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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 |
attribute | NC_GLOBAL | acquisition_description | String | Little Lagoon is a shallow coastal lagoon that is tidally connected to the\nGulf of Mexico but has no riverine inputs. The water in the lagoon is\nreplenished solely from precipitation and groundwater inputs primarily on the\nEast end (Su et al. 2012). Because of the rapid development in Baldwin County,\na large amount of NO3- enters the Little Lagoon system through SGD (Murgulet &\nTick 2008). In this region, there can be rapid changes in the depth to\ngroundwater (Fig. 4.1 inset) and episodic SGD inputs to the lagoon (Su et\nal.2013). Within the lagoon, three sites were selected (East, Mouth, and West)\nto represent the gradient that exists across the lagoon from the input of\ngroundwater. Sites were sampled on a near-monthly basis from February 2012 to\nFebruary 2013.\n \nDNRA\\u00a0 \n Approximately 1 L of outflow water was collected from the inflow water and\neach core forDNRA analysis. Appropriate sample volume was determined after NH4\n+ nutrient analysis and expected atom % enrichment. \\u03b415N-NH4 + was\nmeasured in samples, constructed blanks, and standards that bracketed the NH4\n+ concentration of the samples following a modified ammonium diffusion\nprocedure (Holmes et al. 1998) that collects NH4 + dissolved in water by\nconverting NH4 + to NH3 under basic conditions and then traps the NH3 on an\nacidified glass fiber filter. Non diffused standards were prepared according\nto Stark and Hart (1996) to account for blank corrections. After 15N analysis\non a Europa Scientific SL-2020 system (Stable Isotope Lab, Utah State\nUniversity), DNRA was calculated from the production rate of 15NH4 + (p15NH4\n+) during the incubation according to Christensen et. al (2000): (7) where is\nthe production of 15N-NH4 + and D14 and D15 are the denitrification rates of\n14N-NO3 - and 15N-NO3 -, respectively. This assumes that DNRA takes place in\nthe same sediment layers as denitrification and that the 15N labeling of NO3 -\nbeing reduced to NH4 + equals the 15N labeling of NO3 - being reduced to N2\n(Christensen et al. 2000).\n \nDenitrification and anammox from slurry assays\n \nVolumetric rates of denitrification, anammox, and the relative contribution of\nanammox to gross N2 production were determined from sediment slurry\nincubations. Slurry rates for depth-integrated sediments (0-50 mm) were\nprepared in Exetainers (Thamdrup & Dalsgaard 2002) with artificial seawater\n(ASW) (70.2g NaCl, 3.0g KCl, 49.4 g MgSO4*7H2O, 5.8g CaCl2*2H2O L-1)\nconstructed at a salinity of 52 and diluted with deionized water to match the\nsalinity of each site. After dilution, homogenized sediment from 0 to 50 mm\nwas added to the ASW and the incubation bottle was sparged with N2 and amended\nwith 100 \\u03bcmol L-1 Na15NO3 - (99 atom %). Sediment slurry was dispensed to\n12 ml Exetainers, yielding approximately 1 ml of sediment and 11 ml ASW with\nno headspace. For each site, 12 vials total were incubated with three vials\nstopped at time points 0 to 36 h. Incubations were stopped by adding 250\n\\u03bcL of ZnCl2 and resealing the vials without headspace. Denitrification\nand anammox rates in slurries were calculated according to equations 5 and 6\ndescribed below.\\u00a0\n \nExcess 29N2 and 30N2 concentrations for intact core and slurry incubations\nwere calculated from dissolved 29N2:28N2 and 30N2:28N2 measured using a MIMS.\nRates of excess 29N2 (p29) and 30N2 (p30) production were calculated from the\nflux calculation described above. Rates of ambient 14N2 production (p14) in\ncore incubations with 15NO3 - tracer addition were determined as (Nielsen\n1992, Risgaard-Petersen et al. 2003):\\u00a0\n \n(1) p14 = 2 x r14 \\u00b1 [p29 + p30 \\u00b1 (1 - r16)]\n \nThe 14N:15N ratio of NO3 - undergoing reduction to N2 (r14) was determined as\nfollows:\\u00a0\n \n(2) r14 = [R29 x (1 - ra) - ra] x (2 - ra) ^-1\n \nwhere R29 was the ratio of p29 to p30 determined for the cores and ra was the\nrelative contribution of anammox to gross N2 production determined in vial\nslurry incubations. Gross denitrification and anammox rates within intact\nsediment cores with 15NO3 - tracer addition were calculated as follows:\\u00a0\n \n(3) denitrification = p14 \\u00b1 (1 - ra)\n \n(4) anammox = p14 \\u00b1 ra\n \nDenitrification stimulated by the added 15N-NO3 - (D15) was calculated from\nthe classical IPT (Nielsen 1992) and these amended rates are a measure of the\ndenitrification capacity under field conditions when NO3 - is not\nlimiting.