Contributors | Affiliation | Role |
---|---|---|
Shiller, Alan M. | University of Southern Mississippi (USM) | Principal Investigator |
Gilbert, Melissa | University of Southern Mississippi (USM) | Scientist |
Rauch, Shannon | Woods Hole Oceanographic Institution (WHOI BCO-DMO) | BCO-DMO Data Manager |
Clean seawater samples were collected using a GEOTRACES CTD referred to as GT-C/12L GoFlo, and also from the Super-GeoFISH towed surface vehicle. For more information, see the cruise report.
Water samples were filtered through pre-cleaned, 0.2-micrometer (µm) Pall Acropak Supor filter capsules as described elsewhere (e.g., Cutter et al., 2014; Hatta et al., 2015). Filtered water was collected in 125-milliliter (mL) HDPE bottles (Nalgene) that had been precleaned by soaking in hot 1.2 M HCl (reagent grade) for at least 8 hours with subsequent thorough rinsing with ultrapure distilled deionized water (Barnstead E-pure).
Dissolved Rare Earth Elements (REEs including Y), were determined using 14 mL of sample, which was spiked with a mixture of isotopically-enriched Nd-145, Sm-149, Eu-153, Gd-155, Dy-161, Er-167, and Yb-171 (Oak Ridge National Labs). Each spike was >90% enriched in the listed isotopes. The sample/spike ratio was chosen so as to have the analytical isotope ratios approximately the geometric mean of the natural and enriched spike isotope ratios. Samples were then extracted/pre-concentrated using a SeaFAST system (Elemental Scientific, Inc.) operated in offline mode. A similar online SeaFAST extraction procedure is described by Hathorne et al., 2012. The extracted samples were subsequently analyzed using a Thermo-Fisher high-resolution ICP-MS with an Apex-FAST high-efficiency sample introduction system with Spiro desolvator (Elemental Scientific, Inc.). The instrument was operated in low resolution. The enriched isotope spikes also served to provide counts/sec calibration factors for elements that were not spiked with enriched isotopes. This calibration was also examined with a standard made in dilute nitric acid. Precision and recovery were checked by analysis of a large-volume composite seawater sample. Spiked (with a natural isotopic abundance elemental spike) and unspiked aliquots of this sample were analyzed twice in each analytical run. A Ba standard was also run to check for BaO+ interference on several isotopes and Ba in the extracted samples was also monitored. Because the extraction resin in the SeaFAST system (Nobias PA-1) discriminates against Ba, plus the reduction of the BaO+ interference by the desolvation system, BaO+ was less than 0.1% of the counts in Eu-151, Eu-153, Gd-155, and Gd-157. Tests also revealed no significant low REE oxide interference on mid-/high-REEs.
Dissolved Nd was determined in a separate seaFAST extraction, but with essentially the same methodology as the transition metals as described in related dataset "GP15 Dissolved Ba Cd Cu Ga Mn Ni and Pb Leg 2" (https://www.bco-dmo.org/dataset/836121). The samples were spiked with isotopically-enriched Nd-145. Nd was determined in low resolution.
Quality Flags:
SeaDataNet quality flags have been assigned. More information on SeaDataNet quality flags is available from GEOTRACES at https://www.geotraces.org/geotraces-quality-flag-policy/ and from SeaDataNet at https://www.seadatanet.org/Standards/Data-Quality-Control. In summary:
0 = no quality control;
1 = good value;
2 = probably good value;
3 = probably bad value;
4 = bad value;
5 = changed value;
6 = value below detection;
7 = value in excess;
8 = interpolated value;
9 = missing value;
A = value phenomenon uncertain.
- Imported original file "RR1815_dataTemplate.xlsx" into the BCO-DMO system.
- Renamed fields to comply with BCO-DMO naming conventions.
- Created start date-time column in ISO8601 format.
- Removed unused columns: Gear_ID, End_Date_UTC, End_Time_UTC, End_Latitude, End_Longitude. (SD columns are also not used, but kept those).
- Saved the final file as "932559_v1_gp15_dissolved_rees_leg2.csv".
