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 |
Sampling protocol: GEOTRACES protocols were followed and are briefly described in the cruise report: https://www.bodc.ac.uk/resources/inventories/cruise_inventory/report/17252/. Profile samples were collected using a clean rosette/CTD system using cleaned 12-liter (L) GO Niskin-X bottles. Water was filtered in a clean van through AcroPak 1000 cartridges. Clean surface water samples were obtained using a clean fish system similar to systems used on US GEOTRACES cruises. A 6-meter (m) boom kept the sampling system away from the ship and low-density polyethylene tubing was used to pump water to the clean van. Note that samples were collected and filtered by other GP09 scientists; we provided pre-cleaned bottles that were filled at sea and shipped to us.
Analytical protocol: We used high-resolution inductively coupled plasma mass spectrometry (ICP-MS) with calibration by isotope dilution, where possible. All elements except Mo and Ba were preconcentrated using a SeaFAST system. Mo and Ba were instead determined after 30-fold dilution in ultrapure water. See GEOTRACES Intercalibration Report (see Supplemental Files section of metadata) for details. Also see: Gilbert et al., 2023 (Ga); Ho et al., 2018 (Mo, V), Whitmore et al., 2022 (Ba); Rahman et al., 2022 (Ba); and Cao et al., 2024 (REEs).
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 "KK1903_dataTemplate_Shiller.xlsx" into the BCO-DMO system.
- Renamed fields to comply with BCO-DMO naming conventions.
- Created start and end date-time columns in ISO8601 format.
- Removed Gear_ID column (not used).
- Saved the final file as "931959_v1_gp09_dissolved_trace_elements.csv".
- Converted the Intercalibration report from .docx to .pdf and attached it as a Supplemental File named "0000-0002-2068-7909-KK1903-multiple-param-intercal-report.pdf".
File |
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931959_v1_gp09_dissolved_trace_elements.csv (Comma Separated Values (.csv), 186.46 KB) MD5:057c5e0c237ebf1255cf4dce40ba506a Primary data file for dataset ID 931959, version 1 |
File |
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0000-0002-2068-7909-KK1903-multiple-param-intercal-report.pdf (Portable Document Format (.pdf), 1.71 MB) MD5:cc4408056ba1ebe7285819dfa8893723 Cruise KK1903 GEOTRACES Intercalibration Report for dataset 931959 (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 |
End_ISO_DateTime_UTC | Date and time (UTC) at end 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 |
End_Date_UTC | Date at end of sampling event | unitless |
End_Time_UTC | Time (UTC) at end of event | unitless |
Start_Latitude | Latitude at start of sampling event | decimal degrees |
Start_Longitude | Longitude at start of sampling event | decimal degrees |
End_Latitude | Latitude at end of sampling event | decimal degrees |
End_Longitude | Longitude at end of sampling event | decimal degrees |
Rosette_Position | Bottle position on rosette | unitless |
Sample_ID | Sample ID number | unitless |
Sample_Depth | Sample depth | meters (m) |
Ba_D_CONC_BOTTLE_itzwe9 | Concentration of dissolved Ba from bottle samples | nanomoles per kilogram (nmol/kg) |
