Changes
On July 23, 2022 at 3:04:40 AM UTC, 851c91e4-6343-45af-967a-20a33797707e:
-
Added resource 43.html to Evaluating Success and Function of Marsh (Juncus roemerianus) Restoration (2006-2011)
f | 1 | { | f | 1 | { |
2 | "author": "Just Cebrian", | 2 | "author": "Just Cebrian", | ||
3 | "author_email": "jcebrian@disl.org", | 3 | "author_email": "jcebrian@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 | Just Cebrian or Eric Sparks of the Dauphin Island Sea Lab." | 9 | Just Cebrian or Eric Sparks 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, inlandWaters, 012, | 13 | "value": "biota, 002, environment, 007, inlandWaters, 012, | ||
14 | oceans, 014" | 14 | oceans, 014" | ||
15 | }, | 15 | }, | ||
16 | { | 16 | { | ||
17 | "key": "Place Keywords", | 17 | "key": "Place Keywords", | ||
18 | "value": "Grand Bay National Estuarine Research Reserve, NERR, | 18 | "value": "Grand Bay National Estuarine Research Reserve, NERR, | ||
19 | Grand Bay, Mississippi, Heron Bayou" | 19 | Grand Bay, Mississippi, Heron Bayou" | ||
20 | }, | 20 | }, | ||
21 | { | 21 | { | ||
22 | "key": "Theme Keywords", | 22 | "key": "Theme Keywords", | ||
23 | "value": "Juncus roemerianus, black needlerush, marsh | 23 | "value": "Juncus roemerianus, black needlerush, marsh | ||
24 | restoration, ecosystem services, morphology, physiology, colonization, | 24 | restoration, ecosystem services, morphology, physiology, colonization, | ||
25 | salt marsh, vegetation, full density restoration, half density | 25 | salt marsh, vegetation, full density restoration, half density | ||
26 | restoration, nitrogen, groundwater, nutrient filtration, NO3-, | 26 | restoration, nitrogen, groundwater, nutrient filtration, NO3-, | ||
27 | top-down effects, regulation, grazing" | 27 | top-down effects, regulation, grazing" | ||
28 | }, | 28 | }, | ||
29 | { | 29 | { | ||
30 | "key": "Use_Constraints", | 30 | "key": "Use_Constraints", | ||
31 | "value": "Acknowledgment of the DISL: Marine Ecosystems Lab, the | 31 | "value": "Acknowledgment of the DISL: Marine Ecosystems Lab, the | ||
32 | Mississippi Alabama Sea Grant and the NGI/MSU Integrated Ecosystem | 32 | Mississippi Alabama Sea Grant and the NGI/MSU Integrated Ecosystem | ||
33 | Assessment would be appreciated in products developed from these data, | 33 | Assessment would be appreciated in products developed from these data, | ||
34 | and such acknowledgment as is standard for citation and legal | 34 | and such acknowledgment as is standard for citation and legal | ||
35 | practices for data source is expected by users of these data. Users | 35 | practices for data source is expected by users of these data. Users | ||
36 | should be aware that comparison with other data sets for the same area | 36 | should be aware that comparison with other data sets for the same area | ||
37 | from other time periods may be inaccurate due to inconsistencies | 37 | from other time periods may be inaccurate due to inconsistencies | ||
38 | resulting from changes in mapping conventions, data collection, and | 38 | resulting from changes in mapping conventions, data collection, and | ||
39 | computer processes over time. The distributor shall not be liable for | 39 | computer processes over time. The distributor shall not be liable for | ||
40 | improper or incorrect use of these data, based on the description of | 40 | improper or incorrect use of these data, based on the description of | ||
41 | appropriate/inappropriate uses described in the metadata document. | 41 | appropriate/inappropriate uses described in the metadata document. | ||
42 | These data are not legal documents and are not to be used as such." | 42 | These data are not legal documents and are not to be used as such." | ||
43 | }, | 43 | }, | ||
44 | { | 44 | { | ||
45 | "key": "dc.contributor", | 45 | "key": "dc.contributor", | ||
46 | "value": "Eric Sparks" | 46 | "value": "Eric Sparks" | ||
47 | }, | 47 | }, | ||
48 | { | 48 | { | ||
49 | "key": "dc.coverage.placeName", | 49 | "key": "dc.coverage.placeName", | ||
50 | "value": "Grand Bay National Estuarine Research Reserve NERR | 50 | "value": "Grand Bay National Estuarine Research Reserve NERR | ||
51 | Grand Bay Mississippi Heron Bayou" | 51 | Grand Bay Mississippi Heron Bayou" | ||
52 | }, | 52 | }, | ||
53 | { | 53 | { | ||
54 | "key": "dc.coverage.t.max", | 54 | "key": "dc.coverage.t.max", | ||
55 | "value": "2011T" | 55 | "value": "2011T" | ||
