Changes
On July 23, 2022 at 3:03:52 AM UTC, 851c91e4-6343-45af-967a-20a33797707e:
-
Added resource 14.html to Ecosystem Services Provided by Oyster Reefs: An Experimental Assessment in Mobile Bay, Al (focus: infaunal community) - 2004-2006
f | 1 | { | f | 1 | { |
2 | "author": "Dr. Kenneth Heck", | 2 | "author": "Dr. Kenneth Heck", | ||
3 | "author_email": "kheck@disl.org", | 3 | "author_email": "kheck@disl.org", | ||
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": "Access_Constraints", | 7 | "key": "Access_Constraints", | ||
8 | "value": "Permission to access these data must be given by Dr. | 8 | "value": "Permission to access these data must be given by Dr. | ||
9 | Kenneth Heck of the Dauphin Island Sea Lab." | 9 | Kenneth Heck of the Dauphin Island Sea Lab." | ||
10 | }, | 10 | }, | ||
11 | { | 11 | { | ||
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13 | "value": "Mobile Bay, Alabama, Gulf of Mexico, Dauphin Island" | 13 | "value": "Mobile Bay, Alabama, Gulf of Mexico, Dauphin Island" | ||
14 | }, | 14 | }, | ||
15 | { | 15 | { | ||
16 | "key": "Theme Keywords", | 16 | "key": "Theme Keywords", | ||
17 | "value": "oyster, restoration, marsh creeks, | 17 | "value": "oyster, restoration, marsh creeks, | ||
18 | Before-After-Control-Impact, BACI, water clarity, nutrient dynamics, | 18 | Before-After-Control-Impact, BACI, water clarity, nutrient dynamics, | ||
19 | water-column primary production, benthic primary production, benthic | 19 | water-column primary production, benthic primary production, benthic | ||
20 | secondary production, juvenile fish, invertebrate, abundance" | 20 | secondary production, juvenile fish, invertebrate, abundance" | ||
21 | }, | 21 | }, | ||
22 | { | 22 | { | ||
23 | "key": "Use_Constraints", | 23 | "key": "Use_Constraints", | ||
24 | "value": "Acknowledgment of the DISL's Marine Ecology Lab, | 24 | "value": "Acknowledgment of the DISL's Marine Ecology Lab, | ||
25 | National Oceanic and Atmospheric Administration (NOAA) and The Alabama | 25 | National Oceanic and Atmospheric Administration (NOAA) and The Alabama | ||
26 | Center for Estuarine Studies (ACES) would be appreciated in products | 26 | Center for Estuarine Studies (ACES) would be appreciated in products | ||
27 | developed from these data, and such acknowledgment as is standard for | 27 | developed from these data, and such acknowledgment as is standard for | ||
28 | citation and legal practices for data source is expected by users of | 28 | citation and legal practices for data source is expected by users of | ||
29 | these data. Users should be aware that comparison with other data sets | 29 | these data. Users should be aware that comparison with other data sets | ||
30 | for the same area from other time periods may be inaccurate due to | 30 | for the same area from other time periods may be inaccurate due to | ||
31 | inconsistencies resulting from changes in mapping conventions, data | 31 | inconsistencies resulting from changes in mapping conventions, data | ||
32 | collection, and computer processes over time. The distributor shall | 32 | collection, and computer processes over time. The distributor shall | ||
33 | not be liable for improper or incorrect use of these data, based on | 33 | not be liable for improper or incorrect use of these data, based on | ||
34 | the description of appropriate/inappropriate uses described in the | 34 | the description of appropriate/inappropriate uses described in the | ||
35 | metadata document. These data are not legal documents and are not to | 35 | metadata document. These data are not legal documents and are not to | ||
36 | be used as such." | 36 | be used as such." | ||
37 | }, | 37 | }, | ||
38 | { | 38 | { | ||
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40 | "value": "DISL: Marine Ecology Lab" | 40 | "value": "DISL: Marine Ecology Lab" | ||
