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Grid DAP Data | Sub- set | Table DAP Data | Make A Graph | W M S | Source Data Files | Acces- sible | Title | Sum- mary | FGDC, ISO, Metadata | Back- ground Info | RSS | E | Institution | Dataset ID |
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data | graph | files | public | [Table 2 - Carbonate data and nutrients during egg experiments] - Table 2: Carbonate data and nutrients measured during Calanus finmarchicus and Meganyctiphanes norvegica egg hatching success experiments, 2011-2012 (Ocean Acidification-Category 1- Impact of ocean acidification on survival of early life stages of planktonic copepods in the genus Calanus in the northern) | I M | background | BCO-DMO | bcodmo_dataset_738494 |
Row Type | Variable Name | Attribute Name | Data Type | Value |
---|---|---|---|---|
attribute | NC_GLOBAL | access_formats | String | .htmlTable,.csv,.json,.mat,.nc,.tsv |
attribute | NC_GLOBAL | acquisition_description | String | Total Alkalinity:\u00a0 Alkalinity was determined using an open cell titration with HCl (Dickson et al., 2007).\u00a0 The pH meter was a Corning model 109 which had been adapted so that the millivolt out was logged by computer through a 14 bit A to D converter.\u00a0 The electrode was an Orion Ross ultra semi-micro glass electrode model 8103-BNUWP.\u00a0 The pH electrode was standardized with accurate pH buffers.\u00a0 The tris buffer ( 2-amino-2-hydroxymethyl-1,3-propanediol) had a pH of about 8.09 depending on temperature.\u00a0 The AMP buffer (2-aminopyridine) had a pH of about 6.79 depending on temperature.\u00a0 Both were dissolved in artificial seawater at S = 35 (Dickson et al., 2007, SOP-6a).\u00a0 Samples and standards were titrated with a 0.15 M HCl solution in 0.45 M NaCl and the temperature was measured to the nearest 0.01C using a NIST calibrated platinum thermometer.\u00a0 The alkalinity standards generally were precise alkalinity/total carbon dioxide seawater standards from Scripps Institute of Oceanography (SIO), but early experiments also used a phosphate buffer standard comprised of an equal molar mixture of KH2PO4\u00a0and Na2HPO4\u00a0-7 H2O in 0.70 M NaCl.\u00a0 This phosphate standard was cross calibrated with the SIO standards.\u00a0 The procedure used generally gave the precision of several replicate standard titrations of 0.06% (standard error of the mean as percent of the mean value).\u00a0 Alkalinities were determined by the fitting procedure described in Dickson et al., 2007 (SOP-3b). Total Carbon Dioxide:\u00a0 These concentrations were determined by acid stripping a 1.113 ml volume of water sample or TCO2\u00a0standard, trapping the expelled CO2, and then injecting it into a Shimadzu Model GC-8A gas chromatograph with a thermal conductivity detector (Christensen, 2008).\u00a0 Two standards were employed, ones made from prebaked and freshly made Na2CO3, and the previously mentioned SIO total carbon dioxide seawater standards.\u00a0 This analytical system obtained a precision of about 0.06% (standard error of the mean as percent of the mean).\u00a0 However, in the results listed in this report, precision was less, averaging about 0.25% (standard error of the mean as percent of the mean) because sample analysis time was speeded up causing slightly less efficient trapping of the sample's CO2.\u00a0 Salinity and Nutrients:\u00a0 Salinity was determined using an Autosal 8400A conductivity salinometer with IAPSO standard seawater standards.\u00a0 Replicate determinations of a single sample were made until two consecutive readings of conductivity matched within +/- 0.002 ppt.