs</p>
http://lod.bco-dmo.org/id/dataset-parameter/1002647.rdf
Name: TALK_D_CONC_BOTTLE_bjyhik
Units: micromoles per kilogram seawater (umol/kg)
Description: <p>Concentration of total alkalinity</p>
http://lod.bco-dmo.org/id/dataset-parameter/1002648.rdf
Name: SD1_TALK_D_CONC_BOTTLE_bjyhik
Units: micromoles per kilogram seawater (umol/kg)
Description: <p>standard deviation of TALK_D_CONC_BOTTLE_bjyhik</p>
http://lod.bco-dmo.org/id/dataset-parameter/1002649.rdf
Name: Flag_TALK_D_CONC_BOTTLE_bjyhik
Units: unitless
Description: <p>Quality flag for TALK_D_CONC_BOTTLE_bjyhik</p>
http://lod.bco-dmo.org/id/dataset-parameter/1002650.rdf
Name: PH_TOT_BOTTLE_5rqziy
Units: unitless
Description: <p>pH, referred to total scale</p>
http://lod.bco-dmo.org/id/dataset-parameter/1002651.rdf
Name: SD1_PH_TOT_BOTTLE_5rqziy
Units: unitless
Description: <p>standard deviation of PH_TOT_BOTTLE_5rqziy</p>
http://lod.bco-dmo.org/id/dataset-parameter/1002652.rdf
Name: Flag_PH_TOT_BOTTLE_5rqziy
Units: unitless
Description: <p>Quality Flag for PH_TOT_BOTTLE_5rqziy</p>
GB/NERC/BODC > British Oceanographic Data Centre, Natural Environment Research Council, United Kingdom
Biological and Chemical Oceanography Data Management Office (BCO-DMO)
Unavailable
508-289-2009
WHOI MS#36
Woods Hole
MA
02543
USA
info@bco-dmo.org
http://www.bco-dmo.org
Monday - Friday 8:00am - 5:00pm
For questions regarding this resource, please contact BCO-DMO via the email address provided.
pointOfContact
https://osprey.bco-dmo.org/dataset/1002581/data/download
download
onLine
dataset
<p>All samples were collected and analyzed following best practices guidelines (Dickeson et al. 2007). Dissolved inorganic carbon (DIC) was collected in 250-milliliter (mL) borosilicate glass reagent bottles and sealed using Apiezon L grease and a rubber band held in place with a plastic hose clamp. The total alkalinity (TA) and pH<sub>T</sub> were collected in 150 mL borosilicate glass serum bottles and sealed with a butyl-rubber cap and aluminum seal. All bottles were filled in the same manner. A silicone tube was attached to the Niskin valve. A small amount of water was added to the bottle, and the bottle was swirled to cover all surfaces and dumped out. This rinse was repeated a total of three times. Then the tube was placed near the bottom of the bottle and filled. The tube was tapped against the bottom to dislodge any bubbles, and care was taken to overflow any bubbles. Once full, the water was allowed to overflow for at least half the volume of the bottle (as estimated by time to fill the bottle) and all visible bubbles were gone. Overflow water was used to rinse the caps. With the water still flowing, the tube was gently, but quickly, removed leaving the bottle full to the brim. A pipette was then used to remove a precise amount of water, leaving ~1% headspace once the bottle was capped. After removing the water for headspace, a saturated mercuric chloride solution was added to a total volume of 0.04% of the sample. The DIC was then capped with a glass stopper with Apiezon L grease, twisting the cap to ensure even distribution of grease, creating an airtight seal. A rubber band and hose clamp were then placed on the cap to keep it in place. For TA and pHt, the rubber stopper was inserted and an aluminum seal was crimped on top. Once sealed, all bottles were gently inverted several times in order to mix the mercuric chloride. The entire collection process was completed as quickly as possible, but with care, to minimize any gas exchange. After collection, DIC/TA bottles were placed in plastic crates with protective foam and stored in a refrigerated shipping van until arrival in port. The samples were shipped back to the laboratory without temperature control and stored in the laboratory at room temperature until analysis. The pH<sub>T</sub> samples were immediately placed in a 20-degree Celsius (°C) water bath to equilibrate the temperature before analysis.</p>
<p>The pH<sub>T</sub> at 20°C was analyzed within 6 hours of collection. The samples were allowed a minimum of 2 hours for temperature equilibration before analysis was started. The pH<sub>T</sub> was then measured spectrophotometrically with purified metacresol purple (mCP) dye (Woosley lab batch 4) obtained from the laboratory of Robert H. Byrne (University of South Florida), using a custom-designed automated system similar to that of Carter et al. (2013). The instrument uses a 10 mL Kloehn syringe pump to draw the sample from the bottle, rinse the flow-through 10-centimeter (cm) quartz micro-volume spectrophotometric cell (Starna, Inc.), add and mix the mCP indicator, and finally rinse the cell after analysis. An Agilent 8454 UV/VIS spectrophotometer was used to take the blank, and full spectra with mCP. The absorbances at 434, 578, 730, and 488 nanometers (nm) were used for calculations. The equations of Liu et al. (2011) were used to calculate pH<sub>T</sub>, and the isobestic absorbance at 488 nm was used to determine the indicator perturbation adjustment following the method described in Carter et al. (2013). The dye perturbation slope and intercept were -0.0649 and 0.0781, respectively. Duplicate samples, Certified reference material provided by the laboratory of Andrew G. Dickson (University of California, San Diego), and TRIS buffers prepared according to Paulsen and Dickson (2020) were used to check precision and "accuracy". The mean absolute difference between duplicate samples was 0.0013 ± 0.0008 (N=27). The mean and standard deviation of CRM (Batch 199) were 7.9115 ± 0.0013 (N =15), and for TRIS (Woosley Lab Batch 5) 8.21514 ± 0.0016 (N = 17).</p>
