Changes
On July 27, 2022 at 2:33:29 PM UTC, 851c91e4-6343-45af-967a-20a33797707e:
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Added resource R4.x262.000-0022-metadata.xml to Spatial heterogeneity of nitrogen cycling in Deepwater Horizon-impacted salt marshes from May 2016-February 2017
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": "DOI", | 7 | "key": "DOI", | ||
8 | "value": "doi:10.7266/N7251GJ3" | 8 | "value": "doi:10.7266/N7251GJ3" | ||
9 | }, | 9 | }, | ||
10 | { | 10 | { | ||
11 | "key": "ISO.principalInvestigator", | 11 | "key": "ISO.principalInvestigator", | ||
12 | "value": "Behzad Mortazavi <bmortazavi@ua.edu>" | 12 | "value": "Behzad Mortazavi <bmortazavi@ua.edu>" | ||
13 | }, | 13 | }, | ||
14 | { | 14 | { | ||
15 | "key": "Place Keywords", | 15 | "key": "Place Keywords", | ||
16 | "value": "Chandeleur Islands, northern Gulf of Mexico" | 16 | "value": "Chandeleur Islands, northern Gulf of Mexico" | ||
17 | }, | 17 | }, | ||
18 | { | 18 | { | ||
19 | "key": "Temporal Begin", | 19 | "key": "Temporal Begin", | ||
20 | "value": "2016-05-24" | 20 | "value": "2016-05-24" | ||
21 | }, | 21 | }, | ||
22 | { | 22 | { | ||
23 | "key": "Temporal End", | 23 | "key": "Temporal End", | ||
24 | "value": "2017-02-23" | 24 | "value": "2017-02-23" | ||
25 | }, | 25 | }, | ||
26 | { | 26 | { | ||
27 | "key": "Theme Keywords", | 27 | "key": "Theme Keywords", | ||
28 | "value": "ecosystem resilience, denitrification, nitrogen | 28 | "value": "ecosystem resilience, denitrification, nitrogen | ||
29 | fixation, disturbance, nitrogen cycle, Deepwater Horizon, salt marsh" | 29 | fixation, disturbance, nitrogen cycle, Deepwater Horizon, salt marsh" | ||
30 | }, | 30 | }, | ||
31 | { | 31 | { | ||
32 | "key": "spatial", | 32 | "key": "spatial", | ||
33 | "value": "{ \"type\": \"Polygon\", \"coordinates\": [ [ [ | 33 | "value": "{ \"type\": \"Polygon\", \"coordinates\": [ [ [ | ||
34 | -88.841466, 29.927599 ], [ -88.82778, 29.927599 ], [ -88.82778, | 34 | -88.841466, 29.927599 ], [ -88.82778, 29.927599 ], [ -88.82778, | ||
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36 | } | 36 | } | ||
37 | ], | 37 | ], | ||
38 | "groups": [], | 38 | "groups": [], | ||
39 | "id": "7bbccd32-db02-4df3-9350-12c634aa0fca", | 39 | "id": "7bbccd32-db02-4df3-9350-12c634aa0fca", | ||
40 | "isopen": false, | 40 | "isopen": false, | ||
41 | "license_id": null, | 41 | "license_id": null, | ||
42 | "license_title": null, | 42 | "license_title": null, | ||
43 | "maintainer": "data@disl.org", | 43 | "maintainer": "data@disl.org", | ||
44 | "maintainer_email": "data@disl.org", | 44 | "maintainer_email": "data@disl.org", | ||
45 | "metadata_created": "2022-07-27T14:33:28.644194", | 45 | "metadata_created": "2022-07-27T14:33:28.644194", | ||
n | 46 | "metadata_modified": "2022-07-27T14:33:28.644200", | n | 46 | "metadata_modified": "2022-07-27T14:33:29.078021", |
47 | "name": | 47 | "name": | ||
48 | n-cycling-in-deepwater-horizon-impacted-salt-marshes-from-man7251gj3", | 48 | n-cycling-in-deepwater-horizon-impacted-salt-marshes-from-man7251gj3", | ||
49 | "notes": "### Abstract\nHumans have more than doubled the amount of | 49 | "notes": "### Abstract\nHumans have more than doubled the amount of | ||
50 | reactive nitrogen (N) in the environment, contributing to marine | 50 | reactive nitrogen (N) in the environment, contributing to marine | ||
51 | eutrophication. Salt marshes provide important areas of N removal | 51 | eutrophication. Salt marshes provide important areas of N removal | ||
52 | through microbial mediated N-cyling. However, oil spills may alter or | 52 | through microbial mediated N-cyling. However, oil spills may alter or | ||
53 | reduce their functional capacity by reducing plant biomass or altering | 53 | reduce their functional capacity by reducing plant biomass or altering | ||
54 | sediment microbial communities. The objective of our study is to | 54 | sediment microbial communities. The objective of our study is to | ||