SD1_Ba_D_CONC_BOTTLE_itzwe9 | Standard deviation of Ba_D_CONC_BOTTLE_itzwe9 | nanomoles per kilogram (nmol/kg) |
Flag_Ba_D_CONC_BOTTLE_itzwe9 | Quality flag for Ba_D_CONC_BOTTLE_itzwe9 | unitless |
Cu_D_CONC_BOTTLE_ccmjgy | Concentration of dissolved Cu from bottle samples | nanomoles per kilogram (nmol/kg) |
SD1_Cu_D_CONC_BOTTLE_ccmjgy | Standard deviation of Cu_D_CONC_BOTTLE_ccmjgy | nanomoles per kilogram (nmol/kg) |
Flag_Cu_D_CONC_BOTTLE_ccmjgy | Quality flag for Cu_D_CONC_BOTTLE_ccmjgy | unitless |
Ga_D_CONC_BOTTLE_8cvxtj | Concentration of dissolved Ga from bottle samples | picomoles per kilogram (pmol/kg) |
SD1_Ga_D_CONC_BOTTLE_8cvxtj | Standard deviation of Ga_D_CONC_BOTTLE_8cvxtj | picomoles per kilogram (pmol/kg) |
Flag_Ga_D_CONC_BOTTLE_8cvxtj | Quality flag for Ga_D_CONC_BOTTLE_8cvxtj | unitless |
Mn_D_CONC_BOTTLE_do8nav | Concentration of dissolved Mn from bottle samples | nanomoles per kilogram (nmol/kg) |
SD1_Mn_D_CONC_BOTTLE_do8nav | Standard deviation of Mn_D_CONC_BOTTLE_do8nav | nanomoles per kilogram (nmol/kg) |
Flag_Mn_D_CONC_BOTTLE_do8nav | Quality flag for Mn_D_CONC_BOTTLE_do8nav | unitless |
Mo_D_CONC_BOTTLE_ice49g | Concentration of dissolved Mo from bottle samples | nanomoles per kilogram (nmol/kg) |
SD1_Mo_D_CONC_BOTTLE_ice49g | Standard deviation of Mo_D_CONC_BOTTLE_ice49g | nanomoles per kilogram (nmol/kg) |
Flag_Mo_D_CONC_BOTTLE_ice49g | Quality flag for Mo_D_CONC_BOTTLE_ice49g | unitless |
Ni_D_CONC_BOTTLE_n7tn4h | Concentration of dissolved Ni from bottle samples | nanomoles per kilogram (nmol/kg) |
SD1_Ni_D_CONC_BOTTLE_n7tn4h | Standard deviation of Ni_D_CONC_BOTTLE_n7tn4h | nanomoles per kilogram (nmol/kg) |
Flag_Ni_D_CONC_BOTTLE_n7tn4h | Quality flag for Ni_D_CONC_BOTTLE_n7tn4h | unitless |
Pb_D_CONC_BOTTLE_5g4emy | Concentration of dissolved Pb from bottle samples | picomoles per kilogram (pmol/kg) |
SD1_Pb_D_CONC_BOTTLE_5g4emy | Standard deviation of Pb_D_CONC_BOTTLE_5g4emy | picomoles per kilogram (pmol/kg) |
Flag_Pb_D_CONC_BOTTLE_5g4emy | Quality flag for Pb_D_CONC_BOTTLE_5g4emy | unitless |
V_D_CONC_BOTTLE_rps5rc | Concentration of dissolved V from bottle samples | nanomoles per kilogram (nmol/kg) |
SD1_V_D_CONC_BOTTLE_rps5rc | Standard deviation of V_D_CONC_BOTTLE_rps5rc | nanomoles per kilogram (nmol/kg) |
Flag_V_D_CONC_BOTTLE_rps5rc | Quality flag for V_D_CONC_BOTTLE_rps5rc | unitless |
Y_D_CONC_BOTTLE_i4xjdi | Concentration of dissolved Y from bottle samples | picomoles per kilogram (pmol/kg) |
SD1_Y_D_CONC_BOTTLE_i4xjdi | Standard deviation of Y_D_CONC_BOTTLE_i4xjdi | picomoles per kilogram (pmol/kg) |
Flag_Y_D_CONC_BOTTLE_i4xjdi | Quality flag for Y_D_CONC_BOTTLE_i4xjdi | unitless |
La_D_CONC_BOTTLE_0i4lyy | Concentration of dissolved La from bottle samples | picomoles per kilogram (pmol/kg) |
SD1_La_D_CONC_BOTTLE_0i4lyy | Standard deviation of La_D_CONC_BOTTLE_0i4lyy | picomoles per kilogram (pmol/kg) |
Flag_La_D_CONC_BOTTLE_0i4lyy | Quality flag for La_D_CONC_BOTTLE_0i4lyy | unitless |
Ce_D_CONC_BOTTLE_5ujocf | Concentration of dissolved Ce from bottle samples | picomoles per kilogram (pmol/kg) |
SD1_Ce_D_CONC_BOTTLE_5ujocf | Standard deviation of Ce_D_CONC_BOTTLE_5ujocf | picomoles per kilogram (pmol/kg) |