- Converted the Intercalibration report from .docx to .pdf and attached it as a Supplemental File named "0000-0002-2068-7909-RR1815-multiple-param-intercal-report.pdf".
File |
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932559_v1_gp15_dissolved_rees_leg2.csv (Comma Separated Values (.csv), 116.68 KB) MD5:d69e53dac66632300ad0f9584c761d6c Primary data file for dataset ID 932559, version 1 |
File |
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0000-0002-2068-7909-RR1815-multiple-param-intercal-report_rev.pdf (Portable Document Format (.pdf), 2.09 MB) MD5:a4fdefbd277d6c10f8aa0e3730f78769 GEOTRACES Intercalibration Report for dataset 932559 (PI: Alan Shiller) |
Parameter | Description | Units |
Station_ID | Station number | unitless |
Event_ID | Event number | unitless |
Start_ISO_DateTime_UTC | Date and time (UTC) at start of sampling event in ISO 8601 format | unitless |
Start_Date_UTC | Date at start of sampling event | unitless |
Start_Time_UTC | Time (UTC) at start of sampling event | unitless |
Start_Latitude | Latitude at start of sampling event | decimal degrees |
Start_Longitude | Longitude at start of sampling event | decimal degrees |
Rosette_Position | Bottle position on rosette | unitless |
Sample_ID | Sample ID number | unitless |
Sample_Depth | Sample depth | meters (m) |
Y_D_CONC_BOTTLE_vbtqm7 | Concentration of dissolved Y from bottle samples | picomoles per kilogram (pmol/kg) |
SD1_Y_D_CONC_BOTTLE_vbtqm7 | Standard deviation of Y_D_CONC_BOTTLE_vbtqm7 | picomoles per kilogram (pmol/kg) |
Flag_Y_D_CONC_BOTTLE_vbtqm7 | Quality flag for Y_D_CONC_BOTTLE_vbtqm7 | unitless |
Y_D_CONC_FISH_asoboe | Concentration of dissolved Y from towed GeoFish samples | picomoles per kilogram (pmol/kg) |
SD1_Y_D_CONC_FISH_asoboe | Standard deviation of Y_D_CONC_FISH_asoboe | picomoles per kilogram (pmol/kg) |
Flag_Y_D_CONC_FISH_asoboe | Quality flag for Y_D_CONC_FISH_asoboe | unitless |
La_D_CONC_BOTTLE_19sfbu | Concentration of dissolved La from bottle samples | picomoles per kilogram (pmol/kg) |
SD1_La_D_CONC_BOTTLE_19sfbu | Standard deviation of La_D_CONC_BOTTLE_19sfbu | picomoles per kilogram (pmol/kg) |
Flag_La_D_CONC_BOTTLE_19sfbu | Quality flag for La_D_CONC_BOTTLE_19sfbu | unitless |
La_D_CONC_FISH_l1u3qy | Concentration of dissolved La from towed GeoFish samples | picomoles per kilogram (pmol/kg) |
SD1_La_D_CONC_FISH_l1u3qy | Standard deviation of LLa_D_CONC_FISH_l1u3qy | picomoles per kilogram (pmol/kg) |
Flag_La_D_CONC_FISH_l1u3qy | Quality flag for La_D_CONC_FISH_l1u3qy | unitless |
Ce_D_CONC_BOTTLE_7r1crl | Concentration of dissolved Ce from bottle samples | picomoles per kilogram (pmol/kg) |
SD1_Ce_D_CONC_BOTTLE_7r1crl | Standard deviation of Ce_D_CONC_BOTTLE_7r1crl | picomoles per kilogram (pmol/kg) |
Flag_Ce_D_CONC_BOTTLE_7r1crl | Quality flag for Ce_D_CONC_BOTTLE_7r1crl | unitless |
Ce_D_CONC_FISH_nrzhse | Concentration of dissolved Ce from towed GeoFish samples | picomoles per kilogram (pmol/kg) |
SD1_Ce_D_CONC_FISH_nrzhse | Standard deviation of Ce_D_CONC_FISH_nrzhse | picomoles per kilogram (pmol/kg) |
Flag_Ce_D_CONC_FISH_nrzhse | Quality flag for Ce_D_CONC_FISH_nrzhse | unitless |
