BCO-DMO ERDDAP
Accessing BCO-DMO data |
log in
Brought to you by BCO-DMO |
Row Type | Variable Name | Attribute Name | Data Type | Value |
---|---|---|---|---|
attribute | NC_GLOBAL | access_formats | String | .htmlTable,.csv,.json,.mat,.nc,.tsv,.esriCsv,.geoJson |
attribute | NC_GLOBAL | acquisition_description | String | Aerosol sample collection: Aerosols were collected on cellulose filters using\na Tisch Series 235 high-volume (~1 m3 air min-1) aerosol sampler equipped with\na cascade impactor designed for the separation of coarse (>1 \\u00b5m) and fine\n(<1 \\u00b5m) aerosol fractions. The sampler was mounted on a platform atop the\nship\\u2019s wheelhouse as far forward as possible. Relative wind speed and\ndirection were monitored during aerosol sample collection, and the sampler was\noperated only when the ship was steaming into the prevailing wind, in an\neffort to avoid contamination from the ship\\u2019s exhaust and superstructure.\nThe cascade impactor was loaded with Whatman 41 cellulose filters that had\nbeen pre-cleaned at Old Dominion University using 0.1 N and 0.5 N hydrochloric\nacid, following a procedure modified from Baker et al. [2006]. Six filters\n(five 25 cm x 25 cm slotted sheets and one 20.3 cm x 25.4 cm backing sheet)\nwere used for the collection of each aerosol sample. Air flow rates were\ncalculated using manufacturer-provided flow conversion tables and the pressure\ndecrease across the filters, which was measured at the start and end of sample\ncollection using a handheld digital manometer (Dwyer Series). The total air\nvolume sampled was estimated from the period of sample collection and the\naverage value of the initial and final flow rates.\n \nAerosol sample processing: Immediately following collection, the aerosol-laden\nfilters were unloaded and subsampled within a Class-100 clean air bench. Fixed\nportions of the aerosol-laden cellulose filters corresponding to each aerosol\nsize fraction (<1 \\u00b5m and >1 \\u00b5m) were transferred into 47 mm diameter\nperfluoroalkoxy alkane filter funnel assemblies (Savillex) loaded with acid-\ncleaned 0.4 \\u00b5m polycarbonate filter membranes, and leached with 750 ml of\n18.2 M\\u03a9-cm resistivity deionized water (Barnstead Nanopure), in a flow-\nthrough protocol modfied after Buck et al. [2006]. Aliquots of the leachate\nsolutions were immediately transferred into (i) acid-cleaned 125 ml low-\ndensity polyethylene bottles (Nalgene), then acidified with 500 \\u03bcl 6N\nultrapure hydrochloric acid (Fisher Chemical, Optima), for post-cruise\nanalysis of soluble aerosol iron, and (ii) 60 mL polypropylene tubes (Falcon)\nfor shipboard analysis of soluble aerosol nitrate+nitrite, phosphate and\nammonium. In addition, separate portions of the aerosol-laden cellulose\nfilters corresponding to each aerosol size fraction (<1 \\u00b5m and >1\n\\u00b5m) were stored in pre-cleaned ziploc polyethylene bags for microwave\nacid digestion at Old Dominion University. The microwave acid digestion\nprocedure was adapted from Morton et al. [2013], with the resulting digest\nsolutions evaporated to near dryness and then diluted with 20 mL of 1%\nultrapure nitric acid (Fisher Chemical, Optima).\n \nRainwater sample collection: Two methods were used to collect the rain samples\nat sea. Samples Rain-01 and Rain-02 were collected in two acid-cleaned 2 L\nwide-mouth fluorinated high-density polyethylene bottles (Nalgene) mounted\ninside a polyethylene bucket, using an N-Con Systems automated rain sampler.