Flag_Ce_D_CONC_BOTTLE_5ujocf | Quality flag for Ce_D_CONC_BOTTLE_5ujocf | unitless |
Pr_D_CONC_BOTTLE_hxzcbb | Concentration of dissolved Pr from bottle samples | picomoles per kilogram (pmol/kg) |
SD1_Pr_D_CONC_BOTTLE_hxzcbb | Standard deviation of Pr_D_CONC_BOTTLE_hxzcbb | picomoles per kilogram (pmol/kg) |
Flag_Pr_D_CONC_BOTTLE_hxzcbb | Quality flag for Pr_D_CONC_BOTTLE_hxzcbb | unitless |
Nd_D_CONC_BOTTLE_dlc4ah | Concentration of dissolved Nd from bottle samples | picomoles per kilogram (pmol/kg) |
SD1_Nd_D_CONC_BOTTLE_dlc4ah | Standard deviation of Nd_D_CONC_BOTTLE_dlc4ah | picomoles per kilogram (pmol/kg) |
Flag_Nd_D_CONC_BOTTLE_dlc4ah | Quality flag for Nd_D_CONC_BOTTLE_dlc4ah | unitless |
Sm_D_CONC_BOTTLE_t6f5zy | Concentration of dissolved Sm from bottle samples | picomoles per kilogram (pmol/kg) |
SD1_Sm_D_CONC_BOTTLE_t6f5zy | Standard deviation of Sm_D_CONC_BOTTLE_t6f5zy | picomoles per kilogram (pmol/kg) |
Flag_Sm_D_CONC_BOTTLE_t6f5zy | Quality flag for Sm_D_CONC_BOTTLE_t6f5zy | unitless |
Eu_D_CONC_BOTTLE_07fvuy | Concentration of dissolved Eu from bottle samples | picomoles per kilogram (pmol/kg) |
SD1_Eu_D_CONC_BOTTLE_07fvuy | Standard deviation of Eu_D_CONC_BOTTLE_07fvuy | picomoles per kilogram (pmol/kg) |
Flag_Eu_D_CONC_BOTTLE_07fvuy | Quality flag for Eu_D_CONC_BOTTLE_07fvuy | unitless |
Gd_D_CONC_BOTTLE_yk78vk | Concentration of dissolved Gd from bottle samples | picomoles per kilogram (pmol/kg) |
SD1_Gd_D_CONC_BOTTLE_yk78vk | Standard deviation of Gd_D_CONC_BOTTLE_yk78vk | picomoles per kilogram (pmol/kg) |
Flag_Gd_D_CONC_BOTTLE_yk78vk | Quality flag for Gd_D_CONC_BOTTLE_yk78vk | unitless |
Tb_D_CONC_BOTTLE_9zjxfm | Concentration of dissolved Tb from bottle samples | picomoles per kilogram (pmol/kg) |
SD1_Tb_D_CONC_BOTTLE_9zjxfm | Standard deviation of Tb_D_CONC_BOTTLE_9zjxfm | picomoles per kilogram (pmol/kg) |
Flag_Tb_D_CONC_BOTTLE_9zjxfm | Quality flag for Tb_D_CONC_BOTTLE_9zjxfm | unitless |
Dy_D_CONC_BOTTLE_khzysy | Concentration of dissolved Dy from bottle samples | picomoles per kilogram (pmol/kg) |
SD1_Dy_D_CONC_BOTTLE_khzysy | Standard deviation of Dy_D_CONC_BOTTLE_khzysy | picomoles per kilogram (pmol/kg) |
Flag_Dy_D_CONC_BOTTLE_khzysy | Quality flag for Dy_D_CONC_BOTTLE_khzysy | unitless |
Ho_D_CONC_BOTTLE_rrxp5y | Concentration of dissolved Ho from bottle samples | picomoles per kilogram (pmol/kg) |
SD1_Ho_D_CONC_BOTTLE_rrxp5y | Standard deviation of Ho_D_CONC_BOTTLE_rrxp5y | picomoles per kilogram (pmol/kg) |
Flag_Ho_D_CONC_BOTTLE_rrxp5y | Quality flag for Ho_D_CONC_BOTTLE_rrxp5y | unitless |
Er_D_CONC_BOTTLE_rzsrsx | Concentration of dissolved Er from bottle samples | picomoles per kilogram (pmol/kg) |
SD1_Er_D_CONC_BOTTLE_rzsrsx | Standard deviation of Er_D_CONC_BOTTLE_rzsrsx | picomoles per kilogram (pmol/kg) |
Flag_Er_D_CONC_BOTTLE_rzsrsx | Quality flag for Er_D_CONC_BOTTLE_rzsrsx | unitless |
Tm_D_CONC_BOTTLE_thtfhx | Concentration of dissolved Tm from bottle samples | picomoles per kilogram (pmol/kg) |
SD1_Tm_D_CONC_BOTTLE_thtfhx | Standard deviation of Tm_D_CONC_BOTTLE_thtfhx | picomoles per kilogram (pmol/kg) |