\u00a0 Nutrients were determined by autoanalyzer using the methods for nitrate and nitrite of Armstrong et al. (1967) and Pavlou (1972), for ammonium of Koroleff (1970) and Slawyk and MacIsaac (1972), for dissolved inorganic phosphate (Drummond and Maher, 1995), and dissolved silicate (Armstrong et al., 1967).\u00a0 Concentrations were measured in mol L-1\u00a0and converted to mol kg-1\u00a0based on the sample's sigma-t value computed from the sample's salinity and the laboratory temperature during analysis. Calculation of Carbonate System Parameters:\u00a0 Carbonate system parameters, include total pH, were calculated from the measured chemistry of the water samples using the carbonate equilibrium model, CO2SYS (DOE, 1994; Lewis and Wallace, 1995).\u00a0 This program employs the equilibrium coefficients of Roy et al. (1993) for carbonate coefficients, K1 and K2, of Weiss (1974) for carbon dioxide, K0, of Dickson (1990a) for borate, of Dickson and Riley (1979) for fluoride, of Dickson (1990b) for sulfate, and of Millero (1995) for phosphate (kp1, kp2, kp3) and silicate.\u00a0 Seawater density at atmospheric pressure was that of UNESCO (1981). |
attribute | NC_GLOBAL | awards_0_award_nid | String | 54712 |
attribute | NC_GLOBAL | awards_0_award_number | String | OCE-1041081 |
attribute | NC_GLOBAL | awards_0_data_url | String | http://www.nsf.gov/awardsearch/showAward.do?AwardNumber=1041081 |
attribute | NC_GLOBAL | awards_0_funder_name | String | NSF Division of Ocean Sciences |
attribute | NC_GLOBAL | awards_0_funding_acronym | String | NSF OCE |
attribute | NC_GLOBAL | awards_0_funding_source_nid | String | 355 |
attribute | NC_GLOBAL | awards_0_program_manager | String | David L. Garrison |
attribute | NC_GLOBAL | awards_0_program_manager_nid | String | 50534 |
attribute | NC_GLOBAL | cdm_data_type | String | Other |
attribute | NC_GLOBAL | comment | String | Carbonate data and nutrients during egg experiments OCEAN PH AFFECTS CALANUS EGGS - TABLE 2, Preziosi, et al (2017) Mar. Bio. DOI 10.1007/s00227-017-3243-5 PI's: J. Christensen (Green Eyes LLC), J. Runge (GMRI) version: 2018-06-13 |
attribute | NC_GLOBAL | Conventions | String | COARDS, CF-1.6, ACDD-1.3 |
attribute | NC_GLOBAL | creator_email | String | info at bco-dmo.org |
attribute | NC_GLOBAL | creator_name | String | BCO-DMO |
attribute | NC_GLOBAL | creator_type | String | institution |
attribute | NC_GLOBAL | creator_url | String | https://www.bco-dmo.org/ |
attribute | NC_GLOBAL | data_source | String | extract_data_as_tsv version 2.3 19 Dec 2019 |
attribute | NC_GLOBAL | date_created | String | 2018-06-13T19:08:44Z |
attribute | NC_GLOBAL | date_modified | String | 2019-12-04T15:21:32Z |
attribute | NC_GLOBAL | defaultDataQuery | String | &time<now |
attribute | NC_GLOBAL | doi | String | 10.1575/1912/bco-dmo.738494.1 |
attribute | NC_GLOBAL | infoUrl | String | https://www.bco-dmo.org/dataset/738494 |
attribute | NC_GLOBAL | institution | String | BCO-DMO |
attribute | NC_GLOBAL | instruments_0_acronym | String | Nutrient Autoanalyzer |
attribute | NC_GLOBAL | instruments_0_dataset_instrument_nid | String | 738507 |
attribute | NC_GLOBAL | instruments_0_description | String | Nutrient Autoanalyzer is a generic term used when specific type, make and model were not specified. In general, a Nutrient Autoanalyzer is an automated flow-thru system for doing nutrient analysis (nitrate, ammonium, orthophosphate, and silicate) on seawater samples. |
attribute | NC_GLOBAL | instruments_0_instrument_external_identifier | String | https://vocab.nerc.ac.uk/collection/L05/current/LAB04/ |
attribute | NC_GLOBAL | instruments_0_instrument_name | String | Nutrient Autoanalyzer |
attribute | NC_GLOBAL | instruments_0_instrument_nid | String | 558 |
attribute | NC_GLOBAL | instruments_1_acronym | String | salinometer |
