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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 | [Carbon Mineralization] - Barataria Bay carbon mineralization and biogeochemical properties from nine soil cores (Fate of Coastal Wetland Carbon Under Increasing Sea Level Rise: Using the Subsiding Louisiana Coast as a Proxy for Future World-Wide Sea Level Projections) | F I M | background | BCO-DMO | bcodmo_dataset_775547 |
Row Type | Variable Name | Attribute Name | Data Type | Value |
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attribute | NC_GLOBAL | access_formats | String | .htmlTable,.csv,.json,.mat,.nc,.tsv,.esriCsv,.geoJson |
attribute | NC_GLOBAL | acquisition_description | String | Moisture Content: Drying a subsample of soil using a gravimetric oven at 70 \u00b0C after 3 days or until a constant weight was achieved. Dried soils were ground using a SPEX Sample Prep 8000M Mixer/Mill (Metuchen, NJ). Bulk Density: Drying a subsample of soil using a gravimetric oven at 70 \u00b0C after 3 days or until a constant weight was achieved. Dried soils were ground using a SPEX Sample Prep 8000M Mixer/Mill (Metuchen, NJ). pH: Soil pH was determined by creating a 1:5 slurry of soil to distilled, deionized water, and sub- sequent measurement using an Accument bench top pH probe (Accumet XL200, ThermoFisher Scientific, Waltham, MA, USA). Total Carbon: Total Carbon content was determined by use of a Vario Micro Cube CHNS Analyzer on dried, ground subsamples. Total Nitrogen: Total Nitrogen content was determined by use of a Vario Micro Cube CHNS Analyzer on dried, ground subsamples. Total Phosphorus: Dried, ground sub- samples were used to determine percent organic matter using the loss- on-ignition method, where soils were burned at 550\u00b0C in a muffle furnace for a total of 3 h, then soils were digested with 50 mL of 1 N HCl at 100 \u00b0C for 30 min, and filtered through Whatman #41 filter paper for total P analysis (Andersen, 1976). Total P content was then determined colorimetrically via an AQ2 Automated Discrete Analyzer (Seal Analytical, Mequon, WI) in accordance with EPA method 365.1 Rev. 2. Organic Matter Content: Dried, ground sub- samples were used to determine percent organic matter using the loss- on-ignition method, where soils were burned at 550\u00b0C in a muffle furnace for a total of 3 h. Extractable Dissolved Organic Carbon: 1 g dry weight of field-moist soil were weighed into 40 mL centrifuge tubes and extracted with 25 mL of 0.5 M K2SO4, placed in an orbital shaker for 1 h at 25 \u00b0C and 150 rpm then immediately centrifuged for 10 min at 10 \u00b0C and 5000 rpm. The supernatant was vacuum filtered through Supor 0.45 \u03bcM filters, acidified with double distilled H2SO4 for preservation, and stored at 4 \u00b0C until analysis. Dissolved organic carbon (DOC) was determined by use of a Shimadzu TOC-L Analyzer (Kyoto, Japan). Extractable Nitrate: 2.5 g of wet soil (both from the field and from the bottle incubation) into 40 mL centrifuge tubes and adding 25 mL of 2 M KCl. Samples were then shaken continuously on an orbital shaker for 1 h at 25 \u00b0C and 150 rpm, then centrifuged for 10 min at 10 \u00b0C and 5000 rpm. Following the centrifuge, samples were immediately filtered through Supor 0.45 \u03bcM filters and acidified with double distilled H2SO4 to a pH of < 2 for preservation. Extractable nutrients samples were then analyzed using an AQ2 Automated Discrete Analyzer (Seal Analytical, Mequon, WI, EPA methods 231-A Rev.0, 210-A Rev.1, and 204-A Rev.0). Extractable Ammonium: 2.5 g of wet soil (both from the field and from the bottle incubation) into 40 mL centrifuge tubes and adding 25 mL of 2 M KCl. Samples were then shaken continuously on an orbital shaker for 1 h at 25 \u00b0C and 150 rpm, then centrifuged for 10 min at 10 \u00b0C and 5000 rpm. Following the centrifuge, samples were immediately filtered through Supor 0.45 \u03bcM filters and acidified with double distilled H2SO4 to a pH of < 2 for preservation. Extractable nutrients samples were then analyzed using an AQ2 Automated Discrete Analyzer (Seal Analytical, Mequon, WI, EPA methods 231-A Rev.0, 210-A Rev.1, and 204-A Rev.0). Extractable Soluble Reactive Phosphorus: 2.5 g of wet soil (both from the field and from the bottle incubation) into 40 mL centrifuge tubes and adding 25 mL of 2 M KCl. Samples were then shaken continuously on an orbital shaker for 1 h at 25 \u00b0C and 150 rpm, then centrifuged for 10 min at 10 \u00b0C and 5000 rpm. Following the centrifuge, samples were immediately filtered through Supor 0.45 \u03bcM filters and acidified with double distilled H2SO4 to a pH of < 2 for preservation. Extractable nutrients samples were then analyzed using an AQ2 Automated Discrete Analyzer (Seal Analytical, Mequon, WI, EPA methods 231-A Rev.0, 210-A Rev.1, and 204-A Rev.0). Microbial Biomass Carbon: Microbial biomass C (MBC) was determined on soils both immediately after the field sampling and soils from the bottles after the incubation period following the method outlined in Vance et al. (1987). Duplicates of approximately 1 g dry weight of field-moist soil were weighed into 40 mL centrifuge tubes and assigned to either a fumigate or non-fumigate treatment. The fumigated samples were exposed to gaseous chloroform for 24 h in a glass desiccator. After 24 h, the sam- ples were extracted with 25 mL of 0.5 M K2SO4, placed in an orbital shaker for 1 h at 25 \u00b0C and 150 rpm. After incubation, samples were immediately centrifuged for 10 min at 10 \u00b0C and 5000 rpm. The supernatant was vacuum filtered through Supor 0.45 \u03bcM filters, acidified with double distilled H2SO4 for preservation, and stored at 4 \u00b0C until analysis. Non-fumigate samples were processed in the same manner, excluding the chloroform fumigation. Dissolved organic carbon (DOC) was determined by use of a Shimadzu TOC-L Analyzer (Kyoto, Japan). Microbial biomass C was calculated as the difference between the fumigated samples and the non-fumigated samples. B-glucosidase activity: Assays were conducted using fluorescent substrate 4\u2010 methylumbelliferone (MUF) for standardization and fluorescently labeled MUF- specific sub- strates (German et al., 2011). To create a 1:100 slurry, 0.5 g of soil was added to 39 mL of autoclaved distilled deionized water and shaken continuously on an orbital shaker for 1 h at 25 \u00b0C and 150 rpm. Fluor- escence was measured at excitation/emission wavelengths 360/460 on a BioTek Synergy HTX (BioTek Instruments, Inc., Winooski, VT, USA) both immediately after substrate and sample were added, and 24 h later to determine a rate of enzyme activity. N\u2010acetyl\u2010beta\u2010D\u2010glucosaminidase