Flag_Tm_D_CONC_BOTTLE_thtfhx | Quality flag for Tm_D_CONC_BOTTLE_thtfhx | unitless |
Yb_D_CONC_BOTTLE_ft7p4l | Concentration of dissolved Yb from bottle samples | picomoles per kilogram (pmol/kg) |
SD1_Yb_D_CONC_BOTTLE_ft7p4l | Standard deviation of Yb_D_CONC_BOTTLE_ft7p4l | picomoles per kilogram (pmol/kg) |
Flag_Yb_D_CONC_BOTTLE_ft7p4l | Quality flag for Yb_D_CONC_BOTTLE_ft7p4l | unitless |
Lu_D_CONC_BOTTLE_vm4rjv | Concentration of dissolved Lu from bottle samples | picomoles per kilogram (pmol/kg) |
SD1_Lu_D_CONC_BOTTLE_vm4rjv | Standard deviation of Lu_D_CONC_BOTTLE_vm4rjv | picomoles per kilogram (pmol/kg) |
Flag_Lu_D_CONC_BOTTLE_vm4rjv | Quality flag for Lu_D_CONC_BOTTLE_vm4rjv | unitless |
Ba_D_CONC_FISH_hra1ob | Concentration of dissolved Ba from towed fish samples | nanomoles per kilogram (nmol/kg) |
SD1_Ba_D_CONC_FISH_hra1ob | Standard deviation of Ba_D_CONC_FISH_hra1ob | nanomoles per kilogram (nmol/kg) |
Flag_Ba_D_CONC_FISH_hra1ob | Quality flag for Ba_D_CONC_FISH_hra1ob | unitless |
Cu_D_CONC_FISH_1baozt | Concentration of dissolved Cu from towed fish samples | nanomoles per kilogram (nmol/kg) |
SD1_Cu_D_CONC_FISH_1baozt | Standard deviation of Cu_D_CONC_FISH_1baozt | nanomoles per kilogram (nmol/kg) |
Flag_Cu_D_CONC_FISH_1baozt | Quality flag for Cu_D_CONC_FISH_1baozt | unitless |
Ga_D_CONC_FISH_dly4du | Concentration of dissolved Ga from towed fish samples | picomoles per kilogram (pmol/kg) |
SD1_Ga_D_CONC_FISH_dly4du | Standard deviation of Ga_D_CONC_FISH_dly4du | picomoles per kilogram (pmol/kg) |
Flag_Ga_D_CONC_FISH_dly4du | Quality flag for Ga_D_CONC_FISH_dly4du | unitless |
Mn_D_CONC_FISH_b7capx | Concentration of dissolved Mn from towed fish samples | nanomoles per kilogram (nmol/kg) |
SD1_Mn_D_CONC_FISH_b7capx | Standard deviation of Mn_D_CONC_FISH_b7capx | nanomoles per kilogram (nmol/kg) |
Flag_Mn_D_CONC_FISH_b7capx | Quality flag for Mn_D_CONC_FISH_b7capx | unitless |
Mo_D_CONC_FISH_nuboeh | Concentration of dissolved Mo from towed fish samples | nanomoles per kilogram (nmol/kg) |
SD1_Mo_D_CONC_FISH_nuboeh | Standard deviation of Mo_D_CONC_FISH_nuboeh | nanomoles per kilogram (nmol/kg) |
Flag_Mo_D_CONC_FISH_nuboeh | Quality flag for Mo_D_CONC_FISH_nuboeh | unitless |
Ni_D_CONC_FISH_uxcluf | Concentration of dissolved Ni from towed fish samples | nanomoles per kilogram (nmol/kg) |
SD1_Ni_D_CONC_FISH_uxcluf | Standard deviation of Ni_D_CONC_FISH_uxcluf | nanomoles per kilogram (nmol/kg) |
Flag_Ni_D_CONC_FISH_uxcluf | Quality flag for Ni_D_CONC_FISH_uxcluf | unitless |
Pb_D_CONC_FISH_n6tdnb | Concentration of dissolved Pb from towed fish samples | picomoles per kilogram (pmol/kg) |
SD1_Pb_D_CONC_FISH_n6tdnb | Standard deviation of Pb_D_CONC_FISH_n6tdnb | picomoles per kilogram (pmol/kg) |
Flag_Pb_D_CONC_FISH_n6tdnb | Quality flag for Pb_D_CONC_FISH_n6tdnb | unitless |
V_D_CONC_FISH_opbkyb | Concentration of dissolved V from towed fish samples | nanomoles per kilogram (nmol/kg) |
SD1_V_D_CONC_FISH_opbkyb | Standard deviation of V_D_CONC_FISH_opbkyb | nanomoles per kilogram (nmol/kg) |
Flag_V_D_CONC_FISH_opbkyb | Quality flag for V_D_CONC_FISH_opbkyb | unitless |
Y_D_CONC_FISH_tmyjc3 | Concentration of dissolved Y from towed fish samples | picomoles per kilogram (pmol/kg) |