attribute | NC_GLOBAL | instruments_1_dataset_instrument_description | String | Used to measure salinity, with IAPSO seawater standards. |
attribute | NC_GLOBAL | instruments_1_dataset_instrument_nid | String | 738506 |
attribute | NC_GLOBAL | instruments_1_description | String | The salinometer is an instrument for measuring the salinity of a water sample. |
attribute | NC_GLOBAL | instruments_1_instrument_external_identifier | String | https://vocab.nerc.ac.uk/collection/L05/current/LAB30/ |
attribute | NC_GLOBAL | instruments_1_instrument_name | String | Autosal salinometer |
attribute | NC_GLOBAL | instruments_1_instrument_nid | String | 576 |
attribute | NC_GLOBAL | instruments_1_supplied_name | String | Autosal 8400A conductivity salinometer |
attribute | NC_GLOBAL | instruments_2_acronym | String | Gas Chromatograph |
attribute | NC_GLOBAL | instruments_2_dataset_instrument_description | String | Used to measure Total CO2, determined by acid stripping a 1.113 ml volume of water sample or TCO2 standard, trapping the expelled CO2, and then injecting it into the chromatograph had a thermal conductivity detector. |
attribute | NC_GLOBAL | instruments_2_dataset_instrument_nid | String | 738505 |
attribute | NC_GLOBAL | instruments_2_description | String | Instrument separating gases, volatile substances, or substances dissolved in a volatile solvent by transporting an inert gas through a column packed with a sorbent to a detector for assay. (from SeaDataNet, BODC) |
attribute | NC_GLOBAL | instruments_2_instrument_external_identifier | String | https://vocab.nerc.ac.uk/collection/L05/current/LAB02/ |
attribute | NC_GLOBAL | instruments_2_instrument_name | String | Gas Chromatograph |
attribute | NC_GLOBAL | instruments_2_instrument_nid | String | 661 |
attribute | NC_GLOBAL | instruments_2_supplied_name | String | Shimadzu Model GC-8A gas chromatograph |
attribute | NC_GLOBAL | instruments_3_acronym | String | Benchtop pH Meter |
attribute | NC_GLOBAL | instruments_3_dataset_instrument_description | String | Adapted so that the millivolt out was logged by computer through a 14 bit A to D converter. The electrode was an Orion Ross ultra semi-micro glass electrode model 8103-BNUWP. |
attribute | NC_GLOBAL | instruments_3_dataset_instrument_nid | String | 738501 |
attribute | NC_GLOBAL | instruments_3_description | String | An instrument consisting of an electronic voltmeter and pH-responsive electrode that gives a direct conversion of voltage differences to differences of pH at the measurement temperature. (McGraw-Hill Dictionary of Scientific and Technical Terms) This instrument does not map to the NERC instrument vocabulary term for 'pH Sensor' which measures values in the water column. Benchtop models are typically employed for stationary lab applications. |
attribute | NC_GLOBAL | instruments_3_instrument_name | String | Benchtop pH Meter |
attribute | NC_GLOBAL | instruments_3_instrument_nid | String | 681 |
attribute | NC_GLOBAL | instruments_3_supplied_name | String | Corning model 109 |
attribute | NC_GLOBAL | keywords | String | alkalin, altimetry, ammonia, ammonium, bco, bco-dmo, biological, chemical, chemistry, concentration, data, dataset, date, dmo, earth, Earth Science > Oceans > Ocean Chemistry > Ammonia, Earth Science > Oceans > Ocean Chemistry > Nitrate, Earth Science > Oceans > Ocean Chemistry > Phosphate, Earth Science > Oceans > Ocean Chemistry > Silicate, elapsed, erddap, event, experiment, laboratory, management, mass, mass_concentration_of_phosphate_in_sea_water, mass_concentration_of_silicate_in_sea_water, mole, mole_concentration_of_ammonium_in_sea_water, mole_concentration_of_nitrate_in_sea_water, n02, nh4, nitrate, no3, NO3_NO2, ocean, oceanography, oceans, office, omar, omca, phosphate, phttl, po4, preliminary, sal, sampling, SAMPLING_DATE, satellite, science, sea, seawater, silicate, tank, tco2, TEMP, temperature, time, TIME_elapsed, water, xco2 |
