Changes
On July 23, 2022 at 3:05:01 AM UTC, 851c91e4-6343-45af-967a-20a33797707e:
-
Added resource 56.html to Habitat loss and interspecific competition shape coral reef ecosystem processes
f | 1 | { | f | 1 | { |
2 | "author": "Dr. John Valentine or Nathan Lemoine", | 2 | "author": "Dr. John Valentine or Nathan Lemoine", | ||
3 | "author_email": "jvalentine@disl.org", | 3 | "author_email": "jvalentine@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 | John Valentine or Nathan Lemoine of the Dauphin Island Sea Lab." | 9 | John Valentine or Nathan Lemoine of the Dauphin Island Sea Lab." | ||
10 | }, | 10 | }, | ||
11 | { | 11 | { | ||
12 | "key": "ISO 19115 Topic Categories", | 12 | "key": "ISO 19115 Topic Categories", | ||
13 | "value": "biota, 002, environment, 007, oceans, 014" | 13 | "value": "biota, 002, environment, 007, oceans, 014" | ||
14 | }, | 14 | }, | ||
15 | { | 15 | { | ||
16 | "key": "Place Keywords", | 16 | "key": "Place Keywords", | ||
17 | "value": "Florida, United States of America, Florida Keys | 17 | "value": "Florida, United States of America, Florida Keys | ||
18 | National Marine Sanctuary, Grecian Rocks, North Dry Rocks, Horseshoe | 18 | National Marine Sanctuary, Grecian Rocks, North Dry Rocks, Horseshoe | ||
19 | Reef, Dauphin Island Sea Lab" | 19 | Reef, Dauphin Island Sea Lab" | ||
20 | }, | 20 | }, | ||
21 | { | 21 | { | ||
22 | "key": "Theme Keywords", | 22 | "key": "Theme Keywords", | ||
23 | "value": "habitat loss, coral, reefs, ecosystem, competition, | 23 | "value": "habitat loss, coral, reefs, ecosystem, competition, | ||
24 | fish, fish assemblages, coral mortality, degradation, trophic | 24 | fish, fish assemblages, coral mortality, degradation, trophic | ||
25 | interactions, richness, abundance, grazing, predation, herbivory, | 25 | interactions, richness, abundance, grazing, predation, herbivory, | ||
26 | artificial coral, damselfish" | 26 | artificial coral, damselfish" | ||
27 | }, | 27 | }, | ||
28 | { | 28 | { | ||
29 | "key": "Use_Constraints", | 29 | "key": "Use_Constraints", | ||
30 | "value": "Acknowledgment of the DISL: Valentine Lab and the | 30 | "value": "Acknowledgment of the DISL: Valentine Lab and the | ||
31 | NOAA/UNC Wilmington Coral Reef Conservation grant would be appreciated | 31 | NOAA/UNC Wilmington Coral Reef Conservation grant would be appreciated | ||
32 | in products developed from these data, and such acknowledgment as is | 32 | in products developed from these data, and such acknowledgment as is | ||
33 | standard for citation and legal practices for data source is expected | 33 | standard for citation and legal practices for data source is expected | ||
34 | by users of these data. Users should be aware that comparison with | 34 | by users of these data. Users should be aware that comparison with | ||
35 | other data sets for the same area from other time periods may be | 35 | other data sets for the same area from other time periods may be | ||
36 | inaccurate due to inconsistencies resulting from changes in mapping | 36 | inaccurate due to inconsistencies resulting from changes in mapping | ||
37 | conventions, data collection, and computer processes over time. The | 37 | conventions, data collection, and computer processes over time. The | ||
38 | distributor shall not be liable for improper or incorrect use of these | 38 | distributor shall not be liable for improper or incorrect use of these | ||
39 | data, based on the description of appropriate/inappropriate uses | 39 | data, based on the description of appropriate/inappropriate uses | ||
40 | described in the metadata document. These data are not legal documents | 40 | described in the metadata document. These data are not legal documents | ||
41 | and are not to be used as such." | 41 | and are not to be used as such." | ||
42 | }, | 42 | }, | ||
43 | { | 43 | { | ||