55 | determine the effects of the Deepwater Horizon oil spill on nitrogen | 55 | determine the effects of the Deepwater Horizon oil spill on nitrogen | ||
56 | (N) cycling in salt marsh sediments. A study was conducted in the | 56 | (N) cycling in salt marsh sediments. A study was conducted in the | ||
57 | Chandeleur Islands, a chain of barrier islands off the coast of | 57 | Chandeleur Islands, a chain of barrier islands off the coast of | ||
58 | Louisiana which were subjected to a gradient of oil deposition | 58 | Louisiana which were subjected to a gradient of oil deposition | ||
59 | following the spill. Starting in June 2016, we collected sediments | 59 | following the spill. Starting in June 2016, we collected sediments | ||
60 | from three sites subjected to a range of oiling to determine the | 60 | from three sites subjected to a range of oiling to determine the | ||
61 | legacy effect of the oil spill on sediment denitrification and | 61 | legacy effect of the oil spill on sediment denitrification and | ||
62 | nitrogen fixation (N2-fixation). Denitrification capacity, which was | 62 | nitrogen fixation (N2-fixation). Denitrification capacity, which was | ||
63 | determined using the isotope-pairing technique, was highest in | 63 | determined using the isotope-pairing technique, was highest in | ||
64 | September (63.9\u00b130.2) \u00b5mol N m-2 h-1).\n\n### Purpose\nThe | 64 | September (63.9\u00b130.2) \u00b5mol N m-2 h-1).\n\n### Purpose\nThe | ||
65 | purpose of this study was to determine the long-term impacts of oiling | 65 | purpose of this study was to determine the long-term impacts of oiling | ||
66 | on salt marsh ecosystem function (i.e. denitrification and nitrogen | 66 | on salt marsh ecosystem function (i.e. denitrification and nitrogen | ||
67 | fixation) as well as drivers of ecosystem function (i.e. microbial | 67 | fixation) as well as drivers of ecosystem function (i.e. microbial | ||
68 | community composition and functional abundance, environmental | 68 | community composition and functional abundance, environmental | ||
69 | conditions).\n\n**DOI: | 69 | conditions).\n\n**DOI: | ||
70 | [doi:10.7266/N7251GJ3](https://www.doi.org/10.7266/N7251GJ3)**\n\n### | 70 | [doi:10.7266/N7251GJ3](https://www.doi.org/10.7266/N7251GJ3)**\n\n### | ||
71 | Suggested Citation\nCorianne Tatariw, Nikaela Flournoy, Alice | 71 | Suggested Citation\nCorianne Tatariw, Nikaela Flournoy, Alice | ||
72 | Kleinhuizen, Derek Tollette, Edward Overton, Patricia Sobecky, Behzad | 72 | Kleinhuizen, Derek Tollette, Edward Overton, Patricia Sobecky, Behzad | ||
73 | Mortazavi. 2018. Spatial heterogeneity of nitrogen cycling in | 73 | Mortazavi. 2018. Spatial heterogeneity of nitrogen cycling in | ||
74 | Deepwater Horizon-impacted salt marshes from May 2016-February 2017. | 74 | Deepwater Horizon-impacted salt marshes from May 2016-February 2017. | ||
75 | Distributed by: Gulf of Mexico Research Initiative Information and | 75 | Distributed by: Gulf of Mexico Research Initiative Information and | ||
76 | Data Cooperative (GRIIDC), Harte Research Institute, Texas A&M | 76 | Data Cooperative (GRIIDC), Harte Research Institute, Texas A&M | ||
77 | University\u2013Corpus Christi. doi:10.7266/N7251GJ3\n\n### Related | 77 | University\u2013Corpus Christi. doi:10.7266/N7251GJ3\n\n### Related | ||
78 | Publication Citation\n[Tatariw, C., Flournoy, N., Kleinhuizen, A. A., | 78 | Publication Citation\n[Tatariw, C., Flournoy, N., Kleinhuizen, A. A., | ||
79 | Tollette, D., Overton, E. B., Sobecky, P. A., & Mortazavi, B. (2018). | 79 | Tollette, D., Overton, E. B., Sobecky, P. A., & Mortazavi, B. (2018). | ||
80 | Salt marsh denitrification is impacted by oiling intensity six years | 80 | Salt marsh denitrification is impacted by oiling intensity six years | ||
81 | after the Deepwater Horizon oil spill. Environmental Pollution, 243, | 81 | after the Deepwater Horizon oil spill. Environmental Pollution, 243, | ||
82 | 1606\u20131614. | 82 | 1606\u20131614. | ||
83 | 09.034\n](https://dx.doi.org/10.1016/j.envpol.2018.09.034)\n\n**Funded | 83 | 09.034\n](https://dx.doi.org/10.1016/j.envpol.2018.09.034)\n\n**Funded | ||