\\u00a0\n \nRates of denitrification and anammox in vial slurry incubations with 15NO3 -\namendments were calculated from the equations of Thamdrup and Dalsgaard\n(2002): (5) (6) where FN was the fraction of 15N in NO3 -. For months when\nanammox slurry incubations were not performed (August and November 2012), p14\nis calculated as D14 from the IPT (Nielsen 1992). Potential denitrification\nand anammox rates were converted to an areal basis using the wet weight of the\nsediment in the slurry. All rates and fluxes pertaining to N species in this\nstudy were normalized to one atom N.\n \nAdditional methodology can be found in:\n \nBernard, Rebecca & Mortazavi, Behzad & A. Kleinhuizen, Alice. (2015).\nDissimilatory nitrate reduction to ammonium (DNRA) seasonally dominates\nNO3\\u2212 reduction pathways in an anthropogenically impacted sub-tropical\ncoastal lagoon. Biogeochemistry. 125.\n47-64.\\u00a0[10.1007/s10533-015-0111-6](\\\\\"https://link.springer.com/article/10.1007%2Fs10533-015-0111-6\\\\\").\\u00a0 |
attribute | NC_GLOBAL | awards_0_award_nid | String | 497637 |
attribute | NC_GLOBAL | awards_0_award_number | String | OCE-0962008 |
attribute | NC_GLOBAL | awards_0_data_url | String | http://nsf.gov/awardsearch/showAward?AWD_ID=0962008 |
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 | Denitrification and DNRA \n B. Mortazavi and W. Burnett, PIs \n Version 16 January 2018 |
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 | 2018-01-17T20:11:39Z |
attribute | NC_GLOBAL | date_modified | String | 2019-03-15T18:07:13Z |
attribute | NC_GLOBAL | defaultDataQuery | String | &time<now |
attribute | NC_GLOBAL | doi | String | 10.1575/1912/bco-dmo.723966.1 |
attribute | NC_GLOBAL | infoUrl | String | https://www.bco-dmo.org/dataset/723966 |
attribute | NC_GLOBAL | institution | String | BCO-DMO |
attribute | NC_GLOBAL | instruments_0_acronym | String | IR Mass Spec |
attribute | NC_GLOBAL | instruments_0_dataset_instrument_description | String | Used for 15N analysis |
attribute | NC_GLOBAL | instruments_0_dataset_instrument_nid | String | 724410 |
attribute | NC_GLOBAL | instruments_0_description | String | The Isotope-ratio Mass Spectrometer is a particular type of mass spectrometer used to measure the relative abundance of isotopes in a given sample (e.g. VG Prism II Isotope Ratio Mass-Spectrometer). |
attribute | NC_GLOBAL | instruments_0_instrument_external_identifier | String | https://vocab.nerc.ac.uk/collection/L05/current/LAB16/ |
attribute | NC_GLOBAL | instruments_0_instrument_name | String | Isotope-ratio Mass Spectrometer |
attribute | NC_GLOBAL | instruments_0_instrument_nid | String | 469 |
attribute | NC_GLOBAL | instruments_0_supplied_name | String | Europa Scientific SL-2020 system |
attribute | NC_GLOBAL | instruments_1_dataset_instrument_description | String | Used to filter sediment |
attribute | NC_GLOBAL | instruments_1_dataset_instrument_nid | String | 724409 |
attribute | NC_GLOBAL | instruments_1_description | String | A pump is a device that moves fluids (liquids or gases), or sometimes slurries, by mechanical action. Pumps can be classified into three major groups according to the method they use to move the fluid: direct lift, displacement, and gravity pumps |
attribute | NC_GLOBAL | instruments_1_instrument_name | String | Pump |
attribute | NC_GLOBAL | instruments_1_instrument_nid | String | 726 |
attribute | NC_GLOBAL | instruments_1_supplied_name | String | Multichannel proportioning pump |
attribute | NC_GLOBAL | instruments_2_acronym | String | MIMS |
attribute | NC_GLOBAL | instruments_2_dataset_instrument_description | String | Used to measure dissolved gas |
attribute | NC_GLOBAL | instruments_2_dataset_instrument_nid | String | 724407 |
attribute | NC_GLOBAL | instruments_2_description | String | Membrane-introduction mass spectrometry (MIMS) is a method of introducing analytes into the mass spectrometer's vacuum chamber via a semipermeable membrane. |
attribute | NC_GLOBAL | instruments_2_instrument_name | String | Membrane Inlet Mass Spectrometer |
attribute | NC_GLOBAL | instruments_2_instrument_nid | String | 661606 |
attribute | NC_GLOBAL | instruments_2_supplied_name | String | MIMS |
attribute | NC_GLOBAL | instruments_3_acronym | String | CFA |
attribute | NC_GLOBAL | instruments_3_dataset_instrument_description | String | Used to measure continuous flow rate |