Pr_D_CONC_BOTTLE_kytybd | Concentration of dissolved Pr from bottle samples | picomoles per kilogram (pmol/kg) |
SD1_Pr_D_CONC_BOTTLE_kytybd | Standard deviation of Pr_D_CONC_BOTTLE_kytybd | picomoles per kilogram (pmol/kg) |
Flag_Pr_D_CONC_BOTTLE_kytybd | Quality flag for Pr_D_CONC_BOTTLE_kytybd | unitless |
Pr_D_CONC_FISH_xp0hyb | Concentration of dissolved Pr from towed GeoFish samples | picomoles per kilogram (pmol/kg) |
SD1_Pr_D_CONC_FISH_xp0hyb | Standard deviation of Pr_D_CONC_FISH_xp0hyb | picomoles per kilogram (pmol/kg) |
Flag_Pr_D_CONC_FISH_xp0hyb | Quality flag for Pr_D_CONC_FISH_xp0hyb | unitless |
Nd_D_CONC_BOTTLE_4vjjtn | Concentration of dissolved Nd from bottle samples | picomoles per kilogram (pmol/kg) |
SD1_Nd_D_CONC_BOTTLE_4vjjtn | Standard deviation of Nd_D_CONC_BOTTLE_4vjjtn | picomoles per kilogram (pmol/kg) |
Flag_Nd_D_CONC_BOTTLE_4vjjtn | Quality flag for Nd_D_CONC_BOTTLE_4vjjtn | unitless |
Nd_D_CONC_FISH_ea16lv | Concentration of dissolved Nd from towed GeoFish samples | picomoles per kilogram (pmol/kg) |
SD1_Nd_D_CONC_FISH_ea16lv | Standard deviation of Nd_D_CONC_FISH_ea16lv | picomoles per kilogram (pmol/kg) |
Flag_Nd_D_CONC_FISH_ea16lv | Quality flag for Nd_D_CONC_FISH_ea16lv | unitless |
Sm_D_CONC_BOTTLE_4ekw3t | Concentration of dissolved Sm from bottle samples | picomoles per kilogram (pmol/kg) |
SD1_Sm_D_CONC_BOTTLE_4ekw3t | Standard deviation of Sm_D_CONC_BOTTLE_4ekw3t | picomoles per kilogram (pmol/kg) |
Flag_Sm_D_CONC_BOTTLE_4ekw3t | Quality flag for Sm_D_CONC_BOTTLE_4ekw3t | unitless |
Sm_D_CONC_FISH_3j9pqw | Concentration of dissolved Sm from towed GeoFish samples | picomoles per kilogram (pmol/kg) |
SD1_Sm_D_CONC_FISH_3j9pqw | Standard deviation of Sm_D_CONC_FISH_3j9pqw | picomoles per kilogram (pmol/kg) |
Flag_Sm_D_CONC_FISH_3j9pqw | Quality flag for Sm_D_CONC_FISH_3j9pqw | unitless |
Eu_D_CONC_BOTTLE_vbw6j8 | Concentration of dissolved Eu from bottle samples | picomoles per kilogram (pmol/kg) |
SD1_Eu_D_CONC_BOTTLE_vbw6j8 | Standard deviation of Eu_D_CONC_BOTTLE_vbw6j8 | picomoles per kilogram (pmol/kg) |
Flag_Eu_D_CONC_BOTTLE_vbw6j8 | Quality flag for Eu_D_CONC_BOTTLE_vbw6j8 | unitless |
Eu_D_CONC_FISH_60umzp | Concentration of dissolved Eu from towed GeoFish samples | picomoles per kilogram (pmol/kg) |
SD1_Eu_D_CONC_FISH_60umzp | Standard deviation of Eu_D_CONC_FISH_60umzp | picomoles per kilogram (pmol/kg) |
Flag_Eu_D_CONC_FISH_60umzp | Quality flag for Eu_D_CONC_FISH_60umzp | unitless |
Gd_D_CONC_BOTTLE_fgu3vr | Concentration of dissolved Gd from bottle samples | picomoles per kilogram (pmol/kg) |
SD1_Gd_D_CONC_BOTTLE_fgu3vr | Standard deviation of Gd_D_CONC_BOTTLE_fgu3vr | picomoles per kilogram (pmol/kg) |
Flag_Gd_D_CONC_BOTTLE_fgu3vr | Quality flag for Gd_D_CONC_BOTTLE_fgu3vr | unitless |
Gd_D_CONC_FISH_vv3b0x | Concentration of dissolved Gd from towed GeoFish samples | picomoles per kilogram (pmol/kg) |
SD1_Gd_D_CONC_FISH_vv3b0x | Standard deviation of Gd_D_CONC_FISH_vv3b0x | picomoles per kilogram (pmol/kg) |
Flag_Gd_D_CONC_FISH_vv3b0x | Quality flag for Gd_D_CONC_FISH_vv3b0x | unitless |
Tb_D_CONC_BOTTLE_whliao | Concentration of dissolved Tb from bottle samples | picomoles per kilogram (pmol/kg) |