\nSamples Rain-03, Rain-04 and Rain-05 were manually collected using an acid-\ncleaned high-density polyethylene funnel (Nalgene) connected by a Teflon\ncollar to an acid-cleaned 2 L low-density polyethylene bottle (Nalgene). Both\nsample collectors were mounted on a platform atop the ship\\u2019s wheelhouse\nas far forward as possible, with samples collected whilst the ship was\nsteaming into the prevailing wind, in an effort to avoid contamination from\nthe ship\\u2019s exhaust and superstructure. The ODU Rain Composite combines\nsamples collected on the Old Dominion University campus during summer 2014\nusing the manual funnel sampling method.\n \nRainwater sample processing: Immediately following collection, rainwater\nsample containers were capped and transferred to a shipboard Class-100 clean\nair bench for processing. From each sample, aliquots were transferred into (i)\n60 mL polypropylene tubes (Falcon), which were frozen for post cruise analysis\nof nitrate+nitrite, phosphate and ammonium, and, when there was sufficient\nsample volume (ii) acid-cleaned 125 ml low-density polyethylene bottles\n(Nalgene) and acidified to pH 1.8 with 6N ultrapure hydrochloric acid (Fisher\nChemical, Optima) for post-cruise analysis of total iron (more strictly, total\nacid-labile iron). In addition, if the volume of sample was sufficient, the\nrainwater was filtered through an acid-cleaned 0.4 \\u00b5m polycarbonate\nmembrane using a 47 mm diameter perfluoroalkoxy alkane filter funnel assembly\n(Savillex), and the filtrate transferred into an acid-cleaned 125 ml low-\ndensity polyethylene bottles (Nalgene) and acidified to pH 1.8 with 6N\nultrapure hydrochloric acid (Fisher Chemical, Optima) for post-cruise analysis\nof dissolved iron.\n \nDFe and TFe: Dissolved iron and total iron was determined in aerosol leachate\nsolutions (DFe), aerosol digest solutions (TFe), filtered rainwater (DFe) and\nunfiltered rainwater (TFe, or more strictly, total acid-labile iron) were\ndetermined at Old Dominion University using a ThermoFisher Element2 high-\nresolution inductively-coupled plasma mass spectrometer (HR-ICP-MS). Sample\nsolutions were introduced into the ICP-MS without preconcentration, and\nquantified using matrix-matched external standard solutions prepared with SPEX\nCertiPrep Claritas PPT grade standards. An indium internal standard was used\nto correct for instrumental drift. Analytical limits of detection are\nestimated as 0.57 nM for DFe and for TFe in ulfiltered rainwater, and 53 nM\nfor TFe in the aerosol digest solutions. The values presented for DFe and TFe\nin samples represent concentrations after subtracting the concentrations of\nthe corresponding field blanks (Rain-Sampler-Blank, Rain-Funnel-Blank, or Aer-\nBlank). Atmospheric loadings of soluble aerosol iron (Sol Aer Fe) and total\naerosol iron (Tot Aer Fe) were calculated from DFe in aerosol leachates and\nTFe in aerosol digest solutions, respectively, and the total air volume\nsampled in each case, after correcting for the fraction of the active filter\narea that was leached (for DFe) or digested (for TFe).\n \nNO3+NO2: Dissolved nitrate plus nitrite was determined in aerosol leachate\nsolutions and rainwater with an Astoria Pacific nutrient autoanalyzer, using\nstandard colorimetric methods with an estimated detection limit of 0.14\n\\u00b5M (Parsons et al., 1984; Price and Harrison, 1987). Atmospheric loadings\nof soluble aerosol nitrate plus nitrite (Sol Aer NO3+NO2) were calculated from\nNO3+NO2 in aerosol leachates and the total air volume sampled, after\ncorrecting for the fraction of the active filter area that was leached.\n \nPO4: Dissolved phosphate was determined in aerosol leachate solutions and\nrainwater with an Astoria Pacific nutrient autoanalyzer, using standard\ncolorimetric methods with an estimated detection limit of 0.03 \\u00b5M\n(Parsons et al., 1984; Price and Harrison, 1987). Atmospheric loadings of\nsoluble aerosol phosphate (Sol Aer PO4) were calculated from PO4 in aerosol\nleachates and the total air volume sampled, after correcting for the fraction\nof the active filter area that was leached.\n \nNH4: Dissolved ammonium was determined in aerosol leachate solutions and\nrainwater using the manual orthophthaldialdehyde method (Holmes et al., 1999),\nwith an estimated detection limit of 10 nM. Atmospheric loadings of soluble\naerosol ammonium (Sol Aer NH4) were calculated from NH4 in aerosol leachates\nand the total air volume sampled, after correcting for the fraction of the\nactive filter area that was leached. |