activity: Assays were conducted using fluorescent substrate 4\u2010 methylumbelliferone (MUF) for standardization and fluorescently labeled MUF- specific sub- strates (German et al., 2011). To create a 1:100 slurry, 0.5 g of soil was added to 39 mL of autoclaved distilled deionized water and shaken continuously on an orbital shaker for 1 h at 25 \u00b0C and 150 rpm. Fluor- escence was measured at excitation/emission wavelengths 360/460 on a BioTek Synergy HTX (BioTek Instruments, Inc., Winooski, VT, USA) both immediately after substrate and sample were added, and 24 h later to determine a rate of enzyme activity. Alkaline phosphatase activity: Assays were conducted using fluorescent substrate 4\u2010 methylumbelliferone (MUF) for standardization and fluorescently labeled MUF- specific sub- strates (German et al., 2011). To create a 1:100 slurry, 0.5 g of soil was added to 39 mL of autoclaved distilled deionized water and shaken continuously on an orbital shaker for 1 h at 25 \u00b0C and 150 rpm. Fluor- escence was measured at excitation/emission wavelengths 360/460 on a BioTek Synergy HTX (BioTek Instruments, Inc., Winooski, VT, USA) both immediately after substrate and sample were added, and 24 h later to determine a rate of enzyme activity. Xylosidase activity: Assays were conducted using fluorescent substrate 4\u2010 methylumbelliferone (MUF) for standardization and fluorescently labeled MUF- specific sub- strates (German et al., 2011). To create a 1:100 slurry, 0.5 g of soil was added to 39 mL of autoclaved distilled deionized water and shaken continuously on an orbital shaker for 1 h at 25 \u00b0C and 150 rpm. Fluor- escence was measured at excitation/emission wavelengths 360/460 on a BioTek Synergy HTX (BioTek Instruments, Inc., Winooski, VT, USA) both immediately after substrate and sample were added, and 24 h later to determine a rate of enzyme activity. Cellobiosidase activity: Assays were conducted using fluorescent substrate 4\u2010 methylumbelliferone (MUF) for standardization and fluorescently labeled MUF- specific sub- strates (German et al., 2011). To create a 1:100 slurry, 0.5 g of soil was added to 39 mL of autoclaved distilled deionized water and shaken continuously on an orbital shaker for 1 h at 25 \u00b0C and 150 rpm. Fluor- escence was measured at excitation/emission wavelengths 360/460 on a BioTek Synergy HTX (BioTek Instruments, Inc., Winooski, VT, USA) both immediately after substrate and sample were added, and 24 h later to determine a rate of enzyme activity. Rate of carbon dioxide production (potential): Duplicate subsamples (approximately 7 g) from each depth segment of each core were weighed into 100 mL glass serum bottles, capped with a rubber septa and aluminum crimp and evacuated to \u221275 mm Hg. Replicate bottles were randomly assigned to one of two treatments: anaerobic (purged with 99% O2-free N2 gas for 3 min), or aerobic (purged with Breathing Grade air containing 21% O2 for 3 min). Anaerobic bottles were injected with 14 mL of filtered, N2-purged site water, while aerobic bottles were injected with 14 mL of filtered, breathing air-purged site water. Bottles were then placed on an orbital shaker at 150 rpm and 25 \u00b0C. Headspace samples were taken at 1, 2, 4, 7, 10, and 14 day time points, and injected into a GC-2014 gas chromatograph (Shimadzu Instrument, Kyoto, Japan) equipped with a flame ionization detector. Respiration rates were calculated as the change in CO2 production over time. After each gas sample was extracted from the bottles' headspace, the bottle was purged with either 99% O2- free N2 gas or Breathing Grade air for 3 min, depending on treatment. Rate of nitrate mineralization (potential): Following the 14 day incubation, bottles were uncapped, and the remaining soil sample was placed in a 20 mL HDPE scintillation vials Rate of ammonium mineralization (potential): for analysis of extractable ammonium (NH4+), nitrate (NO3\u2212), and soluble reactive phosphorus (SRP), microbial biomass C, and enzyme analysis. |
attribute | NC_GLOBAL | awards_0_award_nid | String | 670519 |
attribute | NC_GLOBAL | awards_0_award_number | String | OCE-1635837 |
attribute | NC_GLOBAL | awards_0_data_url | String | http://www.nsf.gov/awardsearch/showAward.do?AwardNumber=1635837 |
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 | William Miller |
attribute | NC_GLOBAL | awards_0_program_manager_nid | String | 670518 |
attribute | NC_GLOBAL | cdm_data_type | String | Other |
attribute | NC_GLOBAL | comment | String | Barataria Bay Carbon Mineralization PI: Dr. Lisa Chambers Version: 2019-08-16 |
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 | 2019-08-16T13:50:36Z |
attribute | NC_GLOBAL | date_modified | String | 2019-09-05T17:09:11Z |
attribute | NC_GLOBAL | defaultDataQuery | String | &time<now |
attribute | NC_GLOBAL | doi | String | 10.1575/1912/bco-dmo.775547.1 |
attribute | NC_GLOBAL | Easternmost_Easting | double | -89.8998 |
attribute | NC_GLOBAL | geospatial_lat_max | double | 29.4436 |
attribute | NC_GLOBAL | geospatial_lat_min | double | 29.4414 |
attribute | NC_GLOBAL | geospatial_lat_units | String | degrees_north |
attribute | NC_GLOBAL | geospatial_lon_max | double | -89.8998 |
attribute | NC_GLOBAL | geospatial_lon_min | double | -89.9026 |
attribute | NC_GLOBAL | geospatial_lon_units | String | degrees_east |
attribute | NC_GLOBAL | infoUrl | String | https://www.bco-dmo.org/dataset/775547 |
attribute | NC_GLOBAL | institution | String | BCO-DMO |
attribute | NC_GLOBAL | instruments_0_acronym | String | CHN_EA |
attribute | NC_GLOBAL | instruments_0_dataset_instrument_description | String | Total Carbon content was determined by use of a Vario Micro Cube CHNS Analyzer on dried, ground subsamples. Total Nitrogen content was determined by use of a Vario Micro Cube CHNS Analyzer on dried, ground subsamples. |
attribute | NC_GLOBAL | instruments_0_dataset_instrument_nid | String | 775607 |
attribute | NC_GLOBAL | instruments_0_description | String | A CHN Elemental Analyzer is used for the determination of carbon, hydrogen, and nitrogen content in organic and other types of materials, including solids, liquids, volatile, and viscous samples. |
attribute | NC_GLOBAL | instruments_0_instrument_name | String | CHN Elemental Analyzer |
attribute | NC_GLOBAL | instruments_0_instrument_nid | String | 625 |
attribute | NC_GLOBAL | instruments_0_supplied_name | String | Vario Micro Cube CHNS Analyzer |
attribute | NC_GLOBAL | instruments_1_acronym | String | Gas Chromatograph |
attribute | NC_GLOBAL | instruments_1_dataset_instrument_description | String | Headspace samples were taken at 1, 2, 4, 7, 10, and 14 day time points, and injected into a GC-2014 gas chromatograph (Shimadzu Instrument, Kyoto, Japan) equipped with a flame ionization detector. |