41 | }, | 41 | }, | ||
42 | { | 42 | { | ||
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44 | "value": "Mobile Bay Alabama Gulf of Mexico Dauphin Island" | 44 | "value": "Mobile Bay Alabama Gulf of Mexico Dauphin Island" | ||
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70 | { | 70 | { | ||
71 | "key": "dc.creator", | 71 | "key": "dc.creator", | ||
72 | "value": "Dauphin Island Sea Lab (DISL): Marine Ecology Lab" | 72 | "value": "Dauphin Island Sea Lab (DISL): Marine Ecology Lab" | ||
73 | }, | 73 | }, | ||
74 | { | 74 | { | ||
75 | "key": "dc.date", | 75 | "key": "dc.date", | ||
76 | "value": "20080222" | 76 | "value": "20080222" | ||
77 | }, | 77 | }, | ||
78 | { | 78 | { | ||
79 | "key": "dc.description", | 79 | "key": "dc.description", | ||
80 | "value": "The Alabama Oyster Reef Restoration Program began in | 80 | "value": "The Alabama Oyster Reef Restoration Program began in | ||
81 | 2004 to experimentally assess ecosystem benefits of oyster reef | 81 | 2004 to experimentally assess ecosystem benefits of oyster reef | ||
82 | restoration in marsh creeks in Mobile Bay, AL, USA, and document the | 82 | restoration in marsh creeks in Mobile Bay, AL, USA, and document the | ||
83 | spatial scale at which such benefits could be measured. The project | 83 | spatial scale at which such benefits could be measured. The project | ||
84 | relied on a Before-After-Control-Impact (BACI) design in which 3 pairs | 84 | relied on a Before-After-Control-Impact (BACI) design in which 3 pairs | ||
85 | of marsh creeks were monitored for 8 months prior to oyster additions, | 85 | of marsh creeks were monitored for 8 months prior to oyster additions, | ||
86 | and fifteen months after oyster reef additions. Addition of oysters to | 86 | and fifteen months after oyster reef additions. Addition of oysters to | ||
87 | one randomly selected creek of each of the three pairs resulted in | 87 | one randomly selected creek of each of the three pairs resulted in | ||
88 | densities higher than ever previously reported. We assessed whether | 88 | densities higher than ever previously reported. We assessed whether | ||
89 | oyster addition affected water clarity, nutrient dynamics, | 89 | oyster addition affected water clarity, nutrient dynamics, | ||
90 | water-column primary production, benthic primary and secondary | 90 | water-column primary production, benthic primary and secondary | ||
91 | production, and abundance of juvenile fish and invertebrates by | 91 | production, and abundance of juvenile fish and invertebrates by | ||
92 | sampling monthly or bimonthly. While there were short-lived, | 92 | sampling monthly or bimonthly. While there were short-lived, | ||
93 | small-scale increases in water clarity, there were no persistent, | 93 | small-scale increases in water clarity, there were no persistent, | ||
94 | large changes in any response variables between experimental and | 94 | large changes in any response variables between experimental and | ||
95 | control creeks. The absence of dramatic effects was likely due to a | 95 | control creeks. The absence of dramatic effects was likely due to a | ||
96 | combination of factors, including inaccurate initial assumptions, | 96 | combination of factors, including inaccurate initial assumptions, | ||
97 | between-creek variability and intense tropical storm activity. | 97 | between-creek variability and intense tropical storm activity. | ||
98 | Regardless of cause, we did not find substantial changes in water | 98 | Regardless of cause, we did not find substantial changes in water | ||
99 | clarity and biological activity in the experimental creeks. Therefore, | 99 | clarity and biological activity in the experimental creeks. Therefore, | ||
100 | we do not expect large ecosystem benefits to result from oyster | 100 | we do not expect large ecosystem benefits to result from oyster | ||