attribute | NC_GLOBAL | instruments_3_dataset_instrument_nid | String | 724408 |
attribute | NC_GLOBAL | instruments_3_description | String | A sample is injected into a flowing carrier solution passing rapidly through small-bore tubing. |
attribute | NC_GLOBAL | instruments_3_instrument_name | String | Continuous Flow Analyzer |
attribute | NC_GLOBAL | instruments_3_instrument_nid | String | 661968 |
attribute | NC_GLOBAL | instruments_3_supplied_name | String | Continuous Flow Analyzer |
attribute | NC_GLOBAL | keywords | String | bco, bco-dmo, biological, chemical, data, dataset, date, description, dmo, east, East_SE, erddap, management, mouth, Mouth_SE, oceanography, office, preliminary, value, Value_Description, west, West_SE, year |
attribute | NC_GLOBAL | license | String | https://www.bco-dmo.org/dataset/723966/license |
attribute | NC_GLOBAL | metadata_source | String | https://www.bco-dmo.org/api/dataset/723966 |
attribute | NC_GLOBAL | param_mapping | String | {'723966': {}} |
attribute | NC_GLOBAL | parameter_source | String | https://www.bco-dmo.org/mapserver/dataset/723966/parameters |
attribute | NC_GLOBAL | people_0_affiliation | String | National Science Foundation |
attribute | NC_GLOBAL | people_0_affiliation_acronym | String | NSF-DEB |
attribute | NC_GLOBAL | people_0_person_name | String | Dr Behzad Mortazavi |
attribute | NC_GLOBAL | people_0_person_nid | String | 491316 |
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 | Florida State University |
attribute | NC_GLOBAL | people_1_affiliation_acronym | String | FSU - EOAS |
attribute | NC_GLOBAL | people_1_person_name | String | Dr William C. Burnett |
attribute | NC_GLOBAL | people_1_person_nid | String | 491315 |
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 | National Science Foundation |
attribute | NC_GLOBAL | people_2_affiliation_acronym | String | NSF-DEB |
attribute | NC_GLOBAL | people_2_person_name | String | Dr Behzad Mortazavi |
attribute | NC_GLOBAL | people_2_person_nid | String | 491316 |
attribute | NC_GLOBAL | people_2_role | String | Contact |
attribute | NC_GLOBAL | people_2_role_type | String | related |
attribute | NC_GLOBAL | people_3_affiliation | String | Woods Hole Oceanographic Institution |
attribute | NC_GLOBAL | people_3_affiliation_acronym | String | WHOI BCO-DMO |
attribute | NC_GLOBAL | people_3_person_name | String | Hannah Ake |
attribute | NC_GLOBAL | people_3_person_nid | String | 650173 |
attribute | NC_GLOBAL | people_3_role | String | BCO-DMO Data Manager |
attribute | NC_GLOBAL | people_3_role_type | String | related |
attribute | NC_GLOBAL | project | String | LittleLagoonGroundwater |
attribute | NC_GLOBAL | projects_0_acronym | String | LittleLagoonGroundwater |
attribute | NC_GLOBAL | projects_0_description | String | This project investigated the link between submarine groundwater discharge (SGD) and microalgal dynamics in Little Lagoon, Alabama. In contrast to most near-shore environments, it is fully accessible; has no riverine inputs; and is large enough to display ecological diversity (c. 14x 0.75 km) yet small enough to be comprehensively sampled on appropriate temporal and spatial scales. The PIs have previously demonstrated that the lagoon is a hot-spot for toxic blooms of the diatom Pseudo-nitzchia spp. that are correlated with discharge from the surficial aquifer. This project assessed variability in SGD, the dependence of benthic nutrient fluxes on microphytobenthos (MPB) abundance and productivity, and the response of the phytoplankton to nutrient enrichment and dilution. The work integrated multiple temporal and spatial scales and demonstrated both the relative importance of SGD vs. benthic recycling as a source of nutrients, and the role of SGD in structuring the microalgal community. (paraphrased from Award abstract) |
attribute | NC_GLOBAL | projects_0_end_date | String | 2014-08 |
attribute | NC_GLOBAL | projects_0_geolocation | String | southern Alabama, east of Mobile |
attribute | NC_GLOBAL | projects_0_name | String | Groundwater Discharge, Benthic Coupling and Microalgal Community Structure in a Shallow Coastal Lagoon |
attribute | NC_GLOBAL | projects_0_project_nid | String | 491318 |
attribute | NC_GLOBAL | projects_0_start_date | String | 2010-03 |
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 | standard_name_vocabulary | String | CF Standard Name Table v55 |
attribute | NC_GLOBAL | summary | String | Denitrification and DNRA data from Little Lagoon, Alabama collected from 2012-2013 |