attribute | NC_GLOBAL | instruments_1_dataset_instrument_nid | String | 775610 |
attribute | NC_GLOBAL | instruments_1_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_1_instrument_external_identifier | String | https://vocab.nerc.ac.uk/collection/L05/current/LAB02/ |
attribute | NC_GLOBAL | instruments_1_instrument_name | String | Gas Chromatograph |
attribute | NC_GLOBAL | instruments_1_instrument_nid | String | 661 |
attribute | NC_GLOBAL | instruments_1_supplied_name | String | GC-2014 gas chromatograph |
attribute | NC_GLOBAL | instruments_2_acronym | String | Benchtop pH Meter |
attribute | NC_GLOBAL | instruments_2_dataset_instrument_description | String | Soil pH was determined by creating a 1:5 slurry of soil to distilled, deionized water, and sub- sequent measurement using an Accument bench top pH probe (Accumet XL200, ThermoFisher Scientific, Waltham, MA, USA). |
attribute | NC_GLOBAL | instruments_2_dataset_instrument_nid | String | 775606 |
attribute | NC_GLOBAL | instruments_2_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_2_instrument_name | String | Benchtop pH Meter |
attribute | NC_GLOBAL | instruments_2_instrument_nid | String | 681 |
attribute | NC_GLOBAL | instruments_2_supplied_name | String | Accument bench top pH probe |
attribute | NC_GLOBAL | instruments_3_acronym | String | Shimadzu TOC-L |
attribute | NC_GLOBAL | instruments_3_dataset_instrument_description | String | Dissolved organic carbon (DOC) was determined by use of a Shimadzu TOC-L Analyzer (Kyoto, Japan). |
attribute | NC_GLOBAL | instruments_3_dataset_instrument_nid | String | 775609 |
attribute | NC_GLOBAL | instruments_3_description | String | A Shimadzu TOC-L Analyzer measures DOC by high temperature combustion method. Developed by Shimadzu, the 680 degree C combustion catalytic oxidation method is now used worldwide. One of its most important features is the capacity to efficiently oxidize hard-to-decompose organic compounds, including insoluble and macromolecular organic compounds. The 680 degree C combustion catalytic oxidation method has been adopted for the TOC-L series. http://www.shimadzu.com/an/toc/lab/toc-l2.html |
attribute | NC_GLOBAL | instruments_3_instrument_external_identifier | String | http://onto.nerc.ac.uk/CAST/124.html |
attribute | NC_GLOBAL | instruments_3_instrument_name | String | Shimadzu TOC-L Analyzer |
attribute | NC_GLOBAL | instruments_3_instrument_nid | String | 527277 |
attribute | NC_GLOBAL | instruments_3_supplied_name | String | Shimadzu TOC-L Analyzer |
attribute | NC_GLOBAL | instruments_4_acronym | String | Discrete Analyzer |
attribute | NC_GLOBAL | instruments_4_dataset_instrument_description | String | Total P content was determined colorimetrically via an AQ2 Automated Discrete Analyzer (Seal Analytical, Mequon, WI) in accordance with EPA method 365.1 Rev. 2. Extractable nutrients samples were analyzed using an AQ2 Automated Discrete Analyzer (Seal Analytical, Mequon, WI, EPA methods 231-A Rev.0, 210-A Rev.1, and 204-A Rev.0). |
attribute | NC_GLOBAL | instruments_4_dataset_instrument_nid | String | 775608 |
attribute | NC_GLOBAL | instruments_4_description | String | Discrete analyzers utilize discrete reaction wells to mix and develop the colorimetric reaction, allowing for a wide variety of assays to be performed from one sample. These instruments are ideal for drinking water, wastewater, soil testing, environmental and university or research applications where multiple assays and high throughput are required. |
attribute | NC_GLOBAL | instruments_4_instrument_name | String | Discrete Analyzer |
attribute | NC_GLOBAL | instruments_4_instrument_nid | String | 654337 |
attribute | NC_GLOBAL | instruments_4_supplied_name | String | AQ2 Automated Discrete Analyzer |
attribute | NC_GLOBAL | keywords | String | aerob, ammonia, ammonium, anaerob, ap_aerob, ap_anaerob, ap_field, bco, bco-dmo, bg_aerob, bg_anaerob, bg_field, biological, biomass, bulk, bulk_density_g_cm_3_field, carbon, carbon_dioxide_rate_aerob, carbon_dioxide_rate_anaerob, cb_aerob, cb_anaerob, cb_field, chemical, chemistry, commerce, concentration, content, data, dataset, density, department, depth, depth2, dioxide, dmo, doc, earth, Earth Science > Oceans > Ocean Chemistry > Ammonia, Earth Science > Oceans > Ocean Chemistry > Nitrate, erddap, extractable, extractable_ammonium_aerob, extractable_ammonium_anaerob, extractable_ammonium_field, extractable_doc_field, extractable_nitrate_aerob, extractable_nitrate_anaerob, extractable_nitrate_field, extractable_srp_aerob, extractable_srp_anaerob, extractable_srp_field, field, latitude, longitude, management, matter, microbial, microbial_biomass_c_field, microbial_biomass_carbon_aerob, microbial_biomass_carbon_anaerob, moisture, moisture_content_pcnt_field, mole, mole_concentration_of_ammonium_in_sea_water, mole_concentration_of_nitrate_in_sea_water, n02, nag, nag_aerob, nag_anaerob, nag_field, nh4, nitrate, no3, ocean, oceanography, oceans, office, organic, pcnt, pcnt_organic_matter_field, ph_field, potentially_mineralizable_ammonium_aerob, potentially_mineralizable_ammonium_anaerob, potentially_mineralizable_nitrate_aerob, potentially_mineralizable_nitrate_anaerob, preliminary, rate, replicate, science, sea, seawater, site, site_id, srp, total, total_c_g_cm_3_field, total_c_g_kg_field, total_n_g_cm_3_field, total_n_g_kg_field, total_p_mg_kg_field, water, xy_aerob, xy_anaerob, xy_field |
attribute | NC_GLOBAL | keywords_vocabulary | String | GCMD Science Keywords |
attribute | NC_GLOBAL | license | String | https://www.bco-dmo.org/dataset/775547/license |
attribute | NC_GLOBAL | metadata_source | String | https://www.bco-dmo.org/api/dataset/775547 |
attribute | NC_GLOBAL | Northernmost_Northing | double | 29.4436 |
attribute | NC_GLOBAL | param_mapping | String | {'775547': {'lat': 'flag - latitude', 'lon': 'flag - longitude'}} |
attribute | NC_GLOBAL | parameter_source | String | https://www.bco-dmo.org/mapserver/dataset/775547/parameters |
attribute | NC_GLOBAL | people_0_affiliation | String | University of Central Florida |
attribute | NC_GLOBAL | people_0_affiliation_acronym | String | UCF |
attribute | NC_GLOBAL | people_0_person_name | String | Dr Lisa G Chambers |
attribute | NC_GLOBAL | people_0_person_nid | String | 670523 |
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 | Louisiana State University |
attribute | NC_GLOBAL | people_1_affiliation_acronym | String | LSU |
attribute | NC_GLOBAL | people_1_person_name | String | Dr Robert L. Cook |
attribute | NC_GLOBAL | people_1_person_nid | String | 670531 |
