Changes
On October 10, 2022 at 9:16:59 PM UTC, c17a0114-fe1c-4191-986b-40c4b31b670a:
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Removed the following tags from Denitrification Capacity of a Natural and a Restored Marsh in the Northern Gulf of Mexico from 2014-02-27 to 2015-02-26 (NCEI Accession 0223379)
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Added the following fields to resource Site Characteristics.csv in Denitrification Capacity of a Natural and a Restored Marsh in the Northern Gulf of Mexico from 2014-02-27 to 2015-02-26 (NCEI Accession 0223379)
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resource_id with value
ignore_hash with value
set_url_type with value
task_created with value
ckan_url with value
original_url with value
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Changed value of field
datastore_active
toTrue
in resource Site Characteristics.csv in Denitrification Capacity of a Natural and a Restored Marsh in the Northern Gulf of Mexico from 2014-02-27 to 2015-02-26 (NCEI Accession 0223379) -
Changed value of field
datastore_contains_all_records_of_source_file
toTrue
in resource Site Characteristics.csv in Denitrification Capacity of a Natural and a Restored Marsh in the Northern Gulf of Mexico from 2014-02-27 to 2015-02-26 (NCEI Accession 0223379)
| f | 1 | { | f | 1 | { |
| 2 | "author": "Behzad Mortazavi", | 2 | "author": "Behzad Mortazavi", | ||
| 3 | "author_email": "bmortazavi@ua.edu", | 3 | "author_email": "bmortazavi@ua.edu", | ||
| 4 | "creator_user_id": "851c91e4-6343-45af-967a-20a33797707e", | 4 | "creator_user_id": "851c91e4-6343-45af-967a-20a33797707e", | ||
| 5 | "extras": [ | 5 | "extras": [ | ||
| 6 | { | 6 | { | ||
| 7 | "key": "ISO.principalInvestigator", | 7 | "key": "ISO.principalInvestigator", | ||
| 8 | "value": "Behzad Mortazavi <bmortazavi@ua.edu>" | 8 | "value": "Behzad Mortazavi <bmortazavi@ua.edu>" | ||
| 9 | }, | 9 | }, | ||
| 10 | { | 10 | { | ||
| 11 | "key": "Instrument Keywords", | 11 | "key": "Instrument Keywords", | ||
| 12 | "value": "CHN Analyzer, GPS, nutrient autoanalyzer, sediment | 12 | "value": "CHN Analyzer, GPS, nutrient autoanalyzer, sediment | ||
| 13 | sampler - corer, YSI - handheld multi-parameter instrument, | 13 | sampler - corer, YSI - handheld multi-parameter instrument, | ||
| 14 | AUTOANALYZER > AUTOANALYZER, CHN ANALYZERS > Carbon, Hydrogen, | 14 | AUTOANALYZER > AUTOANALYZER, CHN ANALYZERS > Carbon, Hydrogen, | ||
| 15 | Nitrogen Analyzers, GPS RECEIVERS > GPS RECEIVERS, SEDIMENT CORERS > | 15 | Nitrogen Analyzers, GPS RECEIVERS > GPS RECEIVERS, SEDIMENT CORERS > | ||
| 16 | SEDIMENT CORERS, 0.25 m2 quadrat, Carlo Erba element analyzer, Core | 16 | SEDIMENT CORERS, 0.25 m2 quadrat, Carlo Erba element analyzer, Core | ||
| 17 | tubes, Membrane Inlet Mass Spectrometer, Porewater sipper, Skalar SAN | 17 | tubes, Membrane Inlet Mass Spectrometer, Porewater sipper, Skalar SAN | ||
| 18 | + Autoanalyzer, Trimble NetRS GPS, Triplicate cores (ID 2.6 cm), YSI | 18 | + Autoanalyzer, Trimble NetRS GPS, Triplicate cores (ID 2.6 cm), YSI | ||
| 19 | 556 Multiparameter meter, cut off syringe corer (I.D. 1.3cm)" | 19 | 556 Multiparameter meter, cut off syringe corer (I.D. 1.3cm)" | ||
| 20 | }, | 20 | }, | ||
| 21 | { | 21 | { | ||
| 22 | "key": "NCEI Accession", | 22 | "key": "NCEI Accession", | ||
| 23 | "value": "0223379" | 23 | "value": "0223379" | ||
| 24 | }, | 24 | }, | ||
| 25 | { | 25 | { | ||
| 26 | "key": "Temporal Begin", | 26 | "key": "Temporal Begin", | ||
| 27 | "value": "2014-02-27" | 27 | "value": "2014-02-27" | ||
| 28 | }, | 28 | }, | ||
| 29 | { | 29 | { | ||
| 30 | "key": "Temporal End", | 30 | "key": "Temporal End", | ||
| 31 | "value": "2015-02-26" | 31 | "value": "2015-02-26" | ||
| 32 | }, | 32 | }, | ||
| 33 | { | 33 | { | ||
| 34 | "key": "Theme Keywords", | 34 | "key": "Theme Keywords", | ||
| 35 | "value": "C:N, Carbon content of the sediment as percentage, | 35 | "value": "C:N, Carbon content of the sediment as percentage, | ||
| 36 | Chl-a extracted from sediments (mg m-2), D14 (denitrification rates | 36 | Chl-a extracted from sediments (mg m-2), D14 (denitrification rates | ||