attribute | NC_GLOBAL | keywords_vocabulary | String | GCMD Science Keywords |
attribute | NC_GLOBAL | license | String | https://www.bco-dmo.org/dataset/738494/license |
attribute | NC_GLOBAL | metadata_source | String | https://www.bco-dmo.org/api/dataset/738494 |
attribute | NC_GLOBAL | param_mapping | String | {'738494': {}} |
attribute | NC_GLOBAL | parameter_source | String | https://www.bco-dmo.org/mapserver/dataset/738494/parameters |
attribute | NC_GLOBAL | people_0_affiliation | String | Green Eyes LLC |
attribute | NC_GLOBAL | people_0_person_name | String | John P Christensen |
attribute | NC_GLOBAL | people_0_person_nid | String | 51603 |
attribute | NC_GLOBAL | people_0_role | String | Principal Investigator |
attribute | NC_GLOBAL | people_0_role_type | String | originator |
attribute | NC_GLOBAL | people_1_affiliation | String | Gulf of Maine Research Institute |
attribute | NC_GLOBAL | people_1_affiliation_acronym | String | GMRI |
attribute | NC_GLOBAL | people_1_person_name | String | Jeffrey A. Runge |
attribute | NC_GLOBAL | people_1_person_nid | String | 50905 |
attribute | NC_GLOBAL | people_1_role | String | Co-Principal Investigator |
attribute | NC_GLOBAL | people_1_role_type | String | originator |
attribute | NC_GLOBAL | people_2_affiliation | String | Woods Hole Oceanographic Institution |
attribute | NC_GLOBAL | people_2_affiliation_acronym | String | WHOI BCO-DMO |
attribute | NC_GLOBAL | people_2_person_name | String | Nancy Copley |
attribute | NC_GLOBAL | people_2_person_nid | String | 50396 |
attribute | NC_GLOBAL | people_2_role | String | BCO-DMO Data Manager |
attribute | NC_GLOBAL | people_2_role_type | String | related |
attribute | NC_GLOBAL | project | String | OA Calanus Survival |
attribute | NC_GLOBAL | projects_0_acronym | String | OA Calanus Survival |
attribute | NC_GLOBAL | projects_0_description | String | The project description is a modification of the original NSF award abstract. This research project is part of the larger NSF funded CRI-OA collaborative research initiative and was funded as an Ocean Acidification-Category 1, 2010 award. While attention concerning impacts of predicted acidification of the world's oceans has focused on calcifying organisms, non-calcifying plankton may also be vulnerable. In this project, the investigator will evaluate the potential for impacts of ocean acidification on the reproductive success of three species of planktonic copepods in the genus Calanus that are prominent in high latitude oceans. C. finmarchicus dominates the mesozooplankton biomass across much of the coastal and deep North Atlantic Ocean. C. glacialis and the larger C. hyperboreus are among the most abundant planktonic copepods in the Arctic Ocean. Previous research showed that hatching success of C. finmarchicus eggs was severely inhibited by increased CO2 and lower pH in seawater, but only tested at an extreme level. Preliminary results in the investigator's laboratory indicate that hatching success of C. finmarchicus is substantially reduced at increased seawater CO2 concentrations corresponding to pH levels between 7.9 and 7.5. Predictions of likely decline of surface pH levels to 7.7-7.8 over the next century raise questions about impacts on Calanus population dynamics if these preliminary results are confirmed. C. finmarchicus, for example, is presently at the southern edge of its range in the Gulf of Maine. The combination of higher surface layer temperature and lower pH may inhibit reproductive success during the late summer/fall bloom, which the PI hypothesize is critical to sustain the overwintering