101 | restoration in other marsh creeks in the Gulf of Mexico. This is not | 101 | restoration in other marsh creeks in the Gulf of Mexico. This is not | ||
102 | to say that restoration of oyster reefs should not be carried out, | 102 | to say that restoration of oyster reefs should not be carried out, | ||
103 | especially since our oyster reef restoration was successful and | 103 | especially since our oyster reef restoration was successful and | ||
104 | functional oyster reefs offer other benefits such as enhanced | 104 | functional oyster reefs offer other benefits such as enhanced | ||
105 | benthic-pelagic coupling and denitrification through deposition of | 105 | benthic-pelagic coupling and denitrification through deposition of | ||
106 | feces onto sediments. But our findings do suggest that surrounding | 106 | feces onto sediments. But our findings do suggest that surrounding | ||
107 | landscape may play a critical role if the major goal of oyster reef | 107 | landscape may play a critical role if the major goal of oyster reef | ||
108 | restoration is to augment mobile fishes and decapod crustaceans." | 108 | restoration is to augment mobile fishes and decapod crustaceans." | ||
109 | }, | 109 | }, | ||
110 | { | 110 | { | ||
111 | "key": "dc.language", | 111 | "key": "dc.language", | ||
112 | "value": "en" | 112 | "value": "en" | ||
113 | }, | 113 | }, | ||
114 | { | 114 | { | ||
115 | "key": "dc.source", | 115 | "key": "dc.source", | ||
116 | "value": "Alabama Oyster Reef Restoration Project (core samples | 116 | "value": "Alabama Oyster Reef Restoration Project (core samples | ||
117 | of infaunal community)" | 117 | of infaunal community)" | ||
118 | }, | 118 | }, | ||
119 | { | 119 | { | ||
120 | "key": "dc.subject", | 120 | "key": "dc.subject", | ||
121 | "value": "oyster restoration marsh creeks | 121 | "value": "oyster restoration marsh creeks | ||
122 | Before-After-Control-Impact BACI water clarity nutrient dynamics | 122 | Before-After-Control-Impact BACI water clarity nutrient dynamics | ||
123 | water-column primary production benthic primary production benthic | 123 | water-column primary production benthic primary production benthic | ||
124 | secondary production juvenile fish invertebrate abundance" | 124 | secondary production juvenile fish invertebrate abundance" | ||
125 | }, | 125 | }, | ||
126 | { | 126 | { | ||
127 | "key": "dc.title", | 127 | "key": "dc.title", | ||
128 | "value": "Ecosystem Services Provided by Oyster Reefs: An | 128 | "value": "Ecosystem Services Provided by Oyster Reefs: An | ||
129 | Experimental Assessment in Mobile Bay, Al (focus: infaunal community) | 129 | Experimental Assessment in Mobile Bay, Al (focus: infaunal community) | ||
130 | - 2004-2006" | 130 | - 2004-2006" | ||
131 | }, | 131 | }, | ||
132 | { | 132 | { | ||
133 | "key": "dc.type", | 133 | "key": "dc.type", | ||
134 | "value": "spreadsheet and report" | 134 | "value": "spreadsheet and report" | ||
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153 | yster-reefs-an-experimental-assessment-in-mobile-bay-al-focus-infaun", | 153 | yster-reefs-an-experimental-assessment-in-mobile-bay-al-focus-infaun", | ||
154 | "notes": "The Alabama Oyster Reef Restoration Program began in 2004 | 154 | "notes": "The Alabama Oyster Reef Restoration Program began in 2004 | ||
155 | to experimentally assess ecosystem benefits of oyster reef restoration | 155 | to experimentally assess ecosystem benefits of oyster reef restoration | ||
156 | in marsh creeks in Mobile Bay, AL, USA, and document the spatial scale | 156 | in marsh creeks in Mobile Bay, AL, USA, and document the spatial scale | ||
157 | at which such benefits could be measured. The project relied on a | 157 | at which such benefits could be measured. The project relied on a | ||