attribute | NC_GLOBAL | title | String | [Denitrification and DNRA] - Denitrification and DNRA data from Little Lagoon, Alabama collected from 2012-2013 (Groundwater Discharge, Benthic Coupling and Microalgal Community Structure in a Shallow Coastal Lagoon) |
attribute | NC_GLOBAL | version | String | 1 |
attribute | NC_GLOBAL | xml_source | String | osprey2erddap.update_xml() v1.3 |
variable | Year | byte | ||
attribute | Year | _FillValue | byte | 127 |
attribute | Year | actual_range | byte | 1, 2 |
attribute | Year | bcodmo_name | String | unknown |
attribute | Year | description | String | Year ID that samples were taken |
attribute | Year | long_name | String | Year |
attribute | Year | units | String | unitless |
variable | Value_Description | String | ||
attribute | Value_Description | bcodmo_name | String | unknown |
attribute | Value_Description | description | String | Description of the measurment taken; description includes relevant units for each sample taken; Descriptions include: DIN:DIP = ratio of dissolved inorganic nitrogen to dissolved inorganic phosphate; Denitrification = Denitrification; p14 ambient denitrification = ambient denitrification rates; DNRA = dissimilatory nitrate reduction to ammonium; D15 denitrification = denitrification from added heavy labeled isotope. |
attribute | Value_Description | long_name | String | Value Description |
attribute | Value_Description | units | String | unitless |
variable | Date | String | ||
attribute | Date | bcodmo_name | String | date |
attribute | Date | description | String | Month and day that samples were taken; MMM-DD |
attribute | Date | long_name | String | Date |
attribute | Date | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P01/current/ADATAA01/ |
attribute | Date | units | String | unitless |
variable | East | float | ||
attribute | East | _FillValue | float | NaN |
attribute | East | actual_range | float | -55.13, 5072.2 |
attribute | East | bcodmo_name | String | N |
attribute | East | description | String | Denitrification and DNRA values collected at the East site; location of site is 30.253347, -87.724729 |
attribute | East | long_name | String | East |
attribute | East | units | String | umol N m-2 hr-1; umol N m-2 d-1; mmol NH4+ m-2 d-1 |
variable | East_SE | float | ||
attribute | East_SE | _FillValue | float | NaN |
attribute | East_SE | actual_range | float | 0.0, 1260.2 |
attribute | East_SE | bcodmo_name | String | N |
attribute | East_SE | description | String | Standard error of denitrification and DNRA values collected at the East site |
attribute | East_SE | long_name | String | East SE |
attribute | East_SE | units | String | umol N m-2 hr-1; umol N m-2 d-1; mmol NH4+ m-2 d-1 |
variable | Mouth | float | ||
attribute | Mouth | _FillValue | float | NaN |
attribute | Mouth | actual_range | float | -52.28, 2549.4 |
attribute | Mouth | bcodmo_name | String | N |
attribute | Mouth | description | String | Denitrification and DNRA values collected at the Mouth site; location of site is 30.243683, -87.738407 |
attribute | Mouth | long_name | String | Mouth |
attribute | Mouth | units | String | umol N m-2 hr-1; umol N m-2 d-1; mmol NH4+ m-2 d-1 |
variable | Mouth_SE | float | ||
attribute | Mouth_SE | _FillValue | float | NaN |
attribute | Mouth_SE | actual_range | float | 0.0, 458.2 |
attribute | Mouth_SE | bcodmo_name | String | N |
attribute | Mouth_SE | description | String | Standard error of denitrification and DNRA values collected at the Mouth site |
attribute | Mouth_SE | long_name | String | Mouth SE |
attribute | Mouth_SE | units | String | umol N m-2 hr-1; umol N m-2 d-1; mmol NH4+ m-2 d-1 |
variable | West | float | ||
attribute | West | _FillValue | float | NaN |
attribute | West | actual_range | float | -77.78, 5678.0 |
attribute | West | bcodmo_name | String | N |
attribute | West | description | String | Denitrification and DNRA values collected at the West site; location of site is 30.247181, -87.767856 |
attribute | West | long_name | String | West |
attribute | West | units | String | umol N m-2 hr-1; umol N m-2 d-1; mmol NH4+ m-2 d-1 |
variable | West_SE | float | ||
attribute | West_SE | _FillValue | float | NaN |
attribute | West_SE | actual_range | float | 0.0, 1181.1 |
attribute | West_SE | bcodmo_name | String | N |
attribute | West_SE | description | String | Standard error of denitrification and DNRA values collected at the West site |
attribute | West_SE | long_name | String | West SE |
attribute | West_SE | units | String | umol N m-2 hr-1; umol N m-2 d-1; mmol NH4+ m-2 d-1 |