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On October 10, 2022 at 9:17:07 PM UTC, c17a0114-fe1c-4191-986b-40c4b31b670a:
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in resource Fluxes.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
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of resource Fluxes.csv to2022-10-10 21:15:09.778279
(previously2022-07-28 15:53:45.256938
) 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": "2022-10-10T21:17:04.367820", | n | 69 | "metadata_modified": "2022-10-10T21:17:07.295700", |
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, | ||
103 | "num_tags": 0, | 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", | ||
107 | "description": "The Dauphin Island Sea Lab's (DISL) mission is to | 107 | "description": "The Dauphin Island Sea Lab's (DISL) mission is to | ||
108 | become a center for transformative U.S. oceanic and coastal research | 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 | 109 | and education.. Founded in 1971 by the State of Alabama Legislature to | ||
110 | maximize the marine sciences capabilities of several Alabama | 110 | maximize the marine sciences capabilities of several Alabama | ||
111 | institutions and minimize duplication. \r\n\r\nLocated on the eastern | 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 | 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 | 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 | 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 | 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 | 116 | (UP)](https://www.disl.edu/univ-prog/) serves the students of the | ||
117 | Marine Environmental Sciences Consortium\u2019s (MESC) 22 public and | 117 | Marine Environmental Sciences Consortium\u2019s (MESC) 22 public and | ||
118 | private four-year colleges and universities through graduate and | 118 | private four-year colleges and universities through graduate and | ||
119 | undergraduate programs. Throughout the year, graduate students conduct | 119 | undergraduate programs. Throughout the year, graduate students conduct | ||
120 | research, and attend classes while completing their degree under the | 120 | research, and attend classes while completing their degree under the | ||
121 | mentorship of faculty and staff at the Dauphin Island Sea Lab. | 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/) | 122 | \r\n\r\n[The Discovery Hall Programs (DHP)](https://www.disl.edu/dhp/) | ||
123 | oversees educational programs for K-12 field programs, | 123 | oversees educational programs for K-12 field programs, | ||
124 | teacher-training, and community outreach opportunities. \r\n[The | 124 | teacher-training, and community outreach opportunities. \r\n[The | ||
125 | Estuarium](https://www.disl.edu/aquarium/), our public aquarium | 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 | 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 | 127 | educational outreach mission. The Estuarium focuses solely on the | ||
128 | Mobile-Tensaw Estuary System. The BayMobile allows DHP educators to | 128 | Mobile-Tensaw Estuary System. The BayMobile allows DHP educators to | ||
129 | bring marine science to students across Alabama in the classroom and | 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 | 130 | at community events. \r\n\r\nResearch programs at the Dauphin Island | ||
131 | Sea Lab range from biogeochemistry and oceanography to ecosystem | 131 | Sea Lab range from biogeochemistry and oceanography to ecosystem | ||
132 | ecology. While much of our research focuses on the near-shore and | 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 | 133 | estuarine processes of the northern Gulf of Mexico, field sites of our | ||
134 | internationally-renowned faculty also include the Arctic, Mexico, | 134 | internationally-renowned faculty also include the Arctic, Mexico, | ||
135 | Australia, and other countries.\r\n\r\nThe Dauphin Island Sea Lab also | 135 | Australia, and other countries.\r\n\r\nThe Dauphin Island Sea Lab also | ||
136 | offers state and local government, industry, and agency | 136 | offers state and local government, industry, and agency | ||
137 | decision-makers a range of coastal zone management services, including | 137 | decision-makers a range of coastal zone management services, including | ||
138 | access to the nationally acclaimed data management center. Armed with | 138 | access to the nationally acclaimed data management center. Armed with | ||
139 | data through the DISL data management center, entities can make | 139 | data through the DISL data management center, entities can make | ||
140 | well-informed decisions and sound policies while considering | 140 | well-informed decisions and sound policies while considering | ||
141 | environmental impact. Another key contributor to successful coastal | 141 | environmental impact. Another key contributor to successful coastal | ||
142 | zone management is the Mobile Bay National Estuary Program, which | 142 | zone management is the Mobile Bay National Estuary Program, which | ||
143 | falls within the services of DISL.\r\n\r\n", | 143 | falls within the services of DISL.\r\n\r\n", | ||
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