| 37 | from ambient nitrate) (uM N m-2 hr-1), D15 (denitrification rates from | 37 | from ambient nitrate) (uM N m-2 hr-1), D15 (denitrification rates from | ||
| 38 | added 15 nitrate isotope) (uM N m-2 hr-1), DNF (Denitrification) | 38 | added 15 nitrate isotope) (uM N m-2 hr-1), DNF (Denitrification) | ||
| 39 | Capacity (uM N m-2 hr-1), Dn14 (coupled nitriciation-denitrification) | 39 | Capacity (uM N m-2 hr-1), Dn14 (coupled nitriciation-denitrification) | ||
| 40 | (uM N m-2 hr-1), Dn14 percent of D14, Dried organic biomass above | 40 | (uM N m-2 hr-1), Dn14 percent of D14, Dried organic biomass above | ||
| 41 | ground (kg m-2), Dried organic biomass belowground in experiment cores | 41 | ground (kg m-2), Dried organic biomass belowground in experiment cores | ||
| 42 | to a depth of 20 cm (kg m-2), Dw14 (direct denitrification rates of in | 42 | to a depth of 20 cm (kg m-2), Dw14 (direct denitrification rates of in | ||
| 43 | situ water column nitrate) (uM N m-2 hr-1), Elevation, NH4 extracted | 43 | situ water column nitrate) (uM N m-2 hr-1), Elevation, NH4 extracted | ||
| 44 | from sediments in nmole g-1 dry sediment, NH4 flux rates (uM N m-2 | 44 | from sediments in nmole g-1 dry sediment, NH4 flux rates (uM N m-2 | ||
| 45 | hr-1), NO3 flux rates (uM N m-2 hr-1), PO4 flux rates (uM N m-2 hr-1), | 45 | hr-1), NO3 flux rates (uM N m-2 hr-1), PO4 flux rates (uM N m-2 hr-1), | ||
| 46 | Porewater NH4 at 10 cm depth (micromolar), Porewater NO2 at 10 cm | 46 | Porewater NH4 at 10 cm depth (micromolar), Porewater NO2 at 10 cm | ||
| 47 | depth (micromolar), Porewater NO3 at 10 cm depth (micromolar), | 47 | depth (micromolar), Porewater NO3 at 10 cm depth (micromolar), | ||
| 48 | Porewater NOx at 10 cm depth (micromolar), Porewater PO4 at 10 cm | 48 | Porewater NOx at 10 cm depth (micromolar), Porewater PO4 at 10 cm | ||
| 49 | depth (micromolar), Porewater Sulfide at 10 cm depth (micromolar), | 49 | depth (micromolar), Porewater Sulfide at 10 cm depth (micromolar), | ||
| 50 | Sample replicates, Sampling site type, Seawater NH4 (micromolar), | 50 | Sample replicates, Sampling site type, Seawater NH4 (micromolar), | ||
| 51 | Seawater NO2 (micromolar), Seawater NO3 (micromolar), Seawater NOx | 51 | Seawater NO2 (micromolar), Seawater NO3 (micromolar), Seawater NOx | ||
| 52 | (micromolar), Seawater PO4 (micromolar)" | 52 | (micromolar), Seawater PO4 (micromolar)" | ||
| 53 | }, | 53 | }, | ||
| 54 | { | 54 | { | ||
| 55 | "key": "spatial", | 55 | "key": "spatial", | ||
| 56 | "value": "{ \"type\": \"Polygon\", \"coordinates\": [ [ [ | 56 | "value": "{ \"type\": \"Polygon\", \"coordinates\": [ [ [ | ||
| 57 | -88.0828,30.2508 ], [ -88.0828, 30.2522 ], [ -88.0778, 30.2522 ], [ | 57 | -88.0828,30.2508 ], [ -88.0828, 30.2522 ], [ -88.0778, 30.2522 ], [ | ||
| 58 | -88.0778, 30.2508 ], [ -88.0828,30.2508] ] ] }" | 58 | -88.0778, 30.2508 ], [ -88.0828,30.2508] ] ] }" | ||
| 59 | } | 59 | } | ||
| 60 | ], | 60 | ], | ||
| 61 | "groups": [], | 61 | "groups": [], | ||
| 62 | "id": "d09effd4-b11c-400e-9264-e5f98940e256", | 62 | "id": "d09effd4-b11c-400e-9264-e5f98940e256", | ||
| 63 | "isopen": false, | 63 | "isopen": false, | ||
| 64 | "license_id": "", | 64 | "license_id": "", | ||
| 65 | "license_title": "", | 65 | "license_title": "", | ||
| 66 | "maintainer": "data@disl.org", | 66 | "maintainer": "data@disl.org", | ||
| 67 | "maintainer_email": "data@disl.org", | 67 | "maintainer_email": "data@disl.org", | ||
| 68 | "metadata_created": "2022-07-27T21:54:10.230554", | 68 | "metadata_created": "2022-07-27T21:54:10.230554", | ||
| n | 69 | "metadata_modified": "2022-07-28T20:42:14.111161", | n | 69 | "metadata_modified": "2022-10-10T21:16:58.803765", |
| 70 | "name": | 70 | "name": | ||
| 71 | atural-and-a-restored-marsh-in-the-northern-gulf-of-mexico-from-2014", | 71 | atural-and-a-restored-marsh-in-the-northern-gulf-of-mexico-from-2014", | ||
| 72 | "notes": "### Description\r\nThis dataset includes denitrification | 72 | "notes": "### Description\r\nThis dataset includes denitrification | ||
