Changes
On July 27, 2022 at 2:34:48 PM UTC, 851c91e4-6343-45af-967a-20a33797707e:
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Added resource potential_denitrification_rate_Chandeleur_201507_201602.csv to Potential denitrification rates in moderately oiled marshes at the Chandeleur Island, July 2015 to February 2016
f | 1 | { | f | 1 | { |
2 | "author": "Behzad Mortazavi", | 2 | "author": "Behzad Mortazavi", | ||
3 | "author_email": "bmortazavi@ua.edu", | 3 | "author_email": "bmortazavi@ua.edu", | ||
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7 | "key": "DOI", | 7 | "key": "DOI", | ||
8 | "value": "doi:10.7266/N7GX48KH" | 8 | "value": "doi:10.7266/N7GX48KH" | ||
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, Red Fish Point, Gulf of Mexico, | 16 | "value": "Chandeleur Islands, Red Fish Point, Gulf of Mexico, | ||
17 | Louisiana" | 17 | Louisiana" | ||
18 | }, | 18 | }, | ||
19 | { | 19 | { | ||
20 | "key": "Temporal Begin", | 20 | "key": "Temporal Begin", | ||
21 | "value": "2015-07-09" | 21 | "value": "2015-07-09" | ||
22 | }, | 22 | }, | ||
23 | { | 23 | { | ||
24 | "key": "Temporal End", | 24 | "key": "Temporal End", | ||
25 | "value": "2016-02-22" | 25 | "value": "2016-02-22" | ||
26 | }, | 26 | }, | ||
27 | { | 27 | { | ||
28 | "key": "Theme Keywords", | 28 | "key": "Theme Keywords", | ||
29 | "value": "Denitrification, Nitrogen cycling, marsh sediments, | 29 | "value": "Denitrification, Nitrogen cycling, marsh sediments, | ||
30 | Marsh Habitats, Intertidal Habitats" | 30 | Marsh Habitats, Intertidal Habitats" | ||
31 | }, | 31 | }, | ||
32 | { | 32 | { | ||
33 | "key": "spatial", | 33 | "key": "spatial", | ||
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35 | -88.84119, 29.8628 ], [ -88.84119, 29.8628 ], [ -88.84119, 29.8628 ], | 35 | -88.84119, 29.8628 ], [ -88.84119, 29.8628 ], [ -88.84119, 29.8628 ], | ||
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41 | "isopen": false, | 41 | "isopen": false, | ||
42 | "license_id": null, | 42 | "license_id": null, | ||
43 | "license_title": null, | 43 | "license_title": null, | ||
44 | "maintainer": "data@disl.org", | 44 | "maintainer": "data@disl.org", | ||
45 | "maintainer_email": "data@disl.org", | 45 | "maintainer_email": "data@disl.org", | ||
46 | "metadata_created": "2022-07-27T14:34:47.374816", | 46 | "metadata_created": "2022-07-27T14:34:47.374816", | ||
n | 47 | "metadata_modified": "2022-07-27T14:34:47.833033", | n | 47 | "metadata_modified": "2022-07-27T14:34:48.283823", |
48 | "name": | 48 | "name": | ||
49 | in-moderately-oiled-marshes-at-the-chandeleur-island-july-20n7gx48kh", | 49 | in-moderately-oiled-marshes-at-the-chandeleur-island-july-20n7gx48kh", | ||
50 | "notes": "### Abstract\nThe Deepwater Horizon oil spill has | 50 | "notes": "### Abstract\nThe Deepwater Horizon oil spill has | ||
51 | contributed to significant loss of marsh vegetation. Decreased marsh | 51 | contributed to significant loss of marsh vegetation. Decreased marsh | ||
52 | vegetation habitats can lead to a reduction in organic carbon and | 52 | vegetation habitats can lead to a reduction in organic carbon and | ||
53 | other key nutrients available for microbial communities in sediments. | 53 | other key nutrients available for microbial communities in sediments. | ||