attribute | NC_GLOBAL | awards_0_award_nid | String | 726327 |
attribute | NC_GLOBAL | awards_0_award_number | String | OCE-1260574 |
attribute | NC_GLOBAL | awards_0_data_url | String | http://www.nsf.gov/awardsearch/showAward.do?AwardNumber=1260574 |
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 | Henrietta N Edmonds |
attribute | NC_GLOBAL | awards_0_program_manager_nid | String | 51517 |
attribute | NC_GLOBAL | awards_1_award_nid | String | 726333 |
attribute | NC_GLOBAL | awards_1_award_number | String | OCE-1260454 |
attribute | NC_GLOBAL | awards_1_data_url | String | http://www.nsf.gov/awardsearch/showAward.do?AwardNumber=1260454 |
attribute | NC_GLOBAL | awards_1_funder_name | String | NSF Division of Ocean Sciences |
attribute | NC_GLOBAL | awards_1_funding_acronym | String | NSF OCE |
attribute | NC_GLOBAL | awards_1_funding_source_nid | String | 355 |
attribute | NC_GLOBAL | awards_1_program_manager | String | Henrietta N Edmonds |
attribute | NC_GLOBAL | awards_1_program_manager_nid | String | 51517 |
attribute | NC_GLOBAL | cdm_data_type | String | Other |
attribute | NC_GLOBAL | comment | String | Shipboard aerosol and rain sample nutrients and iron \n PI: Peter Sedwick \n data version 1: 2018-06-18 |
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 | 2018-06-18T15:59:42Z |
attribute | NC_GLOBAL | date_modified | String | 2019-08-16T14:51:57Z |
attribute | NC_GLOBAL | defaultDataQuery | String | &time<now |
attribute | NC_GLOBAL | doi | String | 10.1575/1912/bco-dmo.738744.1 |
attribute | NC_GLOBAL | Easternmost_Easting | double | -70.0543 |
attribute | NC_GLOBAL | geospatial_lat_max | double | 38.5334 |
attribute | NC_GLOBAL | geospatial_lat_min | double | 33.4453 |
attribute | NC_GLOBAL | geospatial_lat_units | String | degrees_north |
attribute | NC_GLOBAL | geospatial_lon_max | double | -70.0543 |
attribute | NC_GLOBAL | geospatial_lon_min | double | -74.3724 |
attribute | NC_GLOBAL | geospatial_lon_units | String | degrees_east |
attribute | NC_GLOBAL | infoUrl | String | https://www.bco-dmo.org/dataset/738744 |
attribute | NC_GLOBAL | institution | String | BCO-DMO |
attribute | NC_GLOBAL | instruments_0_acronym | String | ICP Mass Spec |
attribute | NC_GLOBAL | instruments_0_dataset_instrument_description | String | Iron analysis (DFe and TFe): ThermoFisher Element2 high-resolution inductively-coupled plasma mass spectrometer. |
attribute | NC_GLOBAL | instruments_0_dataset_instrument_nid | String | 738763 |
attribute | NC_GLOBAL | instruments_0_description | String | An ICP Mass Spec is an instrument that passes nebulized samples into an inductively-coupled gas plasma (8-10000 K) where they are atomized and ionized. Ions of specific mass-to-charge ratios are quantified in a quadrupole mass spectrometer. |
attribute | NC_GLOBAL | instruments_0_instrument_external_identifier | String | https://vocab.nerc.ac.uk/collection/L05/current/LAB15/ |
attribute | NC_GLOBAL | instruments_0_instrument_name | String | Inductively Coupled Plasma Mass Spectrometer |
attribute | NC_GLOBAL | instruments_0_instrument_nid | String | 530 |
attribute | NC_GLOBAL | instruments_0_supplied_name | String | ThermoFisher Element2 |
attribute | NC_GLOBAL | instruments_1_acronym | String | Nutrient Autoanalyzer |
attribute | NC_GLOBAL | instruments_1_dataset_instrument_description | String | Macronutrient analysis (NO3+NO2, PO4): Astoria Pacific nutrient autoanalyzer. |