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 | Louisiana State University |
attribute | NC_GLOBAL | people_2_affiliation_acronym | String | LSU |
attribute | NC_GLOBAL | people_2_person_name | String | Dr John R. White |
attribute | NC_GLOBAL | people_2_person_nid | String | 670528 |
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 | Louisiana State University |
attribute | NC_GLOBAL | people_3_affiliation_acronym | String | LSU |
attribute | NC_GLOBAL | people_3_person_name | String | Dr Zuo Xue |
attribute | NC_GLOBAL | people_3_person_nid | String | 670533 |
attribute | NC_GLOBAL | people_3_role | String | Co-Principal Investigator |
attribute | NC_GLOBAL | people_3_role_type | String | originator |
attribute | NC_GLOBAL | people_4_affiliation | String | University of Central Florida |
attribute | NC_GLOBAL | people_4_affiliation_acronym | String | UCF |
attribute | NC_GLOBAL | people_4_person_name | String | Kyle Dittmer |
attribute | NC_GLOBAL | people_4_person_nid | String | 776252 |
attribute | NC_GLOBAL | people_4_role | String | Student |
attribute | NC_GLOBAL | people_4_role_type | String | related |
attribute | NC_GLOBAL | people_5_affiliation | String | University of Central Florida |
attribute | NC_GLOBAL | people_5_affiliation_acronym | String | UCF |
attribute | NC_GLOBAL | people_5_person_name | String | Havalend E Steinmuller |
attribute | NC_GLOBAL | people_5_person_nid | String | 776250 |
attribute | NC_GLOBAL | people_5_role | String | Student |
attribute | NC_GLOBAL | people_5_role_type | String | related |
attribute | NC_GLOBAL | people_6_affiliation | String | Woods Hole Oceanographic Institution |
attribute | NC_GLOBAL | people_6_affiliation_acronym | String | WHOI BCO-DMO |
attribute | NC_GLOBAL | people_6_person_name | String | Mathew Biddle |
attribute | NC_GLOBAL | people_6_person_nid | String | 708682 |
attribute | NC_GLOBAL | people_6_role | String | BCO-DMO Data Manager |
attribute | NC_GLOBAL | people_6_role_type | String | related |
attribute | NC_GLOBAL | project | String | Submerged Wetland Carbon |
attribute | NC_GLOBAL | projects_0_acronym | String | Submerged Wetland Carbon |
attribute | NC_GLOBAL | projects_0_description | String | Description from NSF award abstract: Coastal Louisiana is currently experiencing net sea level rise at rates higher than most of the world's coastlines and within the global range predicted to occur in the next 65 - 85 years, making Louisiana an ideal site to study potential future impacts of rising sea level on coastal systems. This project will use field collection and controlled tank experiments to study the changing organic carbon cycle resulting from erosion of marsh soils along with its impact on associated biogeochemical processes. The hypothesis tested in this study is that the majority of eroded soil organic carbon is converted to carbon dioxide (CO2) and released to the atmosphere, representing an addition to the anthropogenic input of CO2. This process has not been quantified and could be an important missing component in predictive models of atmospheric CO2 changes. While this process may be of only regional importance today in comparison to other sources of CO2, this study of the Louisiana coast will greatly enhance our full understanding of the potential impacts on the global carbon cycle that may result from coastal erosion as global sea level continues to rise. The project will train graduate and undergraduate students in interdisciplinary research involving marine and wetland biogeochemistry, microbiology, and ecological modeling. It will also fund development of an interactive, educational display on the loss of coastal wetlands for the Louisiana Sea Grant's annual Ocean Commotion educational event attended by area middle and high school students, teachers, and parents. Results from this study may also inform community planners both regionally and worldwide as they prepare for sea level rise in coastal communities. Eustatic sea level rise and regional subsidence have created a much greater rate of coastline loss in Louisiana than is being experienced in most of the world's coastal regions, reaching global rates that are predicted to occur worldwide in 65 - 85 years. This provides a unique potential to extrapolate data from Louisiana's changing coastal carbon cycle to both regional and global models of the future impact of sea level rise and coastal erosion. By quantifying and modeling the importance of CO2 emissions resulting directly from mineralized soil organic matter from eroding coastlines, a missing element can be added to climate change models. The PIs here plan to investigate the fate of the coastal wetland carbon pool as it erodes using field sampling, laboratory analysis, mesocosm manipulations, and the creation of a coupled physical-biogeochemical model for the basin being studied. Beyond quantifying increased CO2 emission, the PIs will also address the potential for increased eutrophication due to input of nutrients from eroded soils, as well as the potential for future contribution to existing hypoxic zones in the northern Gulf of Mexico that result from excessive nutrient input from the Mississippi River watershed. |
attribute | NC_GLOBAL | projects_0_end_date | String | 2019-08 |
attribute | NC_GLOBAL | projects_0_geolocation | String | Coastal Lousiana |
attribute | NC_GLOBAL | projects_0_name | String | Fate of Coastal Wetland Carbon Under Increasing Sea Level Rise: Using the Subsiding Louisiana Coast as a Proxy for Future World-Wide Sea Level Projections |
attribute | NC_GLOBAL | projects_0_project_nid | String | 670520 |
attribute | NC_GLOBAL | projects_0_start_date | String | 2016-09 |
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 | 29.4414 |
attribute | NC_GLOBAL | standard_name_vocabulary | String | CF Standard Name Table v55 |
attribute | NC_GLOBAL | summary | String | Nine soil cores (1 m deep) were collected from three sites within Barataria Bay, LA (USA). Both the biogeochemical properties of the soils with depth were determined, as well as the impacts of the introduction of oxygenated seawater on carbon mineralization rates. |
attribute | NC_GLOBAL | title | String | [Carbon Mineralization] - Barataria Bay carbon mineralization and biogeochemical properties from nine soil cores (Fate of Coastal Wetland Carbon Under Increasing Sea Level Rise: Using the Subsiding Louisiana Coast as a Proxy for Future World-Wide Sea Level Projections) |
attribute | NC_GLOBAL | version | String | 1 |
attribute | NC_GLOBAL | Westernmost_Easting | double | -89.9026 |
attribute | NC_GLOBAL | xml_source | String | osprey2erddap.update_xml() v1.3 |
variable | site_id | byte | ||
attribute | site_id | _FillValue | byte | 127 |