SD1_Tb_D_CONC_BOTTLE_whliao | Standard deviation of Tb_D_CONC_BOTTLE_whliao | picomoles per kilogram (pmol/kg) |
Flag_Tb_D_CONC_BOTTLE_whliao | Quality flag for Tb_D_CONC_BOTTLE_whliao | unitless |
Tb_D_CONC_FISH_j519ko | Concentration of dissolved Tb from towed GeoFish samples | picomoles per kilogram (pmol/kg) |
SD1_Tb_D_CONC_FISH_j519ko | Standard deviation of Tb_D_CONC_FISH_j519ko | picomoles per kilogram (pmol/kg) |
Flag_Tb_D_CONC_FISH_j519ko | Quality flag for Tb_D_CONC_FISH_j519ko | unitless |
Dy_D_CONC_BOTTLE_qhjczn | Concentration of dissolved Dy from bottle samples | picomoles per kilogram (pmol/kg) |
SD1_Dy_D_CONC_BOTTLE_qhjczn | Standard deviation of Dy_D_CONC_BOTTLE_qhjczn | picomoles per kilogram (pmol/kg) |
Flag_Dy_D_CONC_BOTTLE_qhjczn | Quality flag for Dy_D_CONC_BOTTLE_qhjczn | unitless |
Dy_D_CONC_FISH_drvjhn | Concentration of dissolved Dy from towed GeoFish samples | picomoles per kilogram (pmol/kg) |
SD1_Dy_D_CONC_FISH_drvjhn | Standard deviation of Dy_D_CONC_FISH_drvjhn | picomoles per kilogram (pmol/kg) |
Flag_Dy_D_CONC_FISH_drvjhn | Quality flag for Dy_D_CONC_FISH_drvjhn | unitless |
Ho_D_CONC_BOTTLE_qafdfm | Concentration of dissolved Ho from bottle samples | picomoles per kilogram (pmol/kg) |
SD1_Ho_D_CONC_BOTTLE_qafdfm | Standard deviation of Ho_D_CONC_BOTTLE_qafdfm | picomoles per kilogram (pmol/kg) |
Flag_Ho_D_CONC_BOTTLE_qafdfm | Quality flag for Ho_D_CONC_BOTTLE_qafdfm | unitless |
Ho_D_CONC_FISH_gjxtdt | Concentration of dissolved Ho from towed GeoFish samples | picomoles per kilogram (pmol/kg) |
SD1_Ho_D_CONC_FISH_gjxtdt | Standard deviation of Ho_D_CONC_FISH_gjxtdt | picomoles per kilogram (pmol/kg) |
Flag_Ho_D_CONC_FISH_gjxtdt | Quality flag for Ho_D_CONC_FISH_gjxtdt | unitless |
Er_D_CONC_BOTTLE_dxdypm | Concentration of dissolved Er from bottle samples | picomoles per kilogram (pmol/kg) |
SD1_Er_D_CONC_BOTTLE_dxdypm | Standard deviation of Er_D_CONC_BOTTLE_dxdypm | picomoles per kilogram (pmol/kg) |
Flag_Er_D_CONC_BOTTLE_dxdypm | Quality flag for Er_D_CONC_BOTTLE_dxdypm | unitless |
Er_D_CONC_FISH_flv4pg | Concentration of dissolved Er from towed GeoFish samples | picomoles per kilogram (pmol/kg) |
SD1_Er_D_CONC_FISH_flv4pg | Standard deviation of Er_D_CONC_FISH_flv4pg | picomoles per kilogram (pmol/kg) |
Flag_Er_D_CONC_FISH_flv4pg | Quality flag for Er_D_CONC_FISH_flv4pg | unitless |
Tm_D_CONC_BOTTLE_d8qf2f | Concentration of dissolved Tm from bottle samples | picomoles per kilogram (pmol/kg) |
SD1_Tm_D_CONC_BOTTLE_d8qf2f | Standard deviation of Tm_D_CONC_BOTTLE_d8qf2f | picomoles per kilogram (pmol/kg) |
Flag_Tm_D_CONC_BOTTLE_d8qf2f | Quality flag for Tm_D_CONC_BOTTLE_d8qf2f | unitless |
Tm_D_CONC_FISH_vshlpq | Concentration of dissolved Tm from towed GeoFish samples | picomoles per kilogram (pmol/kg) |
SD1_Tm_D_CONC_FISH_vshlpq | Standard deviation of Tm_D_CONC_FISH_vshlpq | picomoles per kilogram (pmol/kg) |
Flag_Tm_D_CONC_FISH_vshlpq | Quality flag for Tm_D_CONC_FISH_vshlpq | unitless |
Yb_D_CONC_BOTTLE_aebv5r | Concentration of dissolved Yb from bottle samples | picomoles per kilogram (pmol/kg) |
SD1_Yb_D_CONC_BOTTLE_aebv5r | Standard deviation of Yb_D_CONC_BOTTLE_aebv5r | picomoles per kilogram (pmol/kg) |