84 | by:** Gulf of Mexico Research Initiative (GoMRI)\n\n**Funding cycle:** | 84 | by:** Gulf of Mexico Research Initiative (GoMRI)\n\n**Funding cycle:** | ||
85 | RFP-IV\n\n**Research group:** Alabama Center for Ecological Resilience | 85 | RFP-IV\n\n**Research group:** Alabama Center for Ecological Resilience | ||
86 | (ACER)\n\n", | 86 | (ACER)\n\n", | ||
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90 | "approval_status": "approved", | 90 | "approval_status": "approved", | ||
91 | "created": "2022-07-22T03:25:13.329710", | 91 | "created": "2022-07-22T03:25:13.329710", | ||
92 | "description": "The Dauphin Island Sea Lab organization.", | 92 | "description": "The Dauphin Island Sea Lab organization.", | ||
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96 | "name": "dauphin-island-sea-lab", | 96 | "name": "dauphin-island-sea-lab", | ||
97 | "state": "active", | 97 | "state": "active", | ||
98 | "title": "Dauphin Island Sea Lab", | 98 | "title": "Dauphin Island Sea Lab", | ||
99 | "type": "organization" | 99 | "type": "organization" | ||
100 | }, | 100 | }, | ||
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106 | "state": "active", | 131 | "state": "active", | ||
107 | "tags": [ | 132 | "tags": [ | ||
108 | { | 133 | { | ||
109 | "display_name": "Chandeleur Islands", | 134 | "display_name": "Chandeleur Islands", | ||
110 | "id": "1187d400-d9de-4166-aca2-2e591ecf8c65", | 135 | "id": "1187d400-d9de-4166-aca2-2e591ecf8c65", | ||
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113 | "vocabulary_id": null | 138 | "vocabulary_id": null | ||
114 | }, | 139 | }, | ||
115 | { | 140 | { | ||
116 | "display_name": "Deepwater Horizon", | 141 | "display_name": "Deepwater Horizon", | ||
117 | "id": "0e13401a-3910-4b7f-9e17-df754fe3f24a", | 142 | "id": "0e13401a-3910-4b7f-9e17-df754fe3f24a", | ||
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120 | "vocabulary_id": null | 145 | "vocabulary_id": null | ||
121 | }, | 146 | }, | ||
122 | { | 147 | { | ||
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124 | "id": "ef3cdb87-1cb1-463e-b2d0-5d94ea0794b0", | 149 | "id": "ef3cdb87-1cb1-463e-b2d0-5d94ea0794b0", | ||
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135 | }, | 160 | }, | ||
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142 | }, | 167 | }, | ||
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152 | "id": "be89dc95-5664-48d2-9fd8-d4c0844c595a", | 177 | "id": "be89dc95-5664-48d2-9fd8-d4c0844c595a", | ||
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154 | "state": "active", | 179 | "state": "active", | ||
155 | "vocabulary_id": null | 180 | "vocabulary_id": null | ||
156 | }, | 181 | }, | ||
157 | { | 182 | { | ||
158 | "display_name": "northern Gulf of Mexico", | 183 | "display_name": "northern Gulf of Mexico", | ||
159 | "id": "511c4d3a-d5d8-438d-af93-0bbe19b42564", | 184 | "id": "511c4d3a-d5d8-438d-af93-0bbe19b42564", | ||
160 | "name": "northern Gulf of Mexico", | 185 | "name": "northern Gulf of Mexico", | ||
161 | "state": "active", | 186 | "state": "active", | ||
162 | "vocabulary_id": null | 187 | "vocabulary_id": null | ||
163 | }, | 188 | }, | ||
164 | { | 189 | { | ||
165 | "display_name": "salt marsh", | 190 | "display_name": "salt marsh", | ||
166 | "id": "5c257f3f-a48e-47b6-a1cc-4113dc5cea33", | 191 | "id": "5c257f3f-a48e-47b6-a1cc-4113dc5cea33", | ||
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169 | "vocabulary_id": null | 194 | "vocabulary_id": null | ||
170 | } | 195 | } | ||
171 | ], | 196 | ], | ||
172 | "title": "Spatial heterogeneity of nitrogen cycling in Deepwater | 197 | "title": "Spatial heterogeneity of nitrogen cycling in Deepwater | ||
173 | Horizon-impacted salt marshes from May 2016-February 2017", | 198 | Horizon-impacted salt marshes from May 2016-February 2017", | ||
174 | "type": "dataset", | 199 | "type": "dataset", | ||
175 | "url": null, | 200 | "url": null, | ||
176 | "version": null | 201 | "version": null | ||
177 | } | 202 | } |