158 | Before-After-Control-Impact (BACI) design in which 3 pairs of marsh | 158 | Before-After-Control-Impact (BACI) design in which 3 pairs of marsh | ||
159 | creeks were monitored for 8 months prior to oyster additions, and | 159 | creeks were monitored for 8 months prior to oyster additions, and | ||
160 | fifteen months after oyster reef additions. Addition of oysters to one | 160 | fifteen months after oyster reef additions. Addition of oysters to one | ||
161 | randomly selected creek of each of the three pairs resulted in | 161 | randomly selected creek of each of the three pairs resulted in | ||
162 | densities higher than ever previously reported. We assessed whether | 162 | densities higher than ever previously reported. We assessed whether | ||
163 | oyster addition affected water clarity, nutrient dynamics, | 163 | oyster addition affected water clarity, nutrient dynamics, | ||
164 | water-column primary production, benthic primary and secondary | 164 | water-column primary production, benthic primary and secondary | ||
165 | production, and abundance of juvenile fish and invertebrates by | 165 | production, and abundance of juvenile fish and invertebrates by | ||
166 | sampling monthly or bimonthly. While there were short-lived, | 166 | sampling monthly or bimonthly. While there were short-lived, | ||
167 | small-scale increases in water clarity, there were no persistent, | 167 | small-scale increases in water clarity, there were no persistent, | ||
168 | large changes in any response variables between experimental and | 168 | large changes in any response variables between experimental and | ||
169 | control creeks. The absence of dramatic effects was likely due to a | 169 | control creeks. The absence of dramatic effects was likely due to a | ||
170 | combination of factors, including inaccurate initial assumptions, | 170 | combination of factors, including inaccurate initial assumptions, | ||
171 | between-creek variability and intense tropical storm activity. | 171 | between-creek variability and intense tropical storm activity. | ||
172 | Regardless of cause, we did not find substantial changes in water | 172 | Regardless of cause, we did not find substantial changes in water | ||
173 | clarity and biological activity in the experimental creeks. Therefore, | 173 | clarity and biological activity in the experimental creeks. Therefore, | ||
174 | we do not expect large ecosystem benefits to result from oyster | 174 | we do not expect large ecosystem benefits to result from oyster | ||
175 | restoration in other marsh creeks in the Gulf of Mexico. This is not | 175 | restoration in other marsh creeks in the Gulf of Mexico. This is not | ||
176 | to say that restoration of oyster reefs should not be carried out, | 176 | to say that restoration of oyster reefs should not be carried out, | ||
177 | especially since our oyster reef restoration was successful and | 177 | especially since our oyster reef restoration was successful and | ||
178 | functional oyster reefs offer other benefits such as enhanced | 178 | functional oyster reefs offer other benefits such as enhanced | ||
179 | benthic-pelagic coupling and denitrification through deposition of | 179 | benthic-pelagic coupling and denitrification through deposition of | ||
180 | feces onto sediments. But our findings do suggest that surrounding | 180 | feces onto sediments. But our findings do suggest that surrounding | ||
181 | landscape may play a critical role if the major goal of oyster reef | 181 | landscape may play a critical role if the major goal of oyster reef | ||
182 | restoration is to augment mobile fishes and decapod crustaceans.", | 182 | restoration is to augment mobile fishes and decapod crustaceans.", | ||
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267 | { | 292 | { | ||
268 | "display_name": "invertebrate", | 293 | "display_name": "invertebrate", | ||