Flag_Yb_D_CONC_BOTTLE_aebv5r | Quality flag for Yb_D_CONC_BOTTLE_aebv5r | unitless |
Yb_D_CONC_FISH_7thabf | Concentration of dissolved Yb from towed GeoFish samples | picomoles per kilogram (pmol/kg) |
SD1_Yb_D_CONC_FISH_7thabf | Standard deviation of Yb_D_CONC_FISH_7thabf | picomoles per kilogram (pmol/kg) |
Flag_Yb_D_CONC_FISH_7thabf | Quality flag for Yb_D_CONC_FISH_7thabf | unitless |
Lu_D_CONC_BOTTLE_dgzysp | Concentration of dissolved Lu from bottle samples | picomoles per kilogram (pmol/kg) |
SD1_Lu_D_CONC_BOTTLE_dgzysp | Standard deviation of Lu_D_CONC_BOTTLE_dgzysp | picomoles per kilogram (pmol/kg) |
Flag_Lu_D_CONC_BOTTLE_dgzysp | Quality flag for Lu_D_CONC_BOTTLE_dgzysp | unitless |
Lu_D_CONC_FISH_jcdlov | Concentration of dissolved Lu from towed GeoFish samples | picomoles per kilogram (pmol/kg) |
SD1_Lu_D_CONC_FISH_jcdlov | Standard deviation of Lu_D_CONC_FISH_jcdlov | picomoles per kilogram (pmol/kg) |
Flag_Lu_D_CONC_FISH_jcdlov | Quality flag for Lu_D_CONC_FISH_jcdlov | unitless |
Dataset-specific Instrument Name | Super-GeoFISH towed surface vehicle |
Generic Instrument Name | GeoFish Towed near-Surface Sampler |
Generic Instrument Description | The GeoFish towed sampler is a custom designed near surface ( |
Dataset-specific Instrument Name | GT-C/12L GoFlo |
Generic Instrument Name | GO-FLO Bottle |
Generic Instrument Description | GO-FLO bottle cast used to collect water samples for pigment, nutrient, plankton, etc. The GO-FLO sampling bottle is specially designed to avoid sample contamination at the surface, internal spring contamination, loss of sample on deck (internal seals), and exchange of water from different depths. |
Dataset-specific Instrument Name | SeaFAST system (Elemental Scientific, Inc.) |
Generic Instrument Name | SeaFAST Automated Preconcentration System |
Generic Instrument Description | The seaFAST is an automated sample introduction system for analysis of seawater and other high matrix samples for analyses by ICPMS (Inductively Coupled Plasma Mass Spectrometry). |
Dataset-specific Instrument Name | Thermo-Fisher high resolution ICP-MS |
Generic Instrument Name | Thermo Scientific ELEMENT XR high resolution inductively coupled plasma mass spectrometer |
Dataset-specific Description | Thermo-Fisher high resolution ICP-MS with an Apex-FAST high efficiency sample introduction system with Spiro desolvator (Elemental Scientific, Inc.) |
Generic Instrument Description | A high-resolution (HR) inductively coupled plasma (ICP) mass spectrometer (MS) composed of a dual mode secondary electron multiplier (SEM) and a Faraday detector. The ELEMENT XR instrument has a dynamic range of 5 x 10^7 to 1 x 10^12 counts per second (cps), and allows simultaneous measurement of elements at concentrations over 1000 ug/g. |
Website | |
Platform | R/V Roger Revelle |
Report | |
Start Date | 2018-10-24 |
End Date | 2018-11-24 |
Description | Additional cruise information is available from the Rolling Deck to Repository (R2R): https://www.rvdata.us/search/cruise/RR1815 |