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57 | { | 57 | { | ||
58 | "key": "dc.coverage.t.min", | 58 | "key": "dc.coverage.t.min", | ||
59 | "value": "2006T" | 59 | "value": "2006T" | ||
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77 | { | 77 | { | ||
78 | "key": "dc.creator", | 78 | "key": "dc.creator", | ||
79 | "value": "Dauphin Island Sea Lab's Ecosystems Lab" | 79 | "value": "Dauphin Island Sea Lab's Ecosystems Lab" | ||
80 | }, | 80 | }, | ||
81 | { | 81 | { | ||
82 | "key": "dc.date", | 82 | "key": "dc.date", | ||
83 | "value": "Unpublished material" | 83 | "value": "Unpublished material" | ||
84 | }, | 84 | }, | ||
85 | { | 85 | { | ||
86 | "key": "dc.description", | 86 | "key": "dc.description", | ||
87 | "value": "While many restoration efforts have been conducted, | 87 | "value": "While many restoration efforts have been conducted, | ||
88 | there have been few comparisons of relative success between different | 88 | there have been few comparisons of relative success between different | ||
89 | restoration designs, especially with J. roemerianus. Here we present | 89 | restoration designs, especially with J. roemerianus. Here we present | ||
90 | two restoration designs for evaluation, a full density restoration | 90 | two restoration designs for evaluation, a full density restoration | ||
91 | design and a half density restoration design. Full density | 91 | design and a half density restoration design. Full density | ||
92 | restorations represent the more expensive and labor intensive option. | 92 | restorations represent the more expensive and labor intensive option. | ||
93 | Several parameters will be compared between these two designs relative | 93 | Several parameters will be compared between these two designs relative | ||
94 | to the adjacent natural marsh to determine how the individual plants | 94 | to the adjacent natural marsh to determine how the individual plants | ||
95 | within these treatments perform. Several measurements have and will | 95 | within these treatments perform. Several measurements have and will | ||
96 | continue to be taken as proxies of plant health including: total shoot | 96 | continue to be taken as proxies of plant health including: total shoot | ||
97 | length, percent living tissue length, shoot growth, leaves per shoot, | 97 | length, percent living tissue length, shoot growth, leaves per shoot, | ||
98 | chlorophyll content , and chlorophyll fluorescence. Evaluation of | 98 | chlorophyll content , and chlorophyll fluorescence. Evaluation of | ||
99 | these parameters should yield information on the relative health of | 99 | these parameters should yield information on the relative health of | ||
100 | restored marsh plants as compared to natural marsh plants. No studies | 100 | restored marsh plants as compared to natural marsh plants. No studies | ||
101 | were found that evaluated the colonization rates of J. roemerianus or | 101 | were found that evaluated the colonization rates of J. roemerianus or | ||
102 | the cost effectiveness of any aspect of J. roemerianus marsh | 102 | the cost effectiveness of any aspect of J. roemerianus marsh | ||
103 | restoration. We hope to evaluate the effectiveness of 2 restoration | 103 | restoration. We hope to evaluate the effectiveness of 2 restoration | ||
104 | designs to produce colonizing shoots and compare these observed shoot | 104 | designs to produce colonizing shoots and compare these observed shoot | ||
105 | counts to the associated cost for each design. We will also transform | 105 | counts to the associated cost for each design. We will also transform | ||
106 | these counts into rates, extrapolating coverage areas over certain | 106 | these counts into rates, extrapolating coverage areas over certain | ||
107 | time periods for both designs and also run a cost effective analysis | 107 | time periods for both designs and also run a cost effective analysis | ||
108 | on these rates. Also if differences in rates exist between exterior | 108 | on these rates. Also if differences in rates exist between exterior | ||
109 | and interior colonization shoot lengths will be used to determine if | 109 | and interior colonization shoot lengths will be used to determine if | ||
110 | varying energy allocation strategies are apparent between interior and | 110 | varying energy allocation strategies are apparent between interior and | ||