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45 | "value": "Florida United States of America Florida Keys National | 45 | "value": "Florida United States of America Florida Keys National | ||
46 | Marine Sanctuary Grecian Rocks North Dry Rocks Horseshoe Reef Dauphin | 46 | Marine Sanctuary Grecian Rocks North Dry Rocks Horseshoe Reef Dauphin | ||
47 | Island Sea Lab" | 47 | Island Sea Lab" | ||
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75 | "value": "Dauphin Island Sea Lab: Valentine Lab" | 75 | "value": "Dauphin Island Sea Lab: Valentine Lab" | ||
76 | }, | 76 | }, | ||
77 | { | 77 | { | ||
78 | "key": "dc.date", | 78 | "key": "dc.date", | ||
79 | "value": "Unpublished material" | 79 | "value": "Unpublished material" | ||
80 | }, | 80 | }, | ||
81 | { | 81 | { | ||
82 | "key": "dc.description", | 82 | "key": "dc.description", | ||
83 | "value": "Despite contrasting views on the impacts of loss of | 83 | "value": "Despite contrasting views on the impacts of loss of | ||
84 | live coral cover and habitat complexity on reef fishes, experimental | 84 | live coral cover and habitat complexity on reef fishes, experimental | ||
85 | studies designed to assess the relative impacts of these two factors | 85 | studies designed to assess the relative impacts of these two factors | ||
86 | have not been conducted (Pratchett et al., 2008). Lirman (1999) used a | 86 | have not been conducted (Pratchett et al., 2008). Lirman (1999) used a | ||
87 | mensurative experiment to analyze the impacts of coral mortality and | 87 | mensurative experiment to analyze the impacts of coral mortality and | ||
88 | structural degradation, via comparisons of reef fish assemblages on | 88 | structural degradation, via comparisons of reef fish assemblages on | ||
89 | live and dead A. palmata colonies. His results suggest that loss of | 89 | live and dead A. palmata colonies. His results suggest that loss of | ||
90 | structure provided by A. palmata plays a more important role than loss | 90 | structure provided by A. palmata plays a more important role than loss | ||
91 | of living tissue in determining fish assemblage composition, although | 91 | of living tissue in determining fish assemblage composition, although | ||
92 | the distribution of a number of specialists was related to the | 92 | the distribution of a number of specialists was related to the | ||
93 | presence of live coral tissue. However, mensurative experiments are | 93 | presence of live coral tissue. However, mensurative experiments are | ||
94 | prone to confounding factors and can only correlate measurements. The | 94 | prone to confounding factors and can only correlate measurements. The | ||
95 | lack of manipulative experiments has inhibited researchers from | 95 | lack of manipulative experiments has inhibited researchers from | ||
96 | properly assessing relative importance of live coral cover and | 96 | properly assessing relative importance of live coral cover and | ||
97 | structural complexity. Thus, the objective of this study was to | 97 | structural complexity. Thus, the objective of this study was to | ||
98 | determine how coral biodiversity loss affects coral reef ecosystem | 98 | determine how coral biodiversity loss affects coral reef ecosystem | ||
99 | processes, using a series of manipulative and mensurative experiments | 99 | processes, using a series of manipulative and mensurative experiments | ||
100 | designed to answer three specific questions: 1) How does coral | 100 | designed to answer three specific questions: 1) How does coral | ||
101 | biodiversity loss affect habitat availability? Since the densities of | 101 | biodiversity loss affect habitat availability? Since the densities of | ||
102 | multiple coral species have simultaneously declined (Green et al., | 102 | multiple coral species have simultaneously declined (Green et al., | ||