attribute | site_id | actual_range | byte | 1, 3 |
attribute | site_id | bcodmo_name | String | site |
attribute | site_id | description | String | site identifier |
attribute | site_id | long_name | String | Site Id |
attribute | site_id | units | String | unitless |
variable | replicate | byte | ||
attribute | replicate | _FillValue | byte | 127 |
attribute | replicate | actual_range | byte | 1, 3 |
attribute | replicate | bcodmo_name | String | replicate |
attribute | replicate | description | String | replicate identifier |
attribute | replicate | long_name | String | Replicate |
attribute | replicate | units | String | unitless |
variable | latitude | double | ||
attribute | latitude | _CoordinateAxisType | String | Lat |
attribute | latitude | _FillValue | double | NaN |
attribute | latitude | actual_range | double | 29.4414, 29.4436 |
attribute | latitude | axis | String | Y |
attribute | latitude | bcodmo_name | String | latitude |
attribute | latitude | colorBarMaximum | double | 90.0 |
attribute | latitude | colorBarMinimum | double | -90.0 |
attribute | latitude | description | String | Latitude of observations with positive values indicating North |
attribute | latitude | ioos_category | String | Location |
attribute | latitude | long_name | String | Latitude |
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 | longitude | double | ||
attribute | longitude | _CoordinateAxisType | String | Lon |
attribute | longitude | _FillValue | double | NaN |
attribute | longitude | actual_range | double | -89.9026, -89.8998 |
attribute | longitude | axis | String | X |
attribute | longitude | bcodmo_name | String | longitude |
attribute | longitude | colorBarMaximum | double | 180.0 |
attribute | longitude | colorBarMinimum | double | -180.0 |
attribute | longitude | description | String | Longitude of observations with negative values indicating West |
attribute | longitude | ioos_category | String | Location |
attribute | longitude | long_name | String | Longitude |
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 | depth2 | String | ||
attribute | depth2 | bcodmo_name | String | depth_core |
attribute | depth2 | description | String | depth in core |
attribute | depth2 | long_name | String | Depth |
attribute | depth2 | standard_name | String | depth |
attribute | depth2 | units | String | centimeters (cm) |
variable | nag_aerob | float | ||
attribute | nag_aerob | _FillValue | float | NaN |
attribute | nag_aerob | actual_range | float | 0.0, 110.557 |
attribute | nag_aerob | bcodmo_name | String | unknown |
attribute | nag_aerob | description | String | N‐acetyl‐beta‐D‐glucosaminidase activity under aerobic conditions |
attribute | nag_aerob | long_name | String | Nag Aerob |
attribute | nag_aerob | units | String | nmol MUF g−1 min−1 |
variable | ap_aerob | float | ||
attribute | ap_aerob | _FillValue | float | NaN |
attribute | ap_aerob | actual_range | float | 1.07522, 91.7377 |
attribute | ap_aerob | bcodmo_name | String | unknown |
attribute | ap_aerob | description | String | Alkaline phosphatase activity under aerobic conditions |
attribute | ap_aerob | long_name | String | Ap Aerob |
attribute | ap_aerob | units | String | nmol MUF g−1 min−1 |
variable | bg_aerob | float | ||
attribute | bg_aerob | _FillValue | float | NaN |
attribute | bg_aerob | actual_range | float | 0.0, 111.778 |
attribute | bg_aerob | bcodmo_name | String | unknown |
attribute | bg_aerob | description | String | B-glucosidase activity under aerobic conditions |
attribute | bg_aerob | long_name | String | Bg Aerob |
attribute | bg_aerob | units | String | nmol MUF g−1 min−1 |
variable | xy_aerob | float | ||
attribute | xy_aerob | _FillValue | float | NaN |
attribute | xy_aerob | actual_range | float | 0.0, 31.1253 |
attribute | xy_aerob | bcodmo_name | String | unknown |
attribute | xy_aerob | description | String | Xylosidase activity under aerobic conditions |
attribute | xy_aerob | long_name | String | Xy Aerob |
attribute | xy_aerob | units | String | nmol MUF g−1 min−1 |
variable | cb_aerob | float | ||
attribute | cb_aerob | _FillValue | float | NaN |
attribute | cb_aerob | actual_range | float | 0.0, 41.2463 |
attribute | cb_aerob | bcodmo_name | String | unknown |
attribute | cb_aerob | description | String | Cellobiosidase activity under aerobic conditions |
attribute | cb_aerob | long_name | String | Cb Aerob |
attribute | cb_aerob | units | String | nmol MUF g−1 min−1 |
variable | extractable_nitrate_aerob | float | ||
attribute | extractable_nitrate_aerob | _FillValue | float | NaN |
attribute | extractable_nitrate_aerob | actual_range | float | 1.14072, 144.913 |
attribute | extractable_nitrate_aerob | bcodmo_name | String | NO3 |
attribute | extractable_nitrate_aerob | colorBarMaximum | double | 50.0 |
attribute | extractable_nitrate_aerob | colorBarMinimum | double | 0.0 |
attribute | extractable_nitrate_aerob | description | String | Extractable Nitrate under aerobic conditions |
attribute | extractable_nitrate_aerob | long_name | String | Mole Concentration Of Nitrate In Sea Water |
attribute | extractable_nitrate_aerob | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P01/current/NTRAIGGS/ |
attribute | extractable_nitrate_aerob | units | String | mg kg-1 |
variable | extractable_ammonium_aerob | float | ||
attribute | extractable_ammonium_aerob | _FillValue | float | NaN |
attribute | extractable_ammonium_aerob | actual_range | float | 0.0213014, 21.5944 |
attribute | extractable_ammonium_aerob | bcodmo_name | String | Ammonium |
attribute | extractable_ammonium_aerob | colorBarMaximum | double | 5.0 |
attribute | extractable_ammonium_aerob | colorBarMinimum | double | 0.0 |
attribute | extractable_ammonium_aerob | description | String | Extractable Ammonium under aerobic conditions |
attribute | extractable_ammonium_aerob | long_name | String | Mole Concentration Of Ammonium In Sea Water |
attribute | extractable_ammonium_aerob | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P01/current/AMONAAZX/ |
attribute | extractable_ammonium_aerob | units | String | mg kg-1 |
variable | extractable_srp_aerob | float | ||
attribute | extractable_srp_aerob | _FillValue | float | NaN |
attribute | extractable_srp_aerob | actual_range | float | 0.0, 0.476284 |
attribute | extractable_srp_aerob | bcodmo_name | String | Soluble reactive phosphorus |
attribute | extractable_srp_aerob | description | String | Extractable Soluble Reactive Phosphorus under aerobic conditions |
attribute | extractable_srp_aerob | long_name | String | Extractable Srp Aerob |
attribute | extractable_srp_aerob | units | String | mg kg-1 |
variable | microbial_biomass_carbon_aerob | float | ||