| 73 | rates across a typical northern Gulf of Mexico salt marsh landscape | 73 | rates across a typical northern Gulf of Mexico salt marsh landscape | ||
| 74 | that included a natural marsh, a tidal creek, and a 21-year-old | 74 | that included a natural marsh, a tidal creek, and a 21-year-old | ||
| 75 | restored salt marsh. Denitrification capacity, measured with the | 75 | restored salt marsh. Denitrification capacity, measured with the | ||
| 76 | isotope pairing technique on a membrane inlet mass spectrometer, was | 76 | isotope pairing technique on a membrane inlet mass spectrometer, was | ||
| 77 | comparable across the sites despite significant differences in above | 77 | comparable across the sites despite significant differences in above | ||
| 78 | and below ground characteristics. Total extractable ammonium | 78 | and below ground characteristics. Total extractable ammonium | ||
| 79 | concentrations and sediment carbon content were higher at the natural | 79 | concentrations and sediment carbon content were higher at the natural | ||
| 80 | marsh compared to the restored marsh. Hydrogen sulfide concentrations | 80 | marsh compared to the restored marsh. Hydrogen sulfide concentrations | ||
| 81 | were highest at the creek compared to the vegetated sites and lowest | 81 | were highest at the creek compared to the vegetated sites and lowest | ||
| 82 | at the restored marsh. This suggests that marsh restoration projects | 82 | at the restored marsh. This suggests that marsh restoration projects | ||
| 83 | reestablish nitrogen removal capacity at rates similar to those in | 83 | reestablish nitrogen removal capacity at rates similar to those in | ||
| 84 | natural systems and can help to significantly reduce nitrogen loads to | 84 | natural systems and can help to significantly reduce nitrogen loads to | ||
| 85 | the coastal ocean. \r\n\r\n### Purpose\r\nThis dataset on | 85 | the coastal ocean. \r\n\r\n### Purpose\r\nThis dataset on | ||
| 86 | denitrification rates in restored and a nearby natural marsh are used | 86 | denitrification rates in restored and a nearby natural marsh are used | ||
| 87 | to demonstrate that restored marshes can achieve nitrogen removal | 87 | to demonstrate that restored marshes can achieve nitrogen removal | ||
| 88 | capacity that is similar to that natural marshes. This is despite some | 88 | capacity that is similar to that natural marshes. This is despite some | ||
| 89 | differences with the lower carbon content and total extractable | 89 | differences with the lower carbon content and total extractable | ||
| 90 | ammonium and porewater phosphate, and nitrate and hydrogen sulfide | 90 | ammonium and porewater phosphate, and nitrate and hydrogen sulfide | ||
| 91 | concentrations compared to the natural marsh. While not all ecosystem | 91 | concentrations compared to the natural marsh. While not all ecosystem | ||
| 92 | attributes recover at the same rate following restoration, functions | 92 | attributes recover at the same rate following restoration, functions | ||
| 93 | like nitrogen removal appear to recover and help with removing | 93 | like nitrogen removal appear to recover and help with removing | ||
| 94 | nitrogen that would otherwise be exported to nearby coastal | 94 | nitrogen that would otherwise be exported to nearby coastal | ||
| 95 | waters.\r\n\r\n### Suggested Citation\r\n[Mortazavi, Behzad; | 95 | waters.\r\n\r\n### Suggested Citation\r\n[Mortazavi, Behzad; | ||
| 96 | Kleinhuizen, Alice (2021). Denitrification Capacity of a Natural and a | 96 | Kleinhuizen, Alice (2021). Denitrification Capacity of a Natural and a | ||
| 97 | Restored Marsh in the Northern Gulf of Mexico from 2014-02-27 to | 97 | Restored Marsh in the Northern Gulf of Mexico from 2014-02-27 to | ||
| 98 | 2015-02-26 (NCEI Accession 0223379). [indicate subset used]. NOAA | 98 | 2015-02-26 (NCEI Accession 0223379). [indicate subset used]. NOAA | ||
| 99 | National Centers for Environmental Information. Dataset. | 99 | National Centers for Environmental Information. Dataset. | ||