stock in this region. The investigators will collect C. finmarchicus females from the Gulf of Maine and, with the assistance of Canadian colleagues, C. glacialis and C. hyperboreus females from the deep lower St. Lawrence Estuary. They will conduct laboratory experiments in which hatching success, development and growth of Calanus nauplius stages are measured in controls of natural seawater and at a series of treatments in which CO2 concentrations, pH and temperature are rigorously controlled to represent possible future states of the northern ocean. The investigators will measure present surface and deep pCO2 and pH across the Gulf of Maine, including its deep basins, during a research cruise. The study will evaluate the hypothesis that predicted levels of CO2 increase in the northern ocean will impact population dynamics of the Calanus species. Using the results from the research cruise and a recently developed 1-D, Individual-Based life cycle model, the PI will explore in detail scenarios of impact of higher temperature and lower surface and deep pH on population dynamics of C. finmarchicus in the Gulf of Maine. The lipid-rich Calanus species are considered key intermediary links between primary production and higher trophic levels in North Atlantic and Arctic Ocean food webs. Impacts of higher surface temperature and lower pH on reproductive success may potentially lead to profound changes in energy transfer and structure of pelagic ecosystems in the northern oceans. In the Gulf of Maine, C. finmarchicus serves as primary prey for herring, sand lance, and mackerel, as well as the endangered northern right whale, warranting thorough evaluation of ocean acidification effects on its population dynamics. |
attribute | NC_GLOBAL | projects_0_end_date | String | 2013-10 |
attribute | NC_GLOBAL | projects_0_geolocation | String | Gulf of Maine |
attribute | NC_GLOBAL | projects_0_name | String | Ocean Acidification-Category 1- Impact of ocean acidification on survival of early life stages of planktonic copepods in the genus Calanus in the northern |
attribute | NC_GLOBAL | projects_0_project_nid | String | 2184 |
attribute | NC_GLOBAL | projects_0_start_date | String | 2010-11 |
attribute | NC_GLOBAL | publisher_name | String | Biological and Chemical Oceanographic Data Management Office (BCO-DMO) |
attribute | NC_GLOBAL | publisher_type | String | institution |
attribute | NC_GLOBAL | sourceUrl | String | (local files) |
attribute | NC_GLOBAL | standard_name_vocabulary | String | CF Standard Name Table v55 |
attribute | NC_GLOBAL | summary | String | This dataset presents the carbonate system and nutrients measurements during Calanus finmarchicus and Meganyctiphanes norvegica egg hatching success experiments, 2011-2012. Results are published in Preziosi et al (2017), Table 2. |
attribute | NC_GLOBAL | title | String | [Table 2 - Carbonate data and nutrients during egg experiments] - Table 2: Carbonate data and nutrients measured during Calanus finmarchicus and Meganyctiphanes norvegica egg hatching success experiments, 2011-2012 (Ocean Acidification-Category 1- Impact of ocean acidification on survival of early life stages of planktonic copepods in the genus Calanus in the northern) |
attribute | NC_GLOBAL | version | String | 1 |
attribute | NC_GLOBAL | xml_source | String | osprey2erddap.update_xml() v1.3 |
variable | EXPERIMENT | byte | ||
attribute | EXPERIMENT | _FillValue | byte | 127 |
attribute | EXPERIMENT | actual_range | byte | 1, 13 |
attribute | EXPERIMENT | bcodmo_name | String | exp_id |
attribute | EXPERIMENT | description | String | Number of the experiment |
attribute | EXPERIMENT | long_name | String | EXPERIMENT |
attribute | EXPERIMENT | units | String | unitless |