attribute | microbial_biomass_carbon_aerob | _FillValue | float | NaN |
attribute | microbial_biomass_carbon_aerob | actual_range | float | 1458.1, 41232.3 |
attribute | microbial_biomass_carbon_aerob | bcodmo_name | String | biomass_C |
attribute | microbial_biomass_carbon_aerob | description | String | Microbial Biomass Carbon under aerobic conditions |
attribute | microbial_biomass_carbon_aerob | long_name | String | Microbial Biomass Carbon Aerob |
attribute | microbial_biomass_carbon_aerob | units | String | mg kg-1 |
variable | potentially_mineralizable_nitrate_aerob | float | ||
attribute | potentially_mineralizable_nitrate_aerob | _FillValue | float | NaN |
attribute | potentially_mineralizable_nitrate_aerob | actual_range | float | -0.247567, 8.99623 |
attribute | potentially_mineralizable_nitrate_aerob | bcodmo_name | String | unknown |
attribute | potentially_mineralizable_nitrate_aerob | colorBarMaximum | double | 50.0 |
attribute | potentially_mineralizable_nitrate_aerob | colorBarMinimum | double | 0.0 |
attribute | potentially_mineralizable_nitrate_aerob | description | String | Rate of nitrate mineralization (potential) under aerobic conditions |
attribute | potentially_mineralizable_nitrate_aerob | long_name | String | Mole Concentration Of Nitrate In Sea Water |
attribute | potentially_mineralizable_nitrate_aerob | units | String | mg NH4+ kg -1 d−1 |
variable | potentially_mineralizable_ammonium_aerob | float | ||
attribute | potentially_mineralizable_ammonium_aerob | _FillValue | float | NaN |
attribute | potentially_mineralizable_ammonium_aerob | actual_range | float | -4.45338, 0.439563 |
attribute | potentially_mineralizable_ammonium_aerob | bcodmo_name | String | unknown |
attribute | potentially_mineralizable_ammonium_aerob | colorBarMaximum | double | 5.0 |
attribute | potentially_mineralizable_ammonium_aerob | colorBarMinimum | double | 0.0 |
attribute | potentially_mineralizable_ammonium_aerob | description | String | Rate of ammonium mineralization (potential) under aerobic conditions |
attribute | potentially_mineralizable_ammonium_aerob | long_name | String | Mole Concentration Of Ammonium In Sea Water |
attribute | potentially_mineralizable_ammonium_aerob | units | String | mg NH4+ kg -1 d−1 |
variable | carbon_dioxide_rate_aerob | float | ||
attribute | carbon_dioxide_rate_aerob | _FillValue | float | NaN |
attribute | carbon_dioxide_rate_aerob | actual_range | float | 0.308214, 102.202 |
attribute | carbon_dioxide_rate_aerob | bcodmo_name | String | unknown |
attribute | carbon_dioxide_rate_aerob | description | String | Rate of carbon dioxide production (potential) under aerobic conditions |
attribute | carbon_dioxide_rate_aerob | long_name | String | Carbon Dioxide Rate Aerob |
attribute | carbon_dioxide_rate_aerob | units | String | mg CO2-C kg−1 h−1 |
variable | nag_anaerob | float | ||
attribute | nag_anaerob | _FillValue | float | NaN |
attribute | nag_anaerob | actual_range | float | 0.43613, 138.273 |
attribute | nag_anaerob | bcodmo_name | String | unknown |
attribute | nag_anaerob | description | String | N‐acetyl‐beta‐D‐glucosaminidase activity under anaerobic conditions |
attribute | nag_anaerob | long_name | String | Nag Anaerob |
attribute | nag_anaerob | units | String | nmol MUF g−1 min−1 |
variable | ap_anaerob | float | ||
attribute | ap_anaerob | _FillValue | float | NaN |
attribute | ap_anaerob | actual_range | float | 0.0, 90.3426 |
attribute | ap_anaerob | bcodmo_name | String | unknown |
attribute | ap_anaerob | description | String | Alkaline phosphatase activity under anaerobic conditions |
attribute | ap_anaerob | long_name | String | Ap Anaerob |
attribute | ap_anaerob | units | String | nmol MUF g−1 min−1 |
variable | bg_anaerob | float | ||
attribute | bg_anaerob | _FillValue | float | NaN |
attribute | bg_anaerob | actual_range | float | 0.0, 108.624 |
attribute | bg_anaerob | bcodmo_name | String | unknown |
attribute | bg_anaerob | description | String | B-glucosidase activity under anaerobic conditions |
attribute | bg_anaerob | long_name | String | Bg Anaerob |
attribute | bg_anaerob | units | String | nmol MUF g−1 min−1 |
variable | xy_anaerob | float | ||
attribute | xy_anaerob | _FillValue | float | NaN |
attribute | xy_anaerob | actual_range | float | 0.0, 43.0993 |
attribute | xy_anaerob | bcodmo_name | String | unknown |
attribute | xy_anaerob | description | String | Xylosidase activity under anaerobic conditions |
attribute | xy_anaerob | long_name | String | Xy Anaerob |
attribute | xy_anaerob | units | String | nmol MUF g−1 min−1 |
variable | cb_anaerob | float | ||
attribute | cb_anaerob | _FillValue | float | NaN |
attribute | cb_anaerob | actual_range | float | 0.0, 21.685 |
attribute | cb_anaerob | bcodmo_name | String | unknown |
attribute | cb_anaerob | description | String | Cellobiosidase activity under anaerobic conditions |
attribute | cb_anaerob | long_name | String | Cb Anaerob |
attribute | cb_anaerob | units | String | nmol MUF g−1 min−1 |
variable | extractable_nitrate_anaerob | float | ||
attribute | extractable_nitrate_anaerob | _FillValue | float | NaN |
attribute | extractable_nitrate_anaerob | actual_range | float | 1.0506, 41.4287 |
attribute | extractable_nitrate_anaerob | bcodmo_name | String | NO3 |
attribute | extractable_nitrate_anaerob | colorBarMaximum | double | 50.0 |
attribute | extractable_nitrate_anaerob | colorBarMinimum | double | 0.0 |
attribute | extractable_nitrate_anaerob | description | String | Extractable Nitrate under anaerobic conditions |
attribute | extractable_nitrate_anaerob | long_name | String | Mole Concentration Of Nitrate In Sea Water |
attribute | extractable_nitrate_anaerob | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P01/current/NTRAIGGS/ |
attribute | extractable_nitrate_anaerob | units | String | mg kg-1 |
variable | extractable_ammonium_anaerob | float | ||
attribute | extractable_ammonium_anaerob | _FillValue | float | NaN |
attribute | extractable_ammonium_anaerob | actual_range | float | 0.0, 116.26 |
attribute | extractable_ammonium_anaerob | bcodmo_name | String | Ammonium |
attribute | extractable_ammonium_anaerob | colorBarMaximum | double | 5.0 |
attribute | extractable_ammonium_anaerob | colorBarMinimum | double | 0.0 |
attribute | extractable_ammonium_anaerob | description | String | Extractable Ammonium under anaerobic conditions |
attribute | extractable_ammonium_anaerob | long_name | String | Mole Concentration Of Ammonium In Sea Water |
attribute | extractable_ammonium_anaerob | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P01/current/AMONAAZX/ |
attribute | extractable_ammonium_anaerob | units | String | mg kg-1 |