SD1_Y_D_CONC_FISH_tmyjc3 | Standard deviation of Y_D_CONC_FISH_tmyjc3 | picomoles per kilogram (pmol/kg) |
Flag_Y_D_CONC_FISH_tmyjc3 | Quality flag for Y_D_CONC_FISH_tmyjc3 | unitless |
La_D_CONC_FISH_j3fhke | Concentration of dissolved La from towed fish samples | picomoles per kilogram (pmol/kg) |
SD1_La_D_CONC_FISH_j3fhke | Standard deviation of La_D_CONC_FISH_j3fhke | picomoles per kilogram (pmol/kg) |
Flag_La_D_CONC_FISH_j3fhke | Quality flag for La_D_CONC_FISH_j3fhke | unitless |
Ce_D_CONC_FISH_zhuata | Concentration of dissolved Ce from towed fish samples | picomoles per kilogram (pmol/kg) |
SD1_Ce_D_CONC_FISH_zhuata | Standard deviation of Ce_D_CONC_FISH_zhuata | picomoles per kilogram (pmol/kg) |
Flag_Ce_D_CONC_FISH_zhuata | Quality flag for Ce_D_CONC_FISH_zhuata | unitless |
Pr_D_CONC_FISH_iqdohc | Concentration of dissolved Pr from towed fish samples | picomoles per kilogram (pmol/kg) |
SD1_Pr_D_CONC_FISH_iqdohc | Standard deviation of Pr_D_CONC_FISH_iqdohc | picomoles per kilogram (pmol/kg) |
Flag_Pr_D_CONC_FISH_iqdohc | Quality flag for Pr_D_CONC_FISH_iqdohc | unitless |
Nd_D_CONC_FISH_atm156 | Concentration of dissolved Nd from towed fish samples | picomoles per kilogram (pmol/kg) |
SD1_Nd_D_CONC_FISH_atm156 | Standard deviation of Nd_D_CONC_FISH_atm156 | picomoles per kilogram (pmol/kg) |
Flag_Nd_D_CONC_FISH_atm156 | Quality flag for Nd_D_CONC_FISH_atm156 | unitless |
Sm_D_CONC_FISH_1vsmf0 | Concentration of dissolved Sm from towed fish samples | picomoles per kilogram (pmol/kg) |
SD1_Sm_D_CONC_FISH_1vsmf0 | Standard deviation of Sm_D_CONC_FISH_1vsmf0 | picomoles per kilogram (pmol/kg) |
Flag_Sm_D_CONC_FISH_1vsmf0 | Quality flag for Sm_D_CONC_FISH_1vsmf0 | unitless |
Eu_D_CONC_FISH_xodk9s | Concentration of dissolved Eu from towed fish samples | picomoles per kilogram (pmol/kg) |
SD1_Eu_D_CONC_FISH_xodk9s | Standard deviation of Eu_D_CONC_FISH_xodk9s | picomoles per kilogram (pmol/kg) |
Flag_Eu_D_CONC_FISH_xodk9s | Quality flag for Eu_D_CONC_FISH_xodk9s | unitless |
Gd_D_CONC_FISH_xiy5ir | Concentration of dissolved Gd from towed fish samples | picomoles per kilogram (pmol/kg) |
SD1_Gd_D_CONC_FISH_xiy5ir | Standard deviation of Gd_D_CONC_FISH_xiy5ir | picomoles per kilogram (pmol/kg) |
Flag_Gd_D_CONC_FISH_xiy5ir | Quality flag for Gd_D_CONC_FISH_xiy5ir | unitless |
Tb_D_CONC_FISH_nvbybp | Concentration of dissolved Tb from towed fish samples | picomoles per kilogram (pmol/kg) |
SD1_Tb_D_CONC_FISH_nvbybp | Standard deviation of Tb_D_CONC_FISH_nvbybp | picomoles per kilogram (pmol/kg) |
Flag_Tb_D_CONC_FISH_nvbybp | Quality flag for Tb_D_CONC_FISH_nvbybp | unitless |
Dy_D_CONC_FISH_50moex | Concentration of dissolved Dy from towed fish samples | picomoles per kilogram (pmol/kg) |
SD1_Dy_D_CONC_FISH_50moex | Standard deviation of Dy_D_CONC_FISH_50moex | picomoles per kilogram (pmol/kg) |
Flag_Dy_D_CONC_FISH_50moex | Quality flag for Dy_D_CONC_FISH_50moex | unitless |
Ho_D_CONC_FISH_r1m8ab | Concentration of dissolved Ho from towed fish samples | picomoles per kilogram (pmol/kg) |
SD1_Ho_D_CONC_FISH_r1m8ab | Standard deviation of Ho_D_CONC_FISH_r1m8ab | picomoles per kilogram (pmol/kg) |