attribute | NC_GLOBAL | instruments_1_dataset_instrument_nid | String | 738764 |
attribute | NC_GLOBAL | instruments_1_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_1_instrument_external_identifier | String | https://vocab.nerc.ac.uk/collection/L05/current/LAB04/ |
attribute | NC_GLOBAL | instruments_1_instrument_name | String | Nutrient Autoanalyzer |
attribute | NC_GLOBAL | instruments_1_instrument_nid | String | 558 |
attribute | NC_GLOBAL | instruments_1_supplied_name | String | Astoria Pacific nutrient autoanalyzer |
attribute | NC_GLOBAL | instruments_2_acronym | String | Aerosol_Sampler |
attribute | NC_GLOBAL | instruments_2_dataset_instrument_description | String | Tisch Series 235 high-volume aerosol sampler equipped with a cascade impactor. |
attribute | NC_GLOBAL | instruments_2_dataset_instrument_nid | String | 738761 |
attribute | NC_GLOBAL | instruments_2_description | String | A device that collects a sample of aerosol (dry particles or liquid droplets) from the atmosphere. |
attribute | NC_GLOBAL | instruments_2_instrument_external_identifier | String | https://vocab.nerc.ac.uk/collection/L05/current/13/ |
attribute | NC_GLOBAL | instruments_2_instrument_name | String | Aerosol Sampler |
attribute | NC_GLOBAL | instruments_2_instrument_nid | String | 691 |
attribute | NC_GLOBAL | instruments_2_supplied_name | String | Tisch Series 235 |
attribute | NC_GLOBAL | instruments_3_acronym | String | Precip_Sampler |
attribute | NC_GLOBAL | instruments_3_dataset_instrument_description | String | Rain Sampler: N-CON Systems ADS 00-120 sampler |
attribute | NC_GLOBAL | instruments_3_dataset_instrument_nid | String | 738762 |
attribute | NC_GLOBAL | instruments_3_description | String | A device that collects a sample of precipitation (rain, hail or snow) as it falls. |
attribute | NC_GLOBAL | instruments_3_instrument_external_identifier | String | https://vocab.nerc.ac.uk/collection/L05/current/14/ |
attribute | NC_GLOBAL | instruments_3_instrument_name | String | Precipitation Sampler |
attribute | NC_GLOBAL | instruments_3_instrument_nid | String | 693 |
attribute | NC_GLOBAL | instruments_3_supplied_name | String | ADS 00-120 |
attribute | NC_GLOBAL | instruments_4_acronym | String | Spectrophotometer |
attribute | NC_GLOBAL | instruments_4_dataset_instrument_description | String | Spectrofluorophotometer (NH4): Shimadzu RF1501. |
attribute | NC_GLOBAL | instruments_4_dataset_instrument_nid | String | 738765 |
attribute | NC_GLOBAL | instruments_4_description | String | 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. |
attribute | NC_GLOBAL | instruments_4_instrument_external_identifier | String | https://vocab.nerc.ac.uk/collection/L05/current/LAB20/ |
attribute | NC_GLOBAL | instruments_4_instrument_name | String | Spectrophotometer |
attribute | NC_GLOBAL | instruments_4_instrument_nid | String | 707 |
attribute | NC_GLOBAL | instruments_4_supplied_name | String | Shimadzu RF1501 |
attribute | NC_GLOBAL | keywords | String | aer, air, Air_Volume, ammonia, ammonium, bco, bco-dmo, biological, chemical, chemistry, comment, concentration, data, dataset, date, dfe, dmo, duration, earth, Earth Science > Oceans > Ocean Chemistry > Ammonia, Earth Science > Oceans > Ocean Chemistry > Nitrate, end, End_Lat, End_Long, erddap, long, management, mole, mole_concentration_of_ammonium_in_sea_water, mole_concentration_of_nitrate_in_sea_water, n02, nh4, nitrate, nitrite, no2, no3, NO3_NO2, ocean, oceanography, oceans, office, phosphate, po4, preliminary, sample, Sample_ID, science, sea, seawater, sol, Sol_Aer_Fe, Sol_Aer_NH4, Sol_Aer_NO3_NO2, Sol_Aer_PO4, start, Start_Lat, Start_Long, tfe, time, tot, Tot_Aer_Fe, volume, water |
attribute | NC_GLOBAL | keywords_vocabulary | String | GCMD Science Keywords |