103 | 2008), and the impacts of such cumulative losses on habitat complexity | 103 | 2008), and the impacts of such cumulative losses on habitat complexity | ||
104 | are uncertain, the first experiment quantitatively assesses the | 104 | are uncertain, the first experiment quantitatively assesses the | ||
105 | impacts of coral species richness and identity on reef rugosity using | 105 | impacts of coral species richness and identity on reef rugosity using | ||
106 | both mensurative and manipulative methods. I also investigated the | 106 | both mensurative and manipulative methods. I also investigated the | ||
107 | impacts of coral biodiversity loss on several fish community metrics, | 107 | impacts of coral biodiversity loss on several fish community metrics, | ||
108 | including species richness and overall abundance, in order to assess | 108 | including species richness and overall abundance, in order to assess | ||
109 | the appropriate measure of habitat quality for coral reef fishes. 2) | 109 | the appropriate measure of habitat quality for coral reef fishes. 2) | ||
110 | How does loss of live coral and structure influence fish assemblages? | 110 | How does loss of live coral and structure influence fish assemblages? | ||
111 | I used mensurative survey techniques and experimental manipulations to | 111 | I used mensurative survey techniques and experimental manipulations to | ||
112 | determine the individual effects of both live coral loss and | 112 | determine the individual effects of both live coral loss and | ||
113 | three-dimensional structure on reef fish assemblages. Experimental | 113 | three-dimensional structure on reef fish assemblages. Experimental | ||
114 | plots were created using artificial A. palmata mimics to reconstruct | 114 | plots were created using artificial A. palmata mimics to reconstruct | ||
115 | exact reef shapes, as opposed to cinder blocks, which are proven to be | 115 | exact reef shapes, as opposed to cinder blocks, which are proven to be | ||
116 | ecologically irrelevant approximations of rugosity (Kroutil, 2005). 3) | 116 | ecologically irrelevant approximations of rugosity (Kroutil, 2005). 3) | ||
117 | What are the responses, and the causal mechanisms, of trophic | 117 | What are the responses, and the causal mechanisms, of trophic | ||
118 | interactions to habitat loss? To determine how ecosystem processes, | 118 | interactions to habitat loss? To determine how ecosystem processes, | ||
119 | i.e. grazing and predation, are affected by habitat loss, and the | 119 | i.e. grazing and predation, are affected by habitat loss, and the | ||
120 | spatial extent to which trophic interactions have been affected, | 120 | spatial extent to which trophic interactions have been affected, | ||
121 | processes were measured in `Complex' A. palmata stands, simple sites | 121 | processes were measured in `Complex' A. palmata stands, simple sites | ||
122 | adjacent to (`Near') and removed from (`Far') structurally complex | 122 | adjacent to (`Near') and removed from (`Far') structurally complex | ||
123 | sites , and within experimentally recreated `Current' habitats using | 123 | sites , and within experimentally recreated `Current' habitats using | ||
124 | established tethering techniques (Valentine et al., 2007, 2008; Eklof | 124 | established tethering techniques (Valentine et al., 2007, 2008; Eklof | ||
125 | et al., 2009). The `Current' sites were constructed to mimic the | 125 | et al., 2009). The `Current' sites were constructed to mimic the | ||
126 | current state of isolated, non-living A. palmata skeletons that | 126 | current state of isolated, non-living A. palmata skeletons that | ||
127 | currently characterize Caribbean reefs." | 127 | currently characterize Caribbean reefs." | ||
128 | }, | 128 | }, | ||