variable | extractable_srp_anaerob | float | ||
attribute | extractable_srp_anaerob | _FillValue | float | NaN |
attribute | extractable_srp_anaerob | actual_range | float | 0.0, 0.0333034 |
attribute | extractable_srp_anaerob | bcodmo_name | String | Soluble reactive phosphorus |
attribute | extractable_srp_anaerob | description | String | Extractable Soluble Reactive Phosphorus under anaerobic conditions |
attribute | extractable_srp_anaerob | long_name | String | Extractable Srp Anaerob |
attribute | extractable_srp_anaerob | units | String | mg kg-1 |
variable | microbial_biomass_carbon_anaerob | float | ||
attribute | microbial_biomass_carbon_anaerob | _FillValue | float | NaN |
attribute | microbial_biomass_carbon_anaerob | actual_range | float | 2434.16, 33393.3 |
attribute | microbial_biomass_carbon_anaerob | bcodmo_name | String | biomass_C |
attribute | microbial_biomass_carbon_anaerob | description | String | Microbial Biomass Carbon under anaerobic conditions |
attribute | microbial_biomass_carbon_anaerob | long_name | String | Microbial Biomass Carbon Anaerob |
attribute | microbial_biomass_carbon_anaerob | units | String | mg kg-1 |
variable | potentially_mineralizable_nitrate_anaerob | float | ||
attribute | potentially_mineralizable_nitrate_anaerob | _FillValue | float | NaN |
attribute | potentially_mineralizable_nitrate_anaerob | actual_range | float | -0.091205, 2.47716 |
attribute | potentially_mineralizable_nitrate_anaerob | bcodmo_name | String | NO3 |
attribute | potentially_mineralizable_nitrate_anaerob | colorBarMaximum | double | 50.0 |
attribute | potentially_mineralizable_nitrate_anaerob | colorBarMinimum | double | 0.0 |
attribute | potentially_mineralizable_nitrate_anaerob | description | String | Rate of nitrate mineralization (potential) under anaerobic conditions |
attribute | potentially_mineralizable_nitrate_anaerob | long_name | String | Mole Concentration Of Nitrate In Sea Water |
attribute | potentially_mineralizable_nitrate_anaerob | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P01/current/NTRAIGGS/ |
attribute | potentially_mineralizable_nitrate_anaerob | units | String | mg NH4+ kg -1 d−1 |
variable | potentially_mineralizable_ammonium_anaerob | float | ||
attribute | potentially_mineralizable_ammonium_anaerob | _FillValue | float | NaN |
attribute | potentially_mineralizable_ammonium_anaerob | actual_range | float | -1.59787, 5.95588 |
attribute | potentially_mineralizable_ammonium_anaerob | bcodmo_name | String | Ammonium |
attribute | potentially_mineralizable_ammonium_anaerob | colorBarMaximum | double | 5.0 |
attribute | potentially_mineralizable_ammonium_anaerob | colorBarMinimum | double | 0.0 |
attribute | potentially_mineralizable_ammonium_anaerob | description | String | Rate of ammonium mineralization (potential) under aerobic conditions |
attribute | potentially_mineralizable_ammonium_anaerob | long_name | String | Mole Concentration Of Ammonium In Sea Water |
attribute | potentially_mineralizable_ammonium_anaerob | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P01/current/AMONAAZX/ |
attribute | potentially_mineralizable_ammonium_anaerob | units | String | mg NH4+ kg -1 d−1 |
variable | carbon_dioxide_rate_anaerob | float | ||
attribute | carbon_dioxide_rate_anaerob | _FillValue | float | NaN |
attribute | carbon_dioxide_rate_anaerob | actual_range | float | 0.323712, 86.0494 |
attribute | carbon_dioxide_rate_anaerob | bcodmo_name | String | unknown |
attribute | carbon_dioxide_rate_anaerob | description | String | Rate of carbon dioxide production (potential) under anaerobic conditions |
attribute | carbon_dioxide_rate_anaerob | long_name | String | Carbon Dioxide Rate Anaerob |
attribute | carbon_dioxide_rate_anaerob | units | String | mg CO2-C kg−1 h−1 |
variable | moisture_content_pcnt_field | float | ||
attribute | moisture_content_pcnt_field | _FillValue | float | NaN |
attribute | moisture_content_pcnt_field | actual_range | float | 0.507518, 0.871855 |
attribute | moisture_content_pcnt_field | bcodmo_name | String | unknown |
attribute | moisture_content_pcnt_field | description | String | percent moisture content |
attribute | moisture_content_pcnt_field | long_name | String | Moisture Content Pcnt Field |
attribute | moisture_content_pcnt_field | units | String | precent |
variable | bulk_density_g_cm_3_field | float | ||
attribute | bulk_density_g_cm_3_field | _FillValue | float | NaN |
attribute | bulk_density_g_cm_3_field | actual_range | float | 0.0587003, 0.333452 |
attribute | bulk_density_g_cm_3_field | bcodmo_name | String | unknown |
attribute | bulk_density_g_cm_3_field | description | String | bulk density |
attribute | bulk_density_g_cm_3_field | long_name | String | Bulk Density G Cm 3 Field |
attribute | bulk_density_g_cm_3_field | units | String | g cm-3 |
variable | ph_field | float | ||
attribute | ph_field | _FillValue | float | NaN |
attribute | ph_field | actual_range | float | 5.57, 8.5 |
attribute | ph_field | bcodmo_name | String | pH |
attribute | ph_field | description | String | pH |
attribute | ph_field | long_name | String | Ph Field |
attribute | ph_field | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P01/current/PHXXZZXX/ |
attribute | ph_field | units | String | pH scale |
variable | pcnt_organic_matter_field | float | ||
attribute | pcnt_organic_matter_field | _FillValue | float | NaN |
attribute | pcnt_organic_matter_field | actual_range | float | 7.38236, 66.3895 |
attribute | pcnt_organic_matter_field | bcodmo_name | String | unknown |
attribute | pcnt_organic_matter_field | description | String | Organic matter content |
attribute | pcnt_organic_matter_field | long_name | String | Pcnt Organic Matter Field |
attribute | pcnt_organic_matter_field | units | String | percent |
variable | total_n_g_kg_field | float | ||
attribute | total_n_g_kg_field | _FillValue | float | NaN |
attribute | total_n_g_kg_field | actual_range | float | 1.2916, 17.5756 |
attribute | total_n_g_kg_field | bcodmo_name | String | N |
attribute | total_n_g_kg_field | description | String | Total Nitrogen |
attribute | total_n_g_kg_field | long_name | String | Total N G Kg Field |
attribute | total_n_g_kg_field | units | String | g kg-1 |
variable | total_c_g_kg_field | float | ||
attribute | total_c_g_kg_field | _FillValue | float | NaN |
attribute | total_c_g_kg_field | actual_range | float | 23.8271, 345.342 |
attribute | total_c_g_kg_field | bcodmo_name | String | C |
attribute | total_c_g_kg_field | description | String | Total Carbon |
attribute | total_c_g_kg_field | long_name | String | Total C G Kg Field |
attribute | total_c_g_kg_field | units | String | g kg-1 |
variable | total_n_g_cm_3_field | float | ||