269 | "id": "8e80a4f5-f083-4a52-9fec-118920a2a70a", | 294 | "id": "8e80a4f5-f083-4a52-9fec-118920a2a70a", | ||
270 | "name": "invertebrate", | 295 | "name": "invertebrate", | ||
271 | "state": "active", | 296 | "state": "active", | ||
272 | "vocabulary_id": null | 297 | "vocabulary_id": null | ||
273 | }, | 298 | }, | ||
274 | { | 299 | { | ||
275 | "display_name": "juvenile fish", | 300 | "display_name": "juvenile fish", | ||
276 | "id": "4ba09c2e-e419-44fa-b7fd-76eaf416abe3", | 301 | "id": "4ba09c2e-e419-44fa-b7fd-76eaf416abe3", | ||
277 | "name": "juvenile fish", | 302 | "name": "juvenile fish", | ||
278 | "state": "active", | 303 | "state": "active", | ||
279 | "vocabulary_id": null | 304 | "vocabulary_id": null | ||
280 | }, | 305 | }, | ||
281 | { | 306 | { | ||
282 | "display_name": "marsh creeks", | 307 | "display_name": "marsh creeks", | ||
283 | "id": "7efed83b-ea16-4d9a-8b12-7f1cb5f9b8a1", | 308 | "id": "7efed83b-ea16-4d9a-8b12-7f1cb5f9b8a1", | ||
284 | "name": "marsh creeks", | 309 | "name": "marsh creeks", | ||
285 | "state": "active", | 310 | "state": "active", | ||
286 | "vocabulary_id": null | 311 | "vocabulary_id": null | ||
287 | }, | 312 | }, | ||
288 | { | 313 | { | ||
289 | "display_name": "nutrient dynamics", | 314 | "display_name": "nutrient dynamics", | ||
290 | "id": "8eb9241d-0a15-49d5-a378-3c62c90ab41b", | 315 | "id": "8eb9241d-0a15-49d5-a378-3c62c90ab41b", | ||
291 | "name": "nutrient dynamics", | 316 | "name": "nutrient dynamics", | ||
292 | "state": "active", | 317 | "state": "active", | ||
293 | "vocabulary_id": null | 318 | "vocabulary_id": null | ||
294 | }, | 319 | }, | ||
295 | { | 320 | { | ||
296 | "display_name": "oyster", | 321 | "display_name": "oyster", | ||
297 | "id": "96bdc8b5-c49b-42ca-8fa4-789a20a5963e", | 322 | "id": "96bdc8b5-c49b-42ca-8fa4-789a20a5963e", | ||
298 | "name": "oyster", | 323 | "name": "oyster", | ||
299 | "state": "active", | 324 | "state": "active", | ||
300 | "vocabulary_id": null | 325 | "vocabulary_id": null | ||
301 | }, | 326 | }, | ||
302 | { | 327 | { | ||
303 | "display_name": "restoration", | 328 | "display_name": "restoration", | ||
304 | "id": "db8b6627-d3b5-465b-a953-bd64f302661d", | 329 | "id": "db8b6627-d3b5-465b-a953-bd64f302661d", | ||
305 | "name": "restoration", | 330 | "name": "restoration", | ||
306 | "state": "active", | 331 | "state": "active", | ||
307 | "vocabulary_id": null | 332 | "vocabulary_id": null | ||
308 | }, | 333 | }, | ||
309 | { | 334 | { | ||
310 | "display_name": "water clarity", | 335 | "display_name": "water clarity", | ||
311 | "id": "5fe6e27a-741d-41d2-a685-557eb018b747", | 336 | "id": "5fe6e27a-741d-41d2-a685-557eb018b747", | ||
312 | "name": "water clarity", | 337 | "name": "water clarity", | ||
313 | "state": "active", | 338 | "state": "active", | ||
314 | "vocabulary_id": null | 339 | "vocabulary_id": null | ||
315 | }, | 340 | }, | ||
316 | { | 341 | { | ||
317 | "display_name": "water-column primary production", | 342 | "display_name": "water-column primary production", | ||
318 | "id": "579341ec-48ce-46b6-bf7f-6a90a6fddf37", | 343 | "id": "579341ec-48ce-46b6-bf7f-6a90a6fddf37", | ||
319 | "name": "water-column primary production", | 344 | "name": "water-column primary production", | ||
320 | "state": "active", | 345 | "state": "active", | ||
321 | "vocabulary_id": null | 346 | "vocabulary_id": null | ||
322 | } | 347 | } | ||
323 | ], | 348 | ], | ||
324 | "title": "Ecosystem Services Provided by Oyster Reefs: An | 349 | "title": "Ecosystem Services Provided by Oyster Reefs: An | ||
325 | Experimental Assessment in Mobile Bay, Al (focus: infaunal community) | 350 | Experimental Assessment in Mobile Bay, Al (focus: infaunal community) | ||
326 | - 2004-2006", | 351 | - 2004-2006", | ||
327 | "type": "dataset", | 352 | "type": "dataset", | ||
328 | "url": null, | 353 | "url": null, | ||
329 | "version": null | 354 | "version": null | ||
330 | } | 355 | } |