129 | { | 129 | { | ||
130 | "key": "dc.language", | 130 | "key": "dc.language", | ||
131 | "value": "en" | 131 | "value": "en" | ||
132 | }, | 132 | }, | ||
133 | { | 133 | { | ||
134 | "key": "dc.subject", | 134 | "key": "dc.subject", | ||
135 | "value": "habitat loss coral reefs ecosystem competition fish | 135 | "value": "habitat loss coral reefs ecosystem competition fish | ||
136 | fish assemblages coral mortality degradation trophic interactions | 136 | fish assemblages coral mortality degradation trophic interactions | ||
137 | richness abundance grazing predation herbivory artificial coral | 137 | richness abundance grazing predation herbivory artificial coral | ||
138 | damselfish" | 138 | damselfish" | ||
139 | }, | 139 | }, | ||
140 | { | 140 | { | ||
141 | "key": "dc.title", | 141 | "key": "dc.title", | ||
142 | "value": "Habitat loss and interspecific competition shape coral | 142 | "value": "Habitat loss and interspecific competition shape coral | ||
143 | reef ecosystem processes" | 143 | reef ecosystem processes" | ||
144 | }, | 144 | }, | ||
145 | { | 145 | { | ||
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167 | "notes": "Despite contrasting views on the impacts of loss of live | 167 | "notes": "Despite contrasting views on the impacts of loss of live | ||
168 | coral cover and habitat complexity on reef fishes, experimental | 168 | coral cover and habitat complexity on reef fishes, experimental | ||
169 | studies designed to assess the relative impacts of these two factors | 169 | studies designed to assess the relative impacts of these two factors | ||
170 | have not been conducted (Pratchett et al., 2008). Lirman (1999) used a | 170 | have not been conducted (Pratchett et al., 2008). Lirman (1999) used a | ||
171 | mensurative experiment to analyze the impacts of coral mortality and | 171 | mensurative experiment to analyze the impacts of coral mortality and | ||
172 | structural degradation, via comparisons of reef fish assemblages on | 172 | structural degradation, via comparisons of reef fish assemblages on | ||
173 | live and dead A. palmata colonies. His results suggest that loss of | 173 | live and dead A. palmata colonies. His results suggest that loss of | ||
174 | structure provided by A. palmata plays a more important role than loss | 174 | structure provided by A. palmata plays a more important role than loss | ||
175 | of living tissue in determining fish assemblage composition, although | 175 | of living tissue in determining fish assemblage composition, although | ||
176 | the distribution of a number of specialists was related to the | 176 | the distribution of a number of specialists was related to the | ||
177 | presence of live coral tissue. However, mensurative experiments are | 177 | presence of live coral tissue. However, mensurative experiments are | ||
178 | prone to confounding factors and can only correlate measurements. The | 178 | prone to confounding factors and can only correlate measurements. The | ||
179 | lack of manipulative experiments has inhibited researchers from | 179 | lack of manipulative experiments has inhibited researchers from | ||
180 | properly assessing relative importance of live coral cover and | 180 | properly assessing relative importance of live coral cover and | ||
181 | structural complexity. Thus, the objective of this study was to | 181 | structural complexity. Thus, the objective of this study was to | ||
182 | determine how coral biodiversity loss affects coral reef ecosystem | 182 | determine how coral biodiversity loss affects coral reef ecosystem | ||
183 | processes, using a series of manipulative and mensurative experiments | 183 | processes, using a series of manipulative and mensurative experiments | ||
184 | designed to answer three specific questions: 1) How does coral | 184 | designed to answer three specific questions: 1) How does coral | ||