variable | SAMPLING_DATE | int | ||
attribute | SAMPLING_DATE | _FillValue | int | 2147483647 |
attribute | SAMPLING_DATE | actual_range | int | 110527, 120731 |
attribute | SAMPLING_DATE | bcodmo_name | String | date |
attribute | SAMPLING_DATE | description | String | Date of sampling formatted as yymmdd |
attribute | SAMPLING_DATE | long_name | String | SAMPLING DATE |
attribute | SAMPLING_DATE | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P01/current/ADATAA01/ |
attribute | SAMPLING_DATE | units | String | unitless |
variable | EVENT | byte | ||
attribute | EVENT | _FillValue | byte | 127 |
attribute | EVENT | actual_range | byte | 3, 24 |
attribute | EVENT | bcodmo_name | String | event |
attribute | EVENT | description | String | Number of the sampling event |
attribute | EVENT | long_name | String | EVENT |
attribute | EVENT | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P01/current/EVTAGFL/ |
attribute | EVENT | units | String | unitless |
variable | TIME_elapsed | float | ||
attribute | TIME_elapsed | _FillValue | float | NaN |
attribute | TIME_elapsed | actual_range | float | -7.4, 137.8 |
attribute | TIME_elapsed | bcodmo_name | String | time_elapsed |
attribute | TIME_elapsed | description | String | Time from internment of eggs |
attribute | TIME_elapsed | long_name | String | TIME Elapsed |
attribute | TIME_elapsed | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P01/current/ELTMZZZZ/ |
attribute | TIME_elapsed | units | String | hours |
variable | TANK | byte | ||
attribute | TANK | _FillValue | byte | 127 |
attribute | TANK | actual_range | byte | 1, 6 |
attribute | TANK | bcodmo_name | String | sample |
attribute | TANK | description | String | Number of the tank |
attribute | TANK | long_name | String | TANK |
attribute | TANK | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P02/current/ACYC/ |
attribute | TANK | units | String | unitless |
variable | TEMP | float | ||
attribute | TEMP | _FillValue | float | NaN |
attribute | TEMP | actual_range | float | -99.0, 15.4 |
attribute | TEMP | bcodmo_name | String | temperature |
attribute | TEMP | description | String | Tank temperature |
attribute | TEMP | long_name | String | Temperature |
attribute | TEMP | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P01/current/TEMPP901/ |
attribute | TEMP | units | String | degrees Celsius |
variable | SAL | float | ||
attribute | SAL | _FillValue | float | NaN |
attribute | SAL | actual_range | float | -99.0, 32.389 |
attribute | SAL | bcodmo_name | String | sal |
attribute | SAL | description | String | Salinity in the tank |
attribute | SAL | long_name | String | SAL |
attribute | SAL | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P01/current/PSALST01/ |
attribute | SAL | units | String | parts per thousand (ppt) |
variable | ALKALIN | float | ||
attribute | ALKALIN | _FillValue | float | NaN |
attribute | ALKALIN | actual_range | float | -99.0, 2227.6 |
attribute | ALKALIN | bcodmo_name | String | TALK |
attribute | ALKALIN | description | String | Total alkalinity in the tank |
attribute | ALKALIN | long_name | String | ALKALIN |
attribute | ALKALIN | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P01/current/MDMAP014/ |
attribute | ALKALIN | units | String | micromol/kilogram |
variable | TCO2 | float | ||
attribute | TCO2 | _FillValue | float | NaN |
attribute | TCO2 | actual_range | float | -99.0, 4763.5 |
attribute | TCO2 | bcodmo_name | String | TCO2 |
attribute | TCO2 | description | String | Total CO2 concentration in the tank |
attribute | TCO2 | long_name | String | TCO2 |
attribute | TCO2 | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P01/current/TCO2KG01/ |
attribute | TCO2 | units | String | micromol/kilogram |
variable | NO3_NO2 | float | ||