attribute | NC_GLOBAL | license | String | https://www.bco-dmo.org/dataset/738744/license |
attribute | NC_GLOBAL | metadata_source | String | https://www.bco-dmo.org/api/dataset/738744 |
attribute | NC_GLOBAL | Northernmost_Northing | double | 38.5334 |
attribute | NC_GLOBAL | param_mapping | String | {'738744': {'Start_Long': 'flag - longitude', 'Start_Lat': 'flag - latitude'}} |
attribute | NC_GLOBAL | parameter_source | String | https://www.bco-dmo.org/mapserver/dataset/738744/parameters |
attribute | NC_GLOBAL | people_0_affiliation | String | Old Dominion University |
attribute | NC_GLOBAL | people_0_affiliation_acronym | String | ODU |
attribute | NC_GLOBAL | people_0_person_name | String | Peter N. Sedwick |
attribute | NC_GLOBAL | people_0_person_nid | String | 51056 |
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 | Old Dominion University |
attribute | NC_GLOBAL | people_1_affiliation_acronym | String | ODU |
attribute | NC_GLOBAL | people_1_person_name | String | Dr Margaret Mulholland |
attribute | NC_GLOBAL | people_1_person_nid | String | 51386 |
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 | Pennsylvania State University |
attribute | NC_GLOBAL | people_2_affiliation_acronym | String | PSU |
attribute | NC_GLOBAL | people_2_person_name | String | Dr Raymond Najjar |
attribute | NC_GLOBAL | people_2_person_nid | String | 50813 |
attribute | NC_GLOBAL | people_2_role | String | Co-Principal Investigator |
attribute | NC_GLOBAL | people_2_role_type | String | originator |
attribute | NC_GLOBAL | people_3_affiliation | String | Old Dominion University |
attribute | NC_GLOBAL | people_3_affiliation_acronym | String | ODU |
attribute | NC_GLOBAL | people_3_person_name | String | Peter N. Sedwick |
attribute | NC_GLOBAL | people_3_person_nid | String | 51056 |
attribute | NC_GLOBAL | people_3_role | String | Contact |
attribute | NC_GLOBAL | people_3_role_type | String | related |
attribute | NC_GLOBAL | people_4_affiliation | String | Woods Hole Oceanographic Institution |
attribute | NC_GLOBAL | people_4_affiliation_acronym | String | WHOI BCO-DMO |
attribute | NC_GLOBAL | people_4_person_name | String | Amber York |
attribute | NC_GLOBAL | people_4_person_nid | String | 643627 |
attribute | NC_GLOBAL | people_4_role | String | BCO-DMO Data Manager |
attribute | NC_GLOBAL | people_4_role_type | String | related |
attribute | NC_GLOBAL | project | String | DANCE |
attribute | NC_GLOBAL | projects_0_acronym | String | DANCE |
attribute | NC_GLOBAL | projects_0_description | String | NSF abstract:\nDeposition of atmospheric nitrogen provides reactive nitrogen species that influence primary production in nitrogen-limited regions. Although it is generally assumed that these species in precipitation contributes substantially to anthropogenic nitrogen loadings in many coastal marine systems, its biological impact remains poorly understood. Scientists from Pennsylvania State University, William & Mary College, and Old Dominion University will carry out a process-oriented field and modeling effort to test the hypothesis that deposits of wet atmospheric nitrogen (i.e., precipitation) stimulate primary productivity and accumulation of algal biomass in coastal waters following summer storms and this effect exceeds the associated biogeochemical responses to wind-induced mixing and increased stratification caused by surface freshening in oligotrophic coastal waters of the eastern United States. To attain their goal, the researchers would perform a Lagrangian field experiment during the summer months in coastal waters located between Delaware Bay and the coastal Carolinas to determine the response of surface-layer biogeochemistry and biology to precipitation events, which will be identified and intercepted using radar and satellite data. As regards the modeling effort, a 1-D upper ocean mixing model and a 1-D biogeochemical upper-ocean will be calibrated by assimilating the field data obtained a part of the study using the adjoint method. The hypothesis will be tested using sensitivity studies with the calibrated model combined with in-situ data and results from the incubation experiments. Lastly, to provide regional and historical context for the field measurements and the associated 1-D modeling, linked regional atmospheric-oceanic biogeochemical modeling will be conducted.