185 | biodiversity loss affect habitat availability? Since the densities of | 185 | biodiversity loss affect habitat availability? Since the densities of | ||
186 | multiple coral species have simultaneously declined (Green et al., | 186 | multiple coral species have simultaneously declined (Green et al., | ||
187 | 2008), and the impacts of such cumulative losses on habitat complexity | 187 | 2008), and the impacts of such cumulative losses on habitat complexity | ||
188 | are uncertain, the first experiment quantitatively assesses the | 188 | are uncertain, the first experiment quantitatively assesses the | ||
189 | impacts of coral species richness and identity on reef rugosity using | 189 | impacts of coral species richness and identity on reef rugosity using | ||
190 | both mensurative and manipulative methods. I also investigated the | 190 | both mensurative and manipulative methods. I also investigated the | ||
191 | impacts of coral biodiversity loss on several fish community metrics, | 191 | impacts of coral biodiversity loss on several fish community metrics, | ||
192 | including species richness and overall abundance, in order to assess | 192 | including species richness and overall abundance, in order to assess | ||
193 | the appropriate measure of habitat quality for coral reef fishes. 2) | 193 | the appropriate measure of habitat quality for coral reef fishes. 2) | ||
194 | How does loss of live coral and structure influence fish assemblages? | 194 | How does loss of live coral and structure influence fish assemblages? | ||
195 | I used mensurative survey techniques and experimental manipulations to | 195 | I used mensurative survey techniques and experimental manipulations to | ||
196 | determine the individual effects of both live coral loss and | 196 | determine the individual effects of both live coral loss and | ||
197 | three-dimensional structure on reef fish assemblages. Experimental | 197 | three-dimensional structure on reef fish assemblages. Experimental | ||
198 | plots were created using artificial A. palmata mimics to reconstruct | 198 | plots were created using artificial A. palmata mimics to reconstruct | ||
199 | exact reef shapes, as opposed to cinder blocks, which are proven to be | 199 | exact reef shapes, as opposed to cinder blocks, which are proven to be | ||
200 | ecologically irrelevant approximations of rugosity (Kroutil, 2005). 3) | 200 | ecologically irrelevant approximations of rugosity (Kroutil, 2005). 3) | ||
201 | What are the responses, and the causal mechanisms, of trophic | 201 | What are the responses, and the causal mechanisms, of trophic | ||
202 | interactions to habitat loss? To determine how ecosystem processes, | 202 | interactions to habitat loss? To determine how ecosystem processes, | ||
203 | i.e. grazing and predation, are affected by habitat loss, and the | 203 | i.e. grazing and predation, are affected by habitat loss, and the | ||
204 | spatial extent to which trophic interactions have been affected, | 204 | spatial extent to which trophic interactions have been affected, | ||
205 | processes were measured in `Complex' A. palmata stands, simple sites | 205 | processes were measured in `Complex' A. palmata stands, simple sites | ||
206 | adjacent to (`Near') and removed from (`Far') structurally complex | 206 | adjacent to (`Near') and removed from (`Far') structurally complex | ||
207 | sites , and within experimentally recreated `Current' habitats using | 207 | sites , and within experimentally recreated `Current' habitats using | ||
208 | established tethering techniques (Valentine et al., 2007, 2008; Eklof | 208 | established tethering techniques (Valentine et al., 2007, 2008; Eklof | ||
209 | et al., 2009). The `Current' sites were constructed to mimic the | 209 | et al., 2009). The `Current' sites were constructed to mimic the | ||