111 | exterior shoots. The determination of shoot colonization rates between | 111 | exterior shoots. The determination of shoot colonization rates between | ||
112 | restoration designs as well as cost analysis for each design based on | 112 | restoration designs as well as cost analysis for each design based on | ||
113 | these rates will prove very useful for managers who need to balance | 113 | these rates will prove very useful for managers who need to balance | ||
114 | cost and results for restoration projects. An estimate of | 114 | cost and results for restoration projects. An estimate of | ||
115 | groundwater N partitioning and the capacity of marsh systems to | 115 | groundwater N partitioning and the capacity of marsh systems to | ||
116 | attenuate the ever increasing groundwater derived N loads into marshes | 116 | attenuate the ever increasing groundwater derived N loads into marshes | ||
117 | is a pressing need for managers. On the US Gulf Coast, J. roemerianus | 117 | is a pressing need for managers. On the US Gulf Coast, J. roemerianus | ||
118 | is a dominant marsh plant that is a prime candidate for restoration | 118 | is a dominant marsh plant that is a prime candidate for restoration | ||
119 | projects and is relatively understudied with regards to nutrient | 119 | projects and is relatively understudied with regards to nutrient | ||
120 | filtration capabilities. In this project we aim to quantify the amount | 120 | filtration capabilities. In this project we aim to quantify the amount | ||
121 | of groundwater introduced NO3- that can be attenuated within 2 | 121 | of groundwater introduced NO3- that can be attenuated within 2 | ||
122 | different restoration designs of a J. roemerianus marsh as well as | 122 | different restoration designs of a J. roemerianus marsh as well as | ||
123 | trace the processes that contribute to the attenuation. A high [NO3-] | 123 | trace the processes that contribute to the attenuation. A high [NO3-] | ||
124 | groundwater plume will be continuously pumped through the 2 J. | 124 | groundwater plume will be continuously pumped through the 2 J. | ||
125 | roemerianus restoration designs and 1 unvegetated control for 31 days. | 125 | roemerianus restoration designs and 1 unvegetated control for 31 days. | ||
126 | Subsequent measurements of several N species concentrations, \u03b415N | 126 | Subsequent measurements of several N species concentrations, \u03b415N | ||
127 | value (N species, plants, animals) and conservative tracers will be | 127 | value (N species, plants, animals) and conservative tracers will be | ||
128 | taken to determine the magnitude and primary pathways of N removal | 128 | taken to determine the magnitude and primary pathways of N removal | ||
129 | from this groundwater plume. Spatial and temporal variability will be | 129 | from this groundwater plume. Spatial and temporal variability will be | ||
130 | taken into account by measurements being taken at multiple distances | 130 | taken into account by measurements being taken at multiple distances | ||
131 | from plume injection point on several sampling days. The exact | 131 | from plume injection point on several sampling days. The exact | ||
132 | location and frequency of these measurements differ according to the | 132 | location and frequency of these measurements differ according to the | ||
133 | target measurement. Knowledge of the regulatory mechanisms, | 133 | target measurement. Knowledge of the regulatory mechanisms, | ||
134 | specifically top-down, and its response to fertilization is needed for | 134 | specifically top-down, and its response to fertilization is needed for | ||
135 | J. roemerianus dominated marshes. In this study we try to alleviate | 135 | J. roemerianus dominated marshes. In this study we try to alleviate | ||
136 | the unknowns regarding potential grazer responses to fertilization and | 136 | the unknowns regarding potential grazer responses to fertilization and | ||
137 | the subsequent regulation of J. roemerianus through field and lab | 137 | the subsequent regulation of J. roemerianus through field and lab | ||
138 | experiments. We will determine if grazers preferentially choose | 138 | experiments. We will determine if grazers preferentially choose | ||
139 | fertilized areas of marsh and what potential fertilization level | 139 | fertilized areas of marsh and what potential fertilization level | ||