\nBroader Impacts. Results from the study would be incorporated into class lectures for graduate courses on marine policy and marine biogeochemistry. One graduate student from Pennsylvania State University, one graduate student from the College of William and Mary, and one graduate and one undergraduate student from Old Dominion University would be supported and trained as part of this project. |
attribute | NC_GLOBAL | projects_0_end_date | String | 2017-02 |
attribute | NC_GLOBAL | projects_0_geolocation | String | Offshore Mid-Atlantic Bight and northern South-Atlantic Bight between latitudes 31.60°N and 38.89°N, and longitudes 71.09°W and 75.16°W |
attribute | NC_GLOBAL | projects_0_name | String | Collaborative Research: Impacts of atmospheric nitrogen deposition on the biogeochemistry of oligotrophic coastal waters |
attribute | NC_GLOBAL | projects_0_project_nid | String | 726328 |
attribute | NC_GLOBAL | projects_0_start_date | String | 2013-03 |
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 | Southernmost_Northing | double | 33.4453 |
attribute | NC_GLOBAL | standard_name_vocabulary | String | CF Standard Name Table v55 |
attribute | NC_GLOBAL | summary | String | Shipboard aerosol and rain samples were collected during R/V Hugh R. Sharp cruise HRS1414 offshore in the Mid-Atlantic Bight and northern South-Atlantic Bight from July to August of 2014. Samples were analyzed for nutrients and iron. |
attribute | NC_GLOBAL | title | String | [Shipboard aerosol and rain sample nutrients and iron] - Nutrients and iron in shipboard aerosol and rain samples collected during R/V Hugh R. Sharp cruise HRS1414 in the Mid-Atlantic Bight and northern South-Atlantic Bight from July to August of 2014 (DANCE project) (Collaborative Research: Impacts of atmospheric nitrogen deposition on the biogeochemistry of oligotrophic coastal waters) |
attribute | NC_GLOBAL | version | String | 1 |
attribute | NC_GLOBAL | Westernmost_Easting | double | -74.3724 |
attribute | NC_GLOBAL | xml_source | String | osprey2erddap.update_xml() v1.3 |
variable | Sample_ID | String | ||
attribute | Sample_ID | bcodmo_name | String | sample |
attribute | Sample_ID | description | String | unique identifier for each sample |
attribute | Sample_ID | long_name | String | Sample ID |
attribute | Sample_ID | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P02/current/ACYC/ |
attribute | Sample_ID | units | String | unitless |
variable | Comment | String | ||
attribute | Comment | bcodmo_name | String | comment |
attribute | Comment | description | String | sample comment |
attribute | Comment | long_name | String | Comment |
attribute | Comment | units | String | unitless |
variable | Date | String | ||
attribute | Date | bcodmo_name | String | date |
attribute | Date | description | String | local date (month/day/year) of collection |
attribute | Date | long_name | String | Date |
attribute | Date | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P01/current/ADATAA01/ |
attribute | Date | source_name | String | Date |
attribute | Date | time_precision | String | 1970-01-01 |
attribute | Date | units | String | unitless |
variable | Duration | short | ||
attribute | Duration | _FillValue | short | 32767 |