210 | current state of isolated, non-living A. palmata skeletons that | 210 | current state of isolated, non-living A. palmata skeletons that | ||
211 | currently characterize Caribbean reefs.", | 211 | currently characterize Caribbean reefs.", | ||
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266 | "vocabulary_id": null | 291 | "vocabulary_id": null | ||
267 | }, | 292 | }, | ||
268 | { | 293 | { | ||
269 | "display_name": "Florida Keys National Marine Sanctuary", | 294 | "display_name": "Florida Keys National Marine Sanctuary", | ||
270 | "id": "6778d5ee-d067-4906-8964-14be2aaa859c", | 295 | "id": "6778d5ee-d067-4906-8964-14be2aaa859c", | ||
271 | "name": "Florida Keys National Marine Sanctuary", | 296 | "name": "Florida Keys National Marine Sanctuary", | ||
272 | "state": "active", | 297 | "state": "active", | ||
273 | "vocabulary_id": null | 298 | "vocabulary_id": null | ||
274 | }, | 299 | }, | ||
275 | { | 300 | { | ||
276 | "display_name": "Grecian Rocks", | 301 | "display_name": "Grecian Rocks", | ||
277 | "id": "d240f8a3-8fe6-448f-a128-d5e0ac6086e4", | 302 | "id": "d240f8a3-8fe6-448f-a128-d5e0ac6086e4", | ||
278 | "name": "Grecian Rocks", | 303 | "name": "Grecian Rocks", | ||
279 | "state": "active", | 304 | "state": "active", | ||
280 | "vocabulary_id": null | 305 | "vocabulary_id": null | ||
281 | }, | 306 | }, | ||
282 | { | 307 | { | ||
283 | "display_name": "Horseshoe Reef", | 308 | "display_name": "Horseshoe Reef", | ||
284 | "id": "7adef59e-d84d-4e3e-a35a-bbc50b4bedc0", | 309 | "id": "7adef59e-d84d-4e3e-a35a-bbc50b4bedc0", | ||
285 | "name": "Horseshoe Reef", | 310 | "name": "Horseshoe Reef", | ||
286 | "state": "active", | 311 | "state": "active", | ||
287 | "vocabulary_id": null | 312 | "vocabulary_id": null | ||
288 | }, | 313 | }, | ||
289 | { | 314 | { | ||
290 | "display_name": "North Dry Rocks", | 315 | "display_name": "North Dry Rocks", | ||
291 | "id": "1ee92156-afef-4f57-b30d-7b9c18a4502c", | 316 | "id": "1ee92156-afef-4f57-b30d-7b9c18a4502c", | ||
292 | "name": "North Dry Rocks", | 317 | "name": "North Dry Rocks", | ||
293 | "state": "active", | 318 | "state": "active", | ||
294 | "vocabulary_id": null | 319 | "vocabulary_id": null | ||
295 | }, | 320 | }, | ||
296 | { | 321 | { | ||
297 | "display_name": "United States of America", | 322 | "display_name": "United States of America", | ||
298 | "id": "4561f069-ad2a-4d73-b810-100c08ac299b", | 323 | "id": "4561f069-ad2a-4d73-b810-100c08ac299b", | ||
299 | "name": "United States of America", | 324 | "name": "United States of America", | ||
300 | "state": "active", | 325 | "state": "active", | ||
301 | "vocabulary_id": null | 326 | "vocabulary_id": null | ||
302 | }, | 327 | }, | ||
303 | { | 328 | { | ||
304 | "display_name": "abundance", | 329 | "display_name": "abundance", | ||
305 | "id": "e78b3f21-7bf4-41ec-a631-1ec44b5a4a77", | 330 | "id": "e78b3f21-7bf4-41ec-a631-1ec44b5a4a77", | ||
306 | "name": "abundance", | 331 | "name": "abundance", | ||
307 | "state": "active", | 332 | "state": "active", | ||
308 | "vocabulary_id": null | 333 | "vocabulary_id": null | ||
309 | }, | 334 | }, | ||
310 | { | 335 | { | ||
311 | "display_name": "artificial coral", | 336 | "display_name": "artificial coral", | ||
312 | "id": "65a5e099-2b51-4dad-b4ad-b7212d5ccd71", | 337 | "id": "65a5e099-2b51-4dad-b4ad-b7212d5ccd71", | ||
313 | "name": "artificial coral", | 338 | "name": "artificial coral", | ||
314 | "state": "active", | 339 | "state": "active", | ||
315 | "vocabulary_id": null | 340 | "vocabulary_id": null | ||
316 | }, | 341 | }, | ||
317 | { | 342 | { | ||
318 | "display_name": "biota", | 343 | "display_name": "biota", | ||
319 | "id": "8697f957-08f7-4539-8025-fcb58cb28994", | 344 | "id": "8697f957-08f7-4539-8025-fcb58cb28994", | ||
320 | "name": "biota", | 345 | "name": "biota", | ||