| 100 | https://www.ncei.noaa.gov/archive/accession/0223379. Accessed | 100 | https://www.ncei.noaa.gov/archive/accession/0223379. Accessed | ||
| 101 | [date].](https://www.ncei.noaa.gov/archive/accession/0223379)", | 101 | [date].](https://www.ncei.noaa.gov/archive/accession/0223379)", | ||
| 102 | "num_resources": 15, | 102 | "num_resources": 15, | ||
| n | 103 | "num_tags": 10, | n | 103 | "num_tags": 0, |
| 104 | "organization": { | 104 | "organization": { | ||
| 105 | "approval_status": "approved", | 105 | "approval_status": "approved", | ||
| 106 | "created": "2022-07-22T03:25:13.329710", | 106 | "created": "2022-07-22T03:25:13.329710", | ||
| n | 107 | "description": "The Dauphin Island Sea Lab organization.", | n | 107 | "description": "The Dauphin Island Sea Lab's (DISL) mission is to |
| 108 | become a center for transformative U.S. oceanic and coastal research | ||||
| 109 | and education.. Founded in 1971 by the State of Alabama Legislature to | ||||
| 110 | maximize the marine sciences capabilities of several Alabama | ||||
| 111 | institutions and minimize duplication. \r\n\r\nLocated on the eastern | ||||
| 112 | tip of Dauphin Island, a barrier island in the northern Gulf of | ||||
| 113 | Mexico, DISL is surrounded by Mobile Bay, the Mississippi Sound, and | ||||
| 114 | the waters of the Gulf, making it a perfect location to conduct a wide | ||||
| 115 | range of marine science activity. \r\n\r\n[The University Programs | ||||
| 116 | (UP)](https://www.disl.edu/univ-prog/) serves the students of the | ||||
| 117 | Marine Environmental Sciences Consortium\u2019s (MESC) 22 public and | ||||
| 118 | private four-year colleges and universities through graduate and | ||||
| 119 | undergraduate programs. Throughout the year, graduate students conduct | ||||
| 120 | research, and attend classes while completing their degree under the | ||||
| 121 | mentorship of faculty and staff at the Dauphin Island Sea Lab. | ||||
| 122 | \r\n\r\n[The Discovery Hall Programs (DHP)](https://www.disl.edu/dhp/) | ||||
| 123 | oversees educational programs for K-12 field programs, | ||||
| 124 | teacher-training, and community outreach opportunities. \r\n[The | ||||
| 125 | Estuarium](https://www.disl.edu/aquarium/), our public aquarium | ||||
| 126 | located on the Dauphin Island Sea Lab campus, is a part of DHP's | ||||
| 127 | educational outreach mission. The Estuarium focuses solely on the | ||||
| 128 | Mobile-Tensaw Estuary System. The BayMobile allows DHP educators to | ||||
| 129 | bring marine science to students across Alabama in the classroom and | ||||
| 130 | at community events. \r\n\r\nResearch programs at the Dauphin Island | ||||
| 131 | Sea Lab range from biogeochemistry and oceanography to ecosystem | ||||
| 132 | ecology. While much of our research focuses on the near-shore and | ||||
| 133 | estuarine processes of the northern Gulf of Mexico, field sites of our | ||||
| 134 | internationally-renowned faculty also include the Arctic, Mexico, | ||||
| 135 | Australia, and other countries.\r\n\r\nThe Dauphin Island Sea Lab also | ||||
| 136 | offers state and local government, industry, and agency | ||||
| 137 | decision-makers a range of coastal zone management services, including | ||||
| 138 | access to the nationally acclaimed data management center. Armed with | ||||
| 139 | data through the DISL data management center, entities can make | ||||
| 140 | well-informed decisions and sound policies while considering | ||||
| 141 | environmental impact. Another key contributor to successful coastal | ||||
| 142 | zone management is the Mobile Bay National Estuary Program, which | ||||
| 143 | falls within the services of DISL.\r\n\r\n", | ||||
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| 111 | "name": "dauphin-island-sea-lab", | 148 | "name": "dauphin-island-sea-lab", | ||
| 112 | "state": "active", | 149 | "state": "active", | ||
| 113 | "title": "Dauphin Island Sea Lab", | 150 | "title": "Dauphin Island Sea Lab", | ||
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