attribute | Duration | actual_range | short | 264, 600 |
attribute | Duration | bcodmo_name | String | time_elapsed |
attribute | Duration | description | String | duration of sample collection (aerosols) (NA: not applicable) |
attribute | Duration | long_name | String | Duration |
attribute | Duration | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P01/current/ELTMZZZZ/ |
attribute | Duration | units | String | minutes |
variable | latitude | double | ||
attribute | latitude | _CoordinateAxisType | String | Lat |
attribute | latitude | _FillValue | double | NaN |
attribute | latitude | actual_range | double | 33.4453, 38.5334 |
attribute | latitude | axis | String | Y |
attribute | latitude | bcodmo_name | String | latitude |
attribute | latitude | description | String | latitude at start of sample collection (NA: not applicable) |
attribute | latitude | ioos_category | String | Location |
attribute | latitude | long_name | String | Start Lat |
attribute | latitude | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P09/current/LATX/ |
attribute | latitude | standard_name | String | latitude |
attribute | latitude | units | String | degrees_north |
variable | End_Lat | float | ||
attribute | End_Lat | _FillValue | float | NaN |
attribute | End_Lat | actual_range | float | 33.4254, 38.4044 |
attribute | End_Lat | bcodmo_name | String | latitude |
attribute | End_Lat | description | String | latitude at end of sample collection (NA: not applicable) |
attribute | End_Lat | long_name | String | End Lat |
attribute | End_Lat | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P09/current/LATX/ |
attribute | End_Lat | units | String | decimal degrees |
variable | longitude | double | ||
attribute | longitude | _CoordinateAxisType | String | Lon |
attribute | longitude | _FillValue | double | NaN |
attribute | longitude | actual_range | double | -74.3724, -70.0543 |
attribute | longitude | axis | String | X |
attribute | longitude | bcodmo_name | String | longitude |
attribute | longitude | description | String | longitude at start of sample collection (NA: not applicable) |
attribute | longitude | ioos_category | String | Location |
attribute | longitude | long_name | String | Start Long |
attribute | longitude | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P09/current/LONX/ |
attribute | longitude | standard_name | String | longitude |
attribute | longitude | units | String | degrees_east |
variable | End_Long | float | ||
attribute | End_Long | _FillValue | float | NaN |
attribute | End_Long | actual_range | float | -74.2156, -71.495 |
attribute | End_Long | bcodmo_name | String | longitude |
attribute | End_Long | description | String | longitude at end of sample collection (NA: not applicable) |
attribute | End_Long | long_name | String | End Long |
attribute | End_Long | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P09/current/LONX/ |
attribute | End_Long | units | String | decimal degrees |
variable | Air_Volume | float | ||
attribute | Air_Volume | _FillValue | float | NaN |
attribute | Air_Volume | actual_range | float | 300.7, 684.9 |
attribute | Air_Volume | bcodmo_name | String | sample_volume |
attribute | Air_Volume | description | String | volume of air filtered (aerosols) (NA: not applicable) |
attribute | Air_Volume | long_name | String | Air Volume |
attribute | Air_Volume | units | String | meters cubed (m3) |
variable | DFe | String | ||
attribute | DFe | bcodmo_name | String | Fe |
attribute | DFe | description | String | dissolved iron concentration; (rainwater or aerosol leachate) (NA: not applicable; BDL: below detection limit) |
attribute | DFe | long_name | String | DFe |
attribute | DFe | units | String | nanomoles per liter (nmol/L) |
variable | Sol_Aer_Fe | String | ||
attribute | Sol_Aer_Fe | bcodmo_name | String | Fe |