321 | "state": "active", | 346 | "state": "active", | ||
322 | "vocabulary_id": null | 347 | "vocabulary_id": null | ||
323 | }, | 348 | }, | ||
324 | { | 349 | { | ||
325 | "display_name": "competition", | 350 | "display_name": "competition", | ||
326 | "id": "5053bcae-86b0-48cd-b4cb-59a35eb6aa23", | 351 | "id": "5053bcae-86b0-48cd-b4cb-59a35eb6aa23", | ||
327 | "name": "competition", | 352 | "name": "competition", | ||
328 | "state": "active", | 353 | "state": "active", | ||
329 | "vocabulary_id": null | 354 | "vocabulary_id": null | ||
330 | }, | 355 | }, | ||
331 | { | 356 | { | ||
332 | "display_name": "coral", | 357 | "display_name": "coral", | ||
333 | "id": "23b90ea1-e667-4537-9b2e-3e1c4e47944a", | 358 | "id": "23b90ea1-e667-4537-9b2e-3e1c4e47944a", | ||
334 | "name": "coral", | 359 | "name": "coral", | ||
335 | "state": "active", | 360 | "state": "active", | ||
336 | "vocabulary_id": null | 361 | "vocabulary_id": null | ||
337 | }, | 362 | }, | ||
338 | { | 363 | { | ||
339 | "display_name": "coral mortality", | 364 | "display_name": "coral mortality", | ||
340 | "id": "ed8b9b3a-87ee-4f85-b8b0-af99f5fa9ff9", | 365 | "id": "ed8b9b3a-87ee-4f85-b8b0-af99f5fa9ff9", | ||
341 | "name": "coral mortality", | 366 | "name": "coral mortality", | ||
342 | "state": "active", | 367 | "state": "active", | ||
343 | "vocabulary_id": null | 368 | "vocabulary_id": null | ||
344 | }, | 369 | }, | ||
345 | { | 370 | { | ||
346 | "display_name": "damselfish", | 371 | "display_name": "damselfish", | ||
347 | "id": "ae00ab95-013b-4b59-8ccb-6ebf62fec651", | 372 | "id": "ae00ab95-013b-4b59-8ccb-6ebf62fec651", | ||
348 | "name": "damselfish", | 373 | "name": "damselfish", | ||
349 | "state": "active", | 374 | "state": "active", | ||
350 | "vocabulary_id": null | 375 | "vocabulary_id": null | ||
351 | }, | 376 | }, | ||
352 | { | 377 | { | ||
353 | "display_name": "degradation", | 378 | "display_name": "degradation", | ||
354 | "id": "615fc543-17f2-4271-aada-dad028795317", | 379 | "id": "615fc543-17f2-4271-aada-dad028795317", | ||
355 | "name": "degradation", | 380 | "name": "degradation", | ||
356 | "state": "active", | 381 | "state": "active", | ||
357 | "vocabulary_id": null | 382 | "vocabulary_id": null | ||
358 | }, | 383 | }, | ||
359 | { | 384 | { | ||
360 | "display_name": "ecosystem", | 385 | "display_name": "ecosystem", | ||
361 | "id": "0542feec-3066-48f4-8168-c62fcfe2f406", | 386 | "id": "0542feec-3066-48f4-8168-c62fcfe2f406", | ||
362 | "name": "ecosystem", | 387 | "name": "ecosystem", | ||
363 | "state": "active", | 388 | "state": "active", | ||
364 | "vocabulary_id": null | 389 | "vocabulary_id": null | ||
365 | }, | 390 | }, | ||
366 | { | 391 | { | ||
367 | "display_name": "environment", | 392 | "display_name": "environment", | ||
368 | "id": "c1a667ee-c399-4f70-a7cb-449fb05391a4", | 393 | "id": "c1a667ee-c399-4f70-a7cb-449fb05391a4", | ||
369 | "name": "environment", | 394 | "name": "environment", | ||
370 | "state": "active", | 395 | "state": "active", | ||
371 | "vocabulary_id": null | 396 | "vocabulary_id": null | ||
372 | }, | 397 | }, | ||
373 | { | 398 | { | ||
374 | "display_name": "fish", | 399 | "display_name": "fish", | ||
375 | "id": "c82aa021-b238-4ccc-9cea-75d6e2ec19eb", | 400 | "id": "c82aa021-b238-4ccc-9cea-75d6e2ec19eb", | ||
376 | "name": "fish", | 401 | "name": "fish", | ||
377 | "state": "active", | 402 | "state": "active", | ||
378 | "vocabulary_id": null | 403 | "vocabulary_id": null | ||
379 | }, | 404 | }, | ||
380 | { | 405 | { | ||
381 | "display_name": "fish assemblages", | 406 | "display_name": "fish assemblages", | ||
382 | "id": "95d61d0d-941a-4c71-825d-252e6ba701cc", | 407 | "id": "95d61d0d-941a-4c71-825d-252e6ba701cc", | ||
383 | "name": "fish assemblages", | 408 | "name": "fish assemblages", | ||
384 | "state": "active", | 409 | "state": "active", | ||