54 | Potential denitrification rates were achieved by collecting 0-2 cm and | 54 | Potential denitrification rates were achieved by collecting 0-2 cm and | ||
55 | 5-7 cm sediments in vegetated marsh and unvegetated intertidal marsh | 55 | 5-7 cm sediments in vegetated marsh and unvegetated intertidal marsh | ||
56 | habitats. Sediments were treated with and without nitrate and rates | 56 | habitats. Sediments were treated with and without nitrate and rates | ||
57 | will be determined using acetylene inhibition technique.\n\n### | 57 | will be determined using acetylene inhibition technique.\n\n### | ||
58 | Purpose\nThe purpose of this study was to measure potential | 58 | Purpose\nThe purpose of this study was to measure potential | ||
59 | denitrification rates in moderately oiled marsh and intertidal | 59 | denitrification rates in moderately oiled marsh and intertidal | ||
60 | habitats\n\n**DOI: | 60 | habitats\n\n**DOI: | ||
61 | [doi:10.7266/N7GX48KH](https://www.doi.org/10.7266/N7GX48KH)**\n\n### | 61 | [doi:10.7266/N7GX48KH](https://www.doi.org/10.7266/N7GX48KH)**\n\n### | ||
62 | Suggested Citation\nMortazavi, Behzad. 2017. Potential denitrification | 62 | Suggested Citation\nMortazavi, Behzad. 2017. Potential denitrification | ||
63 | rates in moderately oiled marshes at the Chandeleur Island, July 2015 | 63 | rates in moderately oiled marshes at the Chandeleur Island, July 2015 | ||
64 | to February 2016. Distributed by: Gulf of Mexico Research Initiative | 64 | to February 2016. Distributed by: Gulf of Mexico Research Initiative | ||
65 | Information and Data Cooperative (GRIIDC), Harte Research Institute, | 65 | Information and Data Cooperative (GRIIDC), Harte Research Institute, | ||
66 | Texas A&M University\u2013Corpus Christi. doi:10.7266/N7GX48KH\n\n### | 66 | Texas A&M University\u2013Corpus Christi. doi:10.7266/N7GX48KH\n\n### | ||
67 | Related Publication Citation\n[Hinshaw, S. E., Tatariw, C., Flournoy, | 67 | Related Publication Citation\n[Hinshaw, S. E., Tatariw, C., Flournoy, | ||
68 | N., Kleinhuizen, A., Taylor, C., Sobecky, P. A., & Mortazavi, B. | 68 | N., Kleinhuizen, A., Taylor, C., Sobecky, P. A., & Mortazavi, B. | ||
69 | (2017). Vegetation Loss Decreases Salt Marsh Denitrification Capacity: | 69 | (2017). Vegetation Loss Decreases Salt Marsh Denitrification Capacity: | ||
70 | Implications for Marsh Erosion. Environmental Science & Technology, | 70 | Implications for Marsh Erosion. Environmental Science & Technology, | ||
71 | 51(15), 8245\u20138253. | 71 | 51(15), 8245\u20138253. | ||
72 | est.7b00618\n](https://dx.doi.org/10.1021/acs.est.7b00618)\n\n**Funded | 72 | est.7b00618\n](https://dx.doi.org/10.1021/acs.est.7b00618)\n\n**Funded | ||
73 | by:** Gulf of Mexico Research Initiative (GoMRI)\n\n**Funding cycle:** | 73 | by:** Gulf of Mexico Research Initiative (GoMRI)\n\n**Funding cycle:** | ||
74 | RFP-IV\n\n**Research group:** Alabama Center for Ecological Resilience | 74 | RFP-IV\n\n**Research group:** Alabama Center for Ecological Resilience | ||
75 | (ACER)\n\n", | 75 | (ACER)\n\n", | ||
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122 | { | 147 | { | ||
123 | "display_name": "Chandeleur Islands", | 148 | "display_name": "Chandeleur Islands", | ||
124 | "id": "1187d400-d9de-4166-aca2-2e591ecf8c65", | 149 | "id": "1187d400-d9de-4166-aca2-2e591ecf8c65", | ||
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128 | }, | 153 | }, | ||