Flag_Ho_D_CONC_FISH_r1m8ab | Quality flag for Ho_D_CONC_FISH_r1m8ab | unitless |
Er_D_CONC_FISH_aemigv | Concentration of dissolved Er from towed fish samples | picomoles per kilogram (pmol/kg) |
SD1_Er_D_CONC_FISH_aemigv | Standard deviation of Er_D_CONC_FISH_aemigv | picomoles per kilogram (pmol/kg) |
Flag_Er_D_CONC_FISH_aemigv | Quality flag for Er_D_CONC_FISH_aemigv | unitless |
Tm_D_CONC_FISH_k9km6b | Concentration of dissolved Tm from towed fish samples | picomoles per kilogram (pmol/kg) |
SD1_Tm_D_CONC_FISH_k9km6b | Standard deviation of Tm_D_CONC_FISH_k9km6b | picomoles per kilogram (pmol/kg) |
Flag_Tm_D_CONC_FISH_k9km6b | Quality flag for Tm_D_CONC_FISH_k9km6b | unitless |
Yb_D_CONC_FISH_t7qjfy | Concentration of dissolved Yb from towed fish samples | picomoles per kilogram (pmol/kg) |
SD1_Yb_D_CONC_FISH_t7qjfy | Standard deviation of Yb_D_CONC_FISH_t7qjfy | picomoles per kilogram (pmol/kg) |
Flag_Yb_D_CONC_FISH_t7qjfy | Quality flag for Yb_D_CONC_FISH_t7qjfy | unitless |
Lu_D_CONC_FISH_q2njui | Concentration of dissolved Lu from towed fish samples | picomoles per kilogram (pmol/kg) |
SD1_Lu_D_CONC_FISH_q2njui | Standard deviation of Lu_D_CONC_FISH_q2njui | picomoles per kilogram (pmol/kg) |
Flag_Lu_D_CONC_FISH_q2njui | Quality flag for Lu_D_CONC_FISH_q2njui | unitless |
Dataset-specific Instrument Name | 12-L GO Niskin-X bottles |
Generic Instrument Name | Niskin bottle |
Generic 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. |
Dataset-specific Instrument Name | ThermoFisher Element XR ICP-MS |
Generic Instrument Name | Thermo Scientific ELEMENT XR high resolution inductively coupled plasma mass spectrometer |
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. |
Dataset-specific Instrument Name | a clean fish system similar to systems used on US GEOTRACES cruises |
Generic Instrument Name | towed undulating vehicle |
Generic Instrument Description | A towed undulating vehicle is a generic class of instruments. See the data set specific information for a detailed description. These are often prototype instrument packages designed to make very specific measurements. |
Website | |
Platform | R/V Tan Kah Kee |
Report | |
Start Date | 2019-04-25 |
End Date | 2019-06-13 |
NSF Award Abstract:
This project involves a collaboration with Chinese scientists in the analysis of seawater samples collected during mid-2019 in the Northwest Pacific Ocean. The cruise (designated GP09) is part of an international collaborative research effort known as GEOTRACES, which is examining the distributions of trace elements and isotopes throughout the oceans. Some trace elements are micro-nutrients in the ocean, others are potentially toxic in small quantities, and still others can be tracers or indictors of the extent of various ocean processes such as hydrothermal inputs or productivity. The GP09 cruise affords an opportunity to obtain trace element clean water samples from a region that is geologically complex as well as being a meeting place for various ocean currents and water masses. It will sample the southwest corner of the North Pacific subtropical gyre, one of the largest oligotrophic (i.e., low nutrient) ocean