A 60-day research cruise took place in 2018 along a transect form Alaska to Tahiti at 152° W. A description of the project titled "Collaborative Research: Management and implementation of the US GEOTRACES Pacific Meridional Transect", funded by NSF, is below. Further project information is available on the US GEOTRACES website and on the cruise blog. A detailed cruise report is also available as a PDF.
Description from NSF award abstract:
GEOTRACES is a global effort in the field of Chemical Oceanography in which the United States plays a major role. The goal of the GEOTRACES program is to understand the distributions of many elements and their isotopes in the ocean. Until quite recently, these elements could not be measured at a global scale. Understanding 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. For example, many "trace elements" (elements that are present in very low amounts) are also important for life, and their presence or absence can play a vital role in the population of marine ecosystems. This project will launch the next major U.S. GEOTRACES expedition in the Pacific Ocean between Alaska and Tahiti. The award made here would support all of the major infrastructure for this expedition, including the research vessel, the sampling equipment, and some of the core oceanographic measurements. This project will also support the personnel needed to lead the expedition and collect the samples.
This project would support the essential sampling operations and infrastructure for the U.S. GEOTRACES Pacific Meridional Transect along 152° W to support a large variety of individual science projects on trace element and isotope (TEI) biogeochemistry that will follow. Thus, the major objectives of this management proposal are: (1) plan and coordinate a 60 day research cruise in 2018; (2) obtain representative samples for a wide variety of TEIs using a conventional CTD/rosette, GEOTRACES Trace Element Sampling Systems, and in situ pumps; (3) acquire conventional CTD hydrographic data along with discrete samples for salinity, dissolved oxygen, algal pigments, and dissolved nutrients at micro- and nanomolar levels; (4) ensure that proper QA/QC protocols are followed and reported, as well as fulfilling all GEOTRACES intercalibration protocols; (5) prepare and deliver all hydrographic data to the GEOTRACES Data Assembly Centre (via the US BCO-DMO data center); and (6) coordinate all cruise communications between investigators, including preparation of a hydrographic report/publication. This project would also provide baseline measurements of TEIs in the Clarion-Clipperton fracture zone (~7.5°N-17°N, ~155°W-115°W) where large-scale deep sea mining is planned. Environmental impact assessments are underway in partnership with the mining industry, but the effect of mining activities on TEIs in the water column is one that could be uniquely assessed by the GEOTRACES community. In support of efforts to communicate the science to a wide audience the investigators will recruit an early career freelance science journalist with interests in marine science and oceanography to participate on the cruise and do public outreach, photography and/or videography, and social media from the ship, as well as to submit articles about the research to national media. The project would also support several graduate students.