attribute | Sol_Aer_Fe | description | String | soluble aerosol iron (atmospheric loading) (ND: not determined; BDL: below detection limit) |
attribute | Sol_Aer_Fe | long_name | String | Sol Aer Fe |
attribute | Sol_Aer_Fe | units | String | nanomoles per meter cubed (nmol/m3) |
variable | TFe | String | ||
attribute | TFe | bcodmo_name | String | Fe |
attribute | TFe | description | String | total iron concentration; (rainwater or aerosol) (ND: not determined; BDL: below detection limit) |
attribute | TFe | long_name | String | TFe |
attribute | TFe | units | String | nanomoles per liter (nmol/L) |
variable | Tot_Aer_Fe | String | ||
attribute | Tot_Aer_Fe | bcodmo_name | String | Fe |
attribute | Tot_Aer_Fe | description | String | total aerosol iron; (atmospheric loading) (NA: not applicable; BDL: below detection limit) |
attribute | Tot_Aer_Fe | long_name | String | Tot Aer Fe |
attribute | Tot_Aer_Fe | units | String | nanomoles per meter cubed (nmol/m3) |
variable | NO3_NO2 | String | ||
attribute | NO3_NO2 | bcodmo_name | String | NO3_NO2 |
attribute | NO3_NO2 | description | String | dissolved nitrate plus nitrite concentration (rainwater or aerosol leachate) (BDL: below detection limit) |
attribute | NO3_NO2 | long_name | String | NO3 NO2 |
attribute | NO3_NO2 | units | String | micromoles per liter (umol/L) |
variable | Sol_Aer_NO3_NO2 | float | ||
attribute | Sol_Aer_NO3_NO2 | _FillValue | float | NaN |
attribute | Sol_Aer_NO3_NO2 | actual_range | float | 1.5, 26.4 |
attribute | Sol_Aer_NO3_NO2 | bcodmo_name | String | NO3_NO2 |
attribute | Sol_Aer_NO3_NO2 | colorBarMaximum | double | 50.0 |
attribute | Sol_Aer_NO3_NO2 | colorBarMinimum | double | 0.0 |
attribute | Sol_Aer_NO3_NO2 | description | String | soluble aerosol nitrate plus nitrite (atmospheric loading) (NA: not applicable) |
attribute | Sol_Aer_NO3_NO2 | long_name | String | Mole Concentration Of Nitrate In Sea Water |
attribute | Sol_Aer_NO3_NO2 | units | String | nanomoles per meter cubed (nmol/m3) |
variable | PO4 | String | ||
attribute | PO4 | bcodmo_name | String | PO4 |
attribute | PO4 | description | String | dissolved phosphate (rainwater or aerosol leachate) (BDL: below detection limit) |
attribute | PO4 | long_name | String | PO4 |
attribute | PO4 | units | String | micromoles per liter (umol/L) |
variable | Sol_Aer_PO4 | String | ||
attribute | Sol_Aer_PO4 | bcodmo_name | String | PO4 |
attribute | Sol_Aer_PO4 | description | String | soluble aerosol phosphate (NA: not applicable; BDL: below detection limit) |
attribute | Sol_Aer_PO4 | long_name | String | Sol Aer PO4 |
attribute | Sol_Aer_PO4 | units | String | nanomoles per meter cubed (nmol/m3) |
variable | NH4 | float | ||
attribute | NH4 | _FillValue | float | NaN |
attribute | NH4 | actual_range | float | 0.01, 35.77 |
attribute | NH4 | bcodmo_name | String | Ammonium |
attribute | NH4 | colorBarMaximum | double | 5.0 |
attribute | NH4 | colorBarMinimum | double | 0.0 |
attribute | NH4 | description | String | dissolved ammonium (rainwater or aerosol leachate) |
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 | micromoles per liter (umol/L) |
variable | Sol_Aer_NH4 | float | ||
attribute | Sol_Aer_NH4 | _FillValue | float | NaN |
attribute | Sol_Aer_NH4 | actual_range | float | 1.9, 43.4 |
attribute | Sol_Aer_NH4 | bcodmo_name | String | Ammonium |
attribute | Sol_Aer_NH4 | colorBarMaximum | double | 5.0 |
attribute | Sol_Aer_NH4 | colorBarMinimum | double | 0.0 |
attribute | Sol_Aer_NH4 | description | String | soluble aerosol ammonium (NA: not applicable) |
attribute | Sol_Aer_NH4 | long_name | String | Mole Concentration Of Ammonium In Sea Water |
attribute | Sol_Aer_NH4 | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P01/current/AMONAAZX/ |
attribute | Sol_Aer_NH4 | units | String | nanomoles per meter cubed (nmol/m3) |