regions and arguably the largest continuous ecosystem on Earth. This region is likely impacted by dust input (including anthropogenic aerosols), nitrogen fixation, hydrothermal inputs, and island effects associated with weathering of the Philippines and margin cycling. Determining material sources, sinks, and cycling in this region is ultimately important for understanding controls on the region's productivity. Many of the trace elements to be determined are also of relevance for paleo-proxy applications (i.e., for understanding what the sediment records of these elements tell us about past ocean processes). However, successful paleo-proxy applications generally require further insight into the processes that affect the cycling of the proxy elements. Because of the wide range of parameters to be determined by GP09 participants, the cruise affords substantial opportunities for collaboration with Chinese colleagues. The knowledge and experience gained from this project will be incorporated into the principle investigator's courses in oceanography. For outreach activities, in collaboration with the University of Southern Mississippi Marine Education Center, high school students will be invited to attend lectures given by scientists about their research. A postdoctoral scholar will also be trained as part of the project
A researcher from the University of Southern Mississippi will obtain clean, filtered trace element samples from a mid-2019 oceanographic research cruise in the Northwest Pacific Ocean. The cruise (GP09) is part of the GEOTRACES program and was led by researchers from Xiamen University, China, with additional participants from other major Chinese oceanographic institutions. The geological and hydrographic complexity, along with the oligotrophic nature of the GP09 cruise track, make this an especially interesting region for study. Trace element distributions are likely to provide insight into various source, sink, and cycling processes of broad interest. For example, a number of the elements we will study have been used (or proposed to be used) as paleoredox and paleoproductivity proxies [e.g., barium (Ba), rare earth elements (REEs), vanadium (V), cadmium (Cd)], but a better understanding of their oceanic cycling is needed to more fully understand their proxy signals. The studies proposed here are also pertinent to important issues including delivery of mineral dust and nutrient iron to the surface ocean [gallium (Ga), REEs and possibly Cd and V], removal and internal cycling of trace elements [Ba, REEs], tracing sources of material including margin sources [Ba, manganese (Mn), REEs, V] and hydrothermal influences [Mn, Ba, REEs], as well as understanding of conservative versus non-conservative changes in tracer distributions [Ba, REEs, V]. The cruise also allows extensive collaboration with other, mainly Chinese, 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 isotopes, as well as compared with other scavenging tracers such as Ga, Al, and Th.
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.
Funding Source | Award |
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NSF Division of Ocean Sciences (NSF OCE) |