<p>The DIC/TA samples were stored in a refrigerated van on deck after collection, and shipped (without temperature control) to the land-based laboratory at MIT (via USAP in Port Hueneme, California), and then stored at room temperature in a closet until analysis. Analyses were performed between 8 and 20 months after the end of the cruise. All TA samples were analyzed first. Then DIC was analyzed with several analyses of TA being performed immediately afterwards from the DIC bottle as a check on the sample collected for TA.</p>
<p>DIC was analyzed using a custom-designed DIC extractor (DICE) built by NOAA PMEL (Pacific Marine Environmental Laboratory). It is a modern version of the original SOMMA system (Johnson 1992) and follows the methods described in Dickson et al. (2007) in SOP 2. Analysis is performed at 20°C. The instrument uses a calibrated pipette to precisely dispense the volume of sample into a stripper chamber where 8.5% phosphoric acid had been added. The acid converted all the DIC to CO<sub>2</sub> gas. A pure N<sub>2</sub> carrier gas then carried the evolved CO<sub>2</sub> through a condensor to remove water vapor followed by a silica gel (Orbo Tube, Millipore-Sigma, Inc.) to remove any organic acids and finally into the coulometer (UIC, Inc.) for detection. The instrument was calibrated at the start of each coulometer cell (1 per day) with a blank, 2 pure (99.999% CO<sub>2</sub>) gas loops, each run at least twice, and certified reference material (CRM) provided by the laboratory of Andrew G. Dickson (University of California, San Diego). Sample values were adjusted to the CRM value for that day using a constant offset from the certified value. Two duplicates per station were analyzed to assess precision. The mean and standard deviation of the absolute difference between duplicates was 1.6 ± 1.1 (N = 29). CRM Batch 216 was used, the overall mean difference from the certified (measured - certified) value was -2.55 ± 1.47 (N = 51).</p>
<p>TA was analyzed using an instrument custom-designed and built by the laboratory of Andrew G. Dickson (UCSD) and described in Dickson et al. (2003, 2007). Analysis was performed at 20°C. A sample of approximately 100 to 130 grams (g) is weighed and added to a clean, dry water-jacketed beaker with a stir bar, and a cap with an Ecotrode electrode (Metrohm, AG), thermometer, acid line, and air line is placed on top. A computer-controlled dosimat then adds enough acid to reach a pH of ~3.5. The sample is then stirred (450 rpm) and bubbled with lab air for 300 seconds to drive off evolved CO<sub>2</sub>. Then 15-20 fine additions of 50 microliters (µL) of acid are added and voltages and temperatures recorded. Once complete, a non-linear least squares fitting method is used to calculate the TA as well as calibrate the E<sup>0</sup> of the electrode. The fitting method is described in Dickson et al. (2003). A CRM was analyzed at the beginning and end of each day. Sample values were NOT adjusted to the certified value. Two duplicates per station were analyzed to assess precision. In addition, several bottles collected for DIC were also analyzed for TA as a check and to provide additional duplicate measurements. These samples were analyzed immediately after analyzing DIC (generally within 15-20 minutes). The acid was ~0.1 N HCl prepared in ~0.6 M NaCl to match the approximate ionic strength of seawater. The exact concentration was calibrated by borax titration following the method of Kolthoff (1926). The mean and standard deviation of the absolute difference between duplicates was 2.43 ± 1.65 (N = 153). The mean and standard deviation of the CRM Batch 216 difference from the certified value (measured - certified) was -0.10 ± 2.09 (N = 116).</p>
Specified by the Principal Investigator(s)
<p>For pH<sub>T</sub>, the raw absorbance values were used to calculate pH<sub>T</sub> on the total scale using the absorbance ratio and equations of Liu et al. (2011). The indicator perturbation adjustment was applied following the method of Carter et al. (2013).</p>
<p>For DIC, the raw coulometer counts were converted to DIC following the equations in Dickson et al. (2007), with the blank and gas calibration factor determined for each coulometer cell. Values were corrected to the CRM using a constant offset from the CRM measured on the same cell as the sample.</p>
<p>For TA, the titration data were fit using the non-linear least squares fit method described in Dickson et al. (2003, 2007). No adjustment was made to the CRM.</p>
<p>For all parameters, values were checked for outliers by comparing near by profiles, comparisons to nutrients, and oxygen, and internal consistency calculations. If a cause for an outlier was found (e.g. analysis issue), the value was flagged as bad; if no clear cause was found, the value was flagged as questionable.</p>
Specified by the Principal Investigator(s)
- Loaded sheet 1 of the original Excel file "NBP2401_Carbon Data Submit BCODMO.xlsx" into the BCO-DMO system, treating "-999", "-999.0000", and "-999.0" as missing values (missing values are empty/blank in the final CSV file).