attribute | total_n_g_cm_3_field | _FillValue | float | NaN |
attribute | total_n_g_cm_3_field | actual_range | float | 334.324, 1357.24 |
attribute | total_n_g_cm_3_field | bcodmo_name | String | N |
attribute | total_n_g_cm_3_field | description | String | Total Nitrogen |
attribute | total_n_g_cm_3_field | long_name | String | Total N G Cm 3 Field |
attribute | total_n_g_cm_3_field | units | String | g cm-3 |
variable | total_c_g_cm_3_field | float | ||
attribute | total_c_g_cm_3_field | _FillValue | float | NaN |
attribute | total_c_g_cm_3_field | actual_range | float | 6126.47, 22721.6 |
attribute | total_c_g_cm_3_field | bcodmo_name | String | C |
attribute | total_c_g_cm_3_field | description | String | Total Carbon |
attribute | total_c_g_cm_3_field | long_name | String | Total C G Cm 3 Field |
attribute | total_c_g_cm_3_field | units | String | g cm-3 |
variable | total_p_mg_kg_field | float | ||
attribute | total_p_mg_kg_field | _FillValue | float | NaN |
attribute | total_p_mg_kg_field | actual_range | float | 315.563, 854.92 |
attribute | total_p_mg_kg_field | bcodmo_name | String | P |
attribute | total_p_mg_kg_field | description | String | Total Phosphorus |
attribute | total_p_mg_kg_field | long_name | String | Total P Mg Kg Field |
attribute | total_p_mg_kg_field | units | String | mg kg-1 |
variable | nag_field | float | ||
attribute | nag_field | _FillValue | float | NaN |
attribute | nag_field | actual_range | float | 0.849778, 67.143 |
attribute | nag_field | bcodmo_name | String | unknown |
attribute | nag_field | description | String | N‐acetyl‐beta‐D‐glucosaminidase activity in the field |
attribute | nag_field | long_name | String | Nag Field |
attribute | nag_field | units | String | nmol MUF g−1 min−1 |
variable | ap_field | float | ||
attribute | ap_field | _FillValue | float | NaN |
attribute | ap_field | actual_range | float | 0.609154, 128.47 |
attribute | ap_field | bcodmo_name | String | unknown |
attribute | ap_field | description | String | Alkaline phosphatase activity in the field |
attribute | ap_field | long_name | String | Ap Field |
attribute | ap_field | units | String | nmol MUF g−1 min−1 |
variable | bg_field | float | ||
attribute | bg_field | _FillValue | float | NaN |
attribute | bg_field | actual_range | float | 0.862556, 124.116 |
attribute | bg_field | bcodmo_name | String | unknown |
attribute | bg_field | description | String | B-glucosidase activity in the field |
attribute | bg_field | long_name | String | Bg Field |
attribute | bg_field | units | String | nmol MUF g−1 min−1 |
variable | xy_field | float | ||
attribute | xy_field | _FillValue | float | NaN |
attribute | xy_field | actual_range | float | 0.215332, 27.377 |
attribute | xy_field | bcodmo_name | String | unknown |
attribute | xy_field | description | String | Xylosidase activity in the field |
attribute | xy_field | long_name | String | Xy Field |
attribute | xy_field | units | String | nmol MUF g−1 min−1 |
variable | cb_field | float | ||
attribute | cb_field | _FillValue | float | NaN |
attribute | cb_field | actual_range | float | 0.0803225, 14.7784 |
attribute | cb_field | bcodmo_name | String | unknown |
attribute | cb_field | description | String | Cellobiosidase activity in the field |
attribute | cb_field | long_name | String | Cb Field |
attribute | cb_field | units | String | nmol MUF g−1 min−1 |
variable | extractable_doc_field | float | ||
attribute | extractable_doc_field | _FillValue | float | NaN |
attribute | extractable_doc_field | actual_range | float | 46.7084, 1713.7 |
attribute | extractable_doc_field | bcodmo_name | String | DOC |
attribute | extractable_doc_field | description | String | Extractable Dissolved Organic Carbon in the field |
attribute | extractable_doc_field | long_name | String | Extractable Doc Field |
attribute | extractable_doc_field | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P01/current/CORGZZZX/ |
attribute | extractable_doc_field | units | String | mg kg-1 |
variable | extractable_nitrate_field | float | ||
attribute | extractable_nitrate_field | _FillValue | float | NaN |
attribute | extractable_nitrate_field | actual_range | float | 0.669632, 9.66034 |
attribute | extractable_nitrate_field | bcodmo_name | String | NO3 |
attribute | extractable_nitrate_field | colorBarMaximum | double | 50.0 |
attribute | extractable_nitrate_field | colorBarMinimum | double | 0.0 |
attribute | extractable_nitrate_field | description | String | Extractable Nitrate in the field |
attribute | extractable_nitrate_field | long_name | String | Mole Concentration Of Nitrate In Sea Water |
attribute | extractable_nitrate_field | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P01/current/NTRAIGGS/ |
attribute | extractable_nitrate_field | units | String | mg kg-1 |
variable | extractable_ammonium_field | float | ||
attribute | extractable_ammonium_field | _FillValue | float | NaN |
attribute | extractable_ammonium_field | actual_range | float | 0.0, 71.2923 |
attribute | extractable_ammonium_field | bcodmo_name | String | Ammonium |
attribute | extractable_ammonium_field | colorBarMaximum | double | 5.0 |
attribute | extractable_ammonium_field | colorBarMinimum | double | 0.0 |
attribute | extractable_ammonium_field | description | String | Extractable Ammonium in the field |
attribute | extractable_ammonium_field | long_name | String | Mole Concentration Of Ammonium In Sea Water |
attribute | extractable_ammonium_field | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P01/current/AMONAAZX/ |
attribute | extractable_ammonium_field | units | String | mg kg-1 |
variable | extractable_srp_field | float | ||
attribute | extractable_srp_field | _FillValue | float | NaN |
attribute | extractable_srp_field | actual_range | float | 0.0, 0.0898194 |
attribute | extractable_srp_field | bcodmo_name | String | Soluble reactive phosphorus |
attribute | extractable_srp_field | description | String | Extractable Soluble Reactive Phosphorus in the field |
attribute | extractable_srp_field | long_name | String | Extractable Srp Field |
attribute | extractable_srp_field | units | String | mg kg-1 |
variable | microbial_biomass_c_field | float | ||
attribute | microbial_biomass_c_field | _FillValue | float | NaN |
attribute | microbial_biomass_c_field | actual_range | float | 974.776, 12996.3 |
attribute | microbial_biomass_c_field | bcodmo_name | String | biomass_C |
attribute | microbial_biomass_c_field | description | String | Microbial Biomass Carbon in the field |
attribute | microbial_biomass_c_field | long_name | String | Microbial Biomass C Field |
attribute | microbial_biomass_c_field | units | String | mg kg-1 |
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.