attribute | NO3_NO2 | _FillValue | float | NaN |
attribute | NO3_NO2 | actual_range | float | -99.0, 9.19 |
attribute | NO3_NO2 | bcodmo_name | String | NO3_NO2 |
attribute | NO3_NO2 | colorBarMaximum | double | 50.0 |
attribute | NO3_NO2 | colorBarMinimum | double | 0.0 |
attribute | NO3_NO2 | description | String | Tank's nitrate + nitrite concentration |
attribute | NO3_NO2 | long_name | String | Mole Concentration Of Nitrate In Sea Water |
attribute | NO3_NO2 | units | String | micromol/kilogram |
variable | NH4 | float | ||
attribute | NH4 | _FillValue | float | NaN |
attribute | NH4 | actual_range | float | -99.0, 2.59 |
attribute | NH4 | bcodmo_name | String | Ammonium |
attribute | NH4 | colorBarMaximum | double | 5.0 |
attribute | NH4 | colorBarMinimum | double | 0.0 |
attribute | NH4 | description | String | Tank's dissolved ammonium concentration |
attribute | NH4 | long_name | String | Mole Concentration Of Ammonium In Sea Water |
attribute | NH4 | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P01/current/AMONAAZX/ |
attribute | NH4 | units | String | micromol/kilogram |
variable | PO4 | float | ||
attribute | PO4 | _FillValue | float | NaN |
attribute | PO4 | actual_range | float | -99.0, 0.99 |
attribute | PO4 | bcodmo_name | String | PO4 |
attribute | PO4 | description | String | Tank's dissolved phosphate concentration |
attribute | PO4 | long_name | String | Mass Concentration Of Phosphate In Sea Water |
attribute | PO4 | units | String | micromol/kilogram |
variable | SI | float | ||
attribute | SI | _FillValue | float | NaN |
attribute | SI | actual_range | float | -99.0, 9.72 |
attribute | SI | bcodmo_name | String | SiOH_4 |
attribute | SI | description | String | Tank's dissolved silicate concentration |
attribute | SI | long_name | String | Mass Concentration Of Silicate In Sea Water |
attribute | SI | units | String | micromol/kilogram |
variable | PHTTL | float | ||
attribute | PHTTL | _FillValue | float | NaN |
attribute | PHTTL | actual_range | float | -99.0, 8.029 |
attribute | PHTTL | bcodmo_name | String | pH |
attribute | PHTTL | description | String | Total pH in the tank (calculated) |
attribute | PHTTL | long_name | String | PHTTL |
attribute | PHTTL | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P01/current/PHXXZZXX/ |
attribute | PHTTL | units | String | pH units |
variable | XCO2 | float | ||
attribute | XCO2 | _FillValue | float | NaN |
attribute | XCO2 | actual_range | float | -99.0, 50962.0 |
attribute | XCO2 | bcodmo_name | String | TCO2 |
attribute | XCO2 | description | String | CO2 gas concentration (calculated) |
attribute | XCO2 | long_name | String | XCO2 |
attribute | XCO2 | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P01/current/TCO2KG01/ |
attribute | XCO2 | units | String | parts per million (ppm) in dry gas |
variable | OMCA | float | ||
attribute | OMCA | _FillValue | float | NaN |
attribute | OMCA | actual_range | float | -99.0, 3.38 |
attribute | OMCA | bcodmo_name | String | Calcite Saturation State |
attribute | OMCA | description | String | Degree of saturation for calcite |
attribute | OMCA | long_name | String | OMCA |
attribute | OMCA | units | String | unitless |
variable | OMAR | float | ||
attribute | OMAR | _FillValue | float | NaN |
attribute | OMAR | actual_range | float | -99.0, 2.15 |
attribute | OMAR | bcodmo_name | String | OM_ar |
attribute | OMAR | description | String | Degree of saturation for aragonite |
attribute | OMAR | long_name | String | OMAR |
attribute | OMAR | units | String | unitless |
The information in the table above is also available in other file formats (.csv, .htmlTable, .itx, .json, .jsonlCSV1, .jsonlCSV, .jsonlKVP, .mat, .nc, .nccsv, .tsv, .xhtml) via a RESTful web service.