385 | "vocabulary_id": null | 410 | "vocabulary_id": null | ||
386 | }, | 411 | }, | ||
387 | { | 412 | { | ||
388 | "display_name": "grazing", | 413 | "display_name": "grazing", | ||
389 | "id": "d67d1c84-6168-40b5-8cb2-1956ce38fd90", | 414 | "id": "d67d1c84-6168-40b5-8cb2-1956ce38fd90", | ||
390 | "name": "grazing", | 415 | "name": "grazing", | ||
391 | "state": "active", | 416 | "state": "active", | ||
392 | "vocabulary_id": null | 417 | "vocabulary_id": null | ||
393 | }, | 418 | }, | ||
394 | { | 419 | { | ||
395 | "display_name": "habitat loss", | 420 | "display_name": "habitat loss", | ||
396 | "id": "24b7ffa0-91f1-4d55-b402-71cfea2b157f", | 421 | "id": "24b7ffa0-91f1-4d55-b402-71cfea2b157f", | ||
397 | "name": "habitat loss", | 422 | "name": "habitat loss", | ||
398 | "state": "active", | 423 | "state": "active", | ||
399 | "vocabulary_id": null | 424 | "vocabulary_id": null | ||
400 | }, | 425 | }, | ||
401 | { | 426 | { | ||
402 | "display_name": "herbivory", | 427 | "display_name": "herbivory", | ||
403 | "id": "5a306f68-de3a-47a3-bcd2-a1ec732b4210", | 428 | "id": "5a306f68-de3a-47a3-bcd2-a1ec732b4210", | ||
404 | "name": "herbivory", | 429 | "name": "herbivory", | ||
405 | "state": "active", | 430 | "state": "active", | ||
406 | "vocabulary_id": null | 431 | "vocabulary_id": null | ||
407 | }, | 432 | }, | ||
408 | { | 433 | { | ||
409 | "display_name": "oceans", | 434 | "display_name": "oceans", | ||
410 | "id": "a6963a6f-1b79-4724-a263-d5f1bebec382", | 435 | "id": "a6963a6f-1b79-4724-a263-d5f1bebec382", | ||
411 | "name": "oceans", | 436 | "name": "oceans", | ||
412 | "state": "active", | 437 | "state": "active", | ||
413 | "vocabulary_id": null | 438 | "vocabulary_id": null | ||
414 | }, | 439 | }, | ||
415 | { | 440 | { | ||
416 | "display_name": "predation", | 441 | "display_name": "predation", | ||
417 | "id": "aa090027-2f68-46a2-abdc-d280af70487e", | 442 | "id": "aa090027-2f68-46a2-abdc-d280af70487e", | ||
418 | "name": "predation", | 443 | "name": "predation", | ||
419 | "state": "active", | 444 | "state": "active", | ||
420 | "vocabulary_id": null | 445 | "vocabulary_id": null | ||
421 | }, | 446 | }, | ||
422 | { | 447 | { | ||
423 | "display_name": "reefs", | 448 | "display_name": "reefs", | ||
424 | "id": "7964a0ab-6ac5-4f36-8aa2-5de96baaa975", | 449 | "id": "7964a0ab-6ac5-4f36-8aa2-5de96baaa975", | ||
425 | "name": "reefs", | 450 | "name": "reefs", | ||
426 | "state": "active", | 451 | "state": "active", | ||
427 | "vocabulary_id": null | 452 | "vocabulary_id": null | ||
428 | }, | 453 | }, | ||
429 | { | 454 | { | ||
430 | "display_name": "richness", | 455 | "display_name": "richness", | ||
431 | "id": "57e08381-7aff-43a7-b871-2a596dc6c116", | 456 | "id": "57e08381-7aff-43a7-b871-2a596dc6c116", | ||
432 | "name": "richness", | 457 | "name": "richness", | ||
433 | "state": "active", | 458 | "state": "active", | ||
434 | "vocabulary_id": null | 459 | "vocabulary_id": null | ||
435 | }, | 460 | }, | ||
436 | { | 461 | { | ||
437 | "display_name": "trophic interactions", | 462 | "display_name": "trophic interactions", | ||
438 | "id": "8e750f8e-7373-451f-a53d-7e3f5aa74fdd", | 463 | "id": "8e750f8e-7373-451f-a53d-7e3f5aa74fdd", | ||
439 | "name": "trophic interactions", | 464 | "name": "trophic interactions", | ||
440 | "state": "active", | 465 | "state": "active", | ||
441 | "vocabulary_id": null | 466 | "vocabulary_id": null | ||
442 | } | 467 | } | ||
443 | ], | 468 | ], | ||
444 | "title": "Habitat loss and interspecific competition shape coral | 469 | "title": "Habitat loss and interspecific competition shape coral | ||
445 | reef ecosystem processes", | 470 | reef ecosystem processes", | ||
446 | "type": "dataset", | 471 | "type": "dataset", | ||
447 | "url": null, | 472 | "url": null, | ||
448 | "version": null | 473 | "version": null | ||
449 | } | 474 | } |