NSF Award Abstract:
This project involves participation in an oceanographic research cruise scheduled for mid-2018 and going from Tahiti to Alaska along 152° W in the Pacific Ocean. This cruise transect will allow for sampling of ocean waters in a wide variety of environments. These environments include the Aleutian margin (where there is significant input of continental materials), the subarctic North Pacific (where plant productivity may be limited by iron availability), deep waters of the North Pacific (which are the oldest deep waters of the ocean), as well as oxygen minimum zones, hydrothermal plumes, and equatorial waters subject to upwelling. The investigators will determine dissolved concentrations of barium (Ba), gallium (Ga), rare earth elements (REEs), and methane. These studies are pertinent to important oceanic issues including delivery of mineral dust and nutrient iron to the surface ocean (Ga), removal and internal cycling of trace elements (Ba, REEs), development of tracers of past ocean processes (Ba), and tracing sources of material (Ga, Ba, REEs, methane) including margin sources (Ba, REEs, methane). Other researchers involved in the cruise will determine additional elements and isotopes including iron (Fe), aluminum (Al), and radium isotopes (Ra). Comparing these chemical distributions is key for all of the involved research groups to test hypothesized mechanisms of element input, removal, and cycling through the ocean. These mechanisms, in turn, are pertinent to understanding the ocean's biological productivity and its role in global climate. The knowledge and experience gained from this project will be incorporated into the principle investigator's courses in oceanography. A graduate student will also be supported and trained as part of this project.
A researcher from the University of Southern Mississippi will participate in the 2018 US GEOTRACES Pacific Meridional Transect (PMT) going from Tahiti to the Aleutians along 152° W. During the cruise, samples will be collected from regions exhibiting strong margin fluxes, the subarctic HNLC waters, the oldest deep water in the world's oceans, the distal ends of hydrothermal plumes from the Juan de Fuca Ridge and East Pacific Rise as well as oxygen minimum zones, equatorial upwelling, and some of the most oligotrophic waters in the world's oceans in the South Pacific gyre at 20°S. The samples will be analyzed for dissolved gallium (Ga), barium (Ba), rare earth elements (REEs) along with dissolved methane. These studies are pertinent to important issues including delivery of mineral dust and nutrient iron to the surface ocean (Ga), removal and internal cycling of trace elements (Ba, REEs), development of paleoceanographic tracers (Ba), tracing sources of material (Ga, Ba, REEs, methane) including margin sources (Ba, REEs, methane), and understanding of conservative vs non-conservative changes in tracer distributions (Ba, REEs). Overall, the gradients in dust delivery, productivity, age of deep waters, and extent of oxygen minimum zones in the PMT provide opportunities to compare how trace element distributions are affected by these gradients and hence inform the interpretation of the distributions. The PMT will also provide the opportunity to examine evolution of chemical signals in deep and bottom waters in a basin with fewer water masses and a longer timescale of basin mixing than the Atlantic. As such, this data may provide an opportunity to tease apart conservative mixing from non-conservative biogeochemistry and will include using water mass deconvolution to estimate the conservative component of trace element distributions, element-AOU plots, and distributions of the deviations from global element-nutrient correlations. The cruise also allows extensive collaboration with other investigators. Thus, the dissolved Ga data will be compared with data obtained by colleagues on distributions of other lithogenic, rapidly-scavenged elements like aluminum (Al) and thorium-232; the dissolved Ba data will be shared with those determining radium and Ba isotopes; and, the REE data will be made available to those examining neodymium (Nd) isotopes as well as compared with other scavenging tracers such as scandium (Sc). Comparing our chemical distributions with those determined by others is key for all of the involved research groups to test hypothesized mechanisms of element input, removal, and cycling through the ocean. These mechanisms, in turn, are pertinent to understanding the ocean's biological productivity and its role in global climate.
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.
Funding Source | Award |
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NSF Division of Ocean Sciences (NSF OCE) |