129 | { | 154 | { | ||
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134 | "vocabulary_id": null | 159 | "vocabulary_id": null | ||
135 | }, | 160 | }, | ||
136 | { | 161 | { | ||
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139 | "name": "Gulf of Mexico", | 164 | "name": "Gulf of Mexico", | ||
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141 | "vocabulary_id": null | 166 | "vocabulary_id": null | ||
142 | }, | 167 | }, | ||
143 | { | 168 | { | ||
144 | "display_name": "Intertidal Habitats", | 169 | "display_name": "Intertidal Habitats", | ||
145 | "id": "b976965d-de83-4d18-8efb-4ce9c6d8e3c8", | 170 | "id": "b976965d-de83-4d18-8efb-4ce9c6d8e3c8", | ||
146 | "name": "Intertidal Habitats", | 171 | "name": "Intertidal Habitats", | ||
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150 | { | 175 | { | ||
151 | "display_name": "Louisiana", | 176 | "display_name": "Louisiana", | ||
152 | "id": "d7699c97-9202-4624-bb36-265d2a628a57", | 177 | "id": "d7699c97-9202-4624-bb36-265d2a628a57", | ||
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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": "Marsh Habitats", | 183 | "display_name": "Marsh Habitats", | ||
159 | "id": "d7303610-1de4-4a5d-b9cc-6624d30977f7", | 184 | "id": "d7303610-1de4-4a5d-b9cc-6624d30977f7", | ||
160 | "name": "Marsh Habitats", | 185 | "name": "Marsh Habitats", | ||
161 | "state": "active", | 186 | "state": "active", | ||
162 | "vocabulary_id": null | 187 | "vocabulary_id": null | ||
163 | }, | 188 | }, | ||
164 | { | 189 | { | ||
165 | "display_name": "Nitrogen cycling", | 190 | "display_name": "Nitrogen cycling", | ||
166 | "id": "b5dfde74-d8a9-45b9-a320-d72d1b936e3f", | 191 | "id": "b5dfde74-d8a9-45b9-a320-d72d1b936e3f", | ||
167 | "name": "Nitrogen cycling", | 192 | "name": "Nitrogen cycling", | ||
168 | "state": "active", | 193 | "state": "active", | ||
169 | "vocabulary_id": null | 194 | "vocabulary_id": null | ||
170 | }, | 195 | }, | ||
171 | { | 196 | { | ||
172 | "display_name": "Red Fish Point", | 197 | "display_name": "Red Fish Point", | ||
173 | "id": "08d44b61-d616-4b27-ba1f-17381f754c34", | 198 | "id": "08d44b61-d616-4b27-ba1f-17381f754c34", | ||
174 | "name": "Red Fish Point", | 199 | "name": "Red Fish Point", | ||
175 | "state": "active", | 200 | "state": "active", | ||
176 | "vocabulary_id": null | 201 | "vocabulary_id": null | ||
177 | }, | 202 | }, | ||
178 | { | 203 | { | ||
179 | "display_name": "marsh sediments", | 204 | "display_name": "marsh sediments", | ||
180 | "id": "8c6e44e6-6168-4041-bec3-6d0adab18a6d", | 205 | "id": "8c6e44e6-6168-4041-bec3-6d0adab18a6d", | ||
181 | "name": "marsh sediments", | 206 | "name": "marsh sediments", | ||
182 | "state": "active", | 207 | "state": "active", | ||
183 | "vocabulary_id": null | 208 | "vocabulary_id": null | ||
184 | } | 209 | } | ||
185 | ], | 210 | ], | ||
186 | "title": "Potential denitrification rates in moderately oiled | 211 | "title": "Potential denitrification rates in moderately oiled | ||
187 | marshes at the Chandeleur Island, July 2015 to February 2016", | 212 | marshes at the Chandeleur Island, July 2015 to February 2016", | ||
188 | "type": "dataset", | 213 | "type": "dataset", | ||
189 | "url": null, | 214 | "url": null, | ||
190 | "version": null | 215 | "version": null | ||
191 | } | 216 | } |