- Renamed columns to comply with BCO-DMO naming conventions.
- Deleted empty columns: End_Date_UTC, End_Time_UTC, End_Latitude, End_Longitude
- Combined Start_Date_UTC (format %d/%m/%Y) and Start_Time_UTC (format %H:%M) into new datetime column Start_ISO_DateTime_UTC (format %Y-%m-%dT%H:%MZ, UTC).
- Converted Start_Date_UTC to date type with output format %Y-%m-%d.
- Converted Start_Time_UTC to time type with output format %H:%M.
- Saved the final file as "1002581_v1_gp17-ant_carbonate_system_data.csv".
- Loaded the original Excel file "NBP2401_RawAbsorbances_pHt.xlsx" into the BCO-DMO system, treating "-999" as a missing value (missing values are empty/blank in the final CSV file).
- Renamed column "GEOTRACES#" to "GEOTRACES_Sample_Num" and "pH TMP" to "pH_TMP".
- Saved the final supplemental file as "1002581_v1_raw_absorbance_values.csv".
Specified by BCO-DMO Data Managers
asNeeded
7.x-1.1
Biological and Chemical Oceanography Data Management Office (BCO-DMO)
Unavailable
508-289-2009
WHOI MS#36
Woods Hole
MA
02543
USA
info@bco-dmo.org
http://www.bco-dmo.org
Monday - Friday 8:00am - 5:00pm
For questions regarding this resource, please contact BCO-DMO via the email address provided.
pointOfContact
custom-designed DIC extractor (DICE)
custom-designed DIC extractor (DICE)
PI Supplied Instrument Name: custom-designed DIC extractor (DICE) PI Supplied Instrument Description:DIC was analyzed using a custom designed DIC extractor (DICE) built by NOAA PMEL (Pacific Marine Environmental Laboratory). It is a modern version of the original SOMMA system (Johnson 1992) and follows the methods described in Dickson et al. (2007) Instrument Name: CO2 Coulometer Instrument Short Name:CO2 coulometer Instrument Description: A CO2 coulometer semi-automatically controls the sample handling and extraction of CO2 from seawater samples. Samples are acidified and the CO2 gas is bubbled into a titration cell where CO2 is converted to hydroxyethylcarbonic acid which is then automatically titrated with a coulometrically-generated base to a colorimetric endpoint. Community Standard Description: http://vocab.nerc.ac.uk/collection/L05/current/LAB12
Niskin bottles
Niskin bottles
PI Supplied Instrument Name: Niskin bottles Instrument Name: Niskin bottle Instrument Short Name:Niskin bottle Instrument Description: A Niskin bottle (a next generation water sampler based on the Nansen bottle) is a cylindrical, non-metallic water collection device with stoppers at both ends. The bottles can be attached individually on a hydrowire or deployed in 12, 24, or 36 bottle Rosette systems mounted on a frame and combined with a CTD. Niskin bottles are used to collect discrete water samples for a range of measurements including pigments, nutrients, plankton, etc. Community Standard Description: http://vocab.nerc.ac.uk/collection/L22/current/TOOL0412/
Agilent 8454 UV/VIS spectrophotometer
Agilent 8454 UV/VIS spectrophotometer
PI Supplied Instrument Name: Agilent 8454 UV/VIS spectrophotometer Instrument Name: Spectrophotometer Instrument Short Name:Spectrophotometer Instrument Description: An instrument used to measure the relative absorption of electromagnetic radiation of different wavelengths in the near infra-red, visible and ultraviolet wavebands by samples. Community Standard Description: http://vocab.nerc.ac.uk/collection/L05/current/LAB20/
custom-built open-cell potentiometric titrator
custom-built open-cell potentiometric titrator
PI Supplied Instrument Name: custom-built open-cell potentiometric titrator PI Supplied Instrument Description:Custom-built open-cell potentiometric titrator (Dickson lab, UCSD) using a Metrohm Ecotrode electrode and automated dosimat for total alkalinity determination via non-linear least squares fitting. Instrument Name: Titrator Instrument Short Name:Titrator Instrument Description: Titrators are instruments that incrementally add quantified aliquots of a reagent to a sample until the end-point of a chemical reaction is reached. Community Standard Description: http://vocab.nerc.ac.uk/collection/L05/current/LAB12/
Cruise: NBP2401
NBP2401
Community Standard Description
International Council for the Exploration of the Sea
RVIB Nathaniel B. Palmer
vessel
NBP2401
Peter N. Sedwick
Old Dominion University
https://www.bodc.ac.uk/resources/inventories/cruise_inventory/reports/nathanielbpalmer_nbp2401.pdf
Report describing NBP2401
Community Standard Description
International Council for the Exploration of the Sea
RVIB Nathaniel B. Palmer
vessel