140 | triggers increased grazing through both field and lab experiments. | 140 | triggers increased grazing through both field and lab experiments. | ||
141 | Also a potential trophic cascade will be tested in which insectivorous | 141 | Also a potential trophic cascade will be tested in which insectivorous | ||
142 | marsh birds regulate insect grazer abundances thus reducing grazing | 142 | marsh birds regulate insect grazer abundances thus reducing grazing | ||
143 | pressures exerted on J. roemerianus. Overall the goals of the project | 143 | pressures exerted on J. roemerianus. Overall the goals of the project | ||
144 | are to understand if top-down control by grazing insects is occurring | 144 | are to understand if top-down control by grazing insects is occurring | ||
145 | in a J. roemerianus marsh and what potential mechanisms contribute to | 145 | in a J. roemerianus marsh and what potential mechanisms contribute to | ||
146 | the enhancement or reduction of this control." | 146 | the enhancement or reduction of this control." | ||
147 | }, | 147 | }, | ||
148 | { | 148 | { | ||
149 | "key": "dc.language", | 149 | "key": "dc.language", | ||
150 | "value": "en" | 150 | "value": "en" | ||
151 | }, | 151 | }, | ||
152 | { | 152 | { | ||
153 | "key": "dc.subject", | 153 | "key": "dc.subject", | ||
154 | "value": "Juncus roemerianus black needlerush marsh restoration | 154 | "value": "Juncus roemerianus black needlerush marsh restoration | ||
155 | ecosystem services morphology physiology colonization salt marsh | 155 | ecosystem services morphology physiology colonization salt marsh | ||
156 | vegetation full density restoration half density restoration nitrogen | 156 | vegetation full density restoration half density restoration nitrogen | ||
157 | groundwater nutrient filtration NO3- top-down effects regulation | 157 | groundwater nutrient filtration NO3- top-down effects regulation | ||
158 | grazing" | 158 | grazing" | ||
159 | }, | 159 | }, | ||
160 | { | 160 | { | ||
161 | "key": "dc.title", | 161 | "key": "dc.title", | ||
162 | "value": "Evaluating Success and Function of Marsh (Juncus | 162 | "value": "Evaluating Success and Function of Marsh (Juncus | ||
163 | roemerianus) Restoration (2006-2011)" | 163 | roemerianus) Restoration (2006-2011)" | ||
164 | }, | 164 | }, | ||
165 | { | 165 | { | ||
166 | "key": "spatial", | 166 | "key": "spatial", | ||
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169 | ], [ -88.40670, 30.39814 ], [ -88.40670, 30.41312 ] ] ] }" | 169 | ], [ -88.40670, 30.39814 ], [ -88.40670, 30.41312 ] ] ] }" | ||
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n | 180 | "metadata_modified": "2022-07-23T03:04:38.622896", | n | 180 | "metadata_modified": "2022-07-23T03:04:39.668992", |
181 | "name": | 181 | "name": | ||
182 | ccess-and-function-of-marsh-juncus-roemerianus-restoration-2006-2011", | 182 | ccess-and-function-of-marsh-juncus-roemerianus-restoration-2006-2011", | ||
183 | "notes": "While many restoration efforts have been conducted, there | 183 | "notes": "While many restoration efforts have been conducted, there | ||
184 | have been few comparisons of relative success between different | 184 | have been few comparisons of relative success between different | ||
185 | restoration designs, especially with J. roemerianus. Here we present | 185 | restoration designs, especially with J. roemerianus. Here we present | ||
186 | two restoration designs for evaluation, a full density restoration | 186 | two restoration designs for evaluation, a full density restoration | ||
187 | design and a half density restoration design. Full density | 187 | design and a half density restoration design. Full density | ||
188 | restorations represent the more expensive and labor intensive option. | 188 | restorations represent the more expensive and labor intensive option. | ||
189 | Several parameters will be compared between these two designs relative | 189 | Several parameters will be compared between these two designs relative | ||
190 | to the adjacent natural marsh to determine how the individual plants | 190 | to the adjacent natural marsh to determine how the individual plants | ||
191 | within these treatments perform. Several measurements have and will | 191 | within these treatments perform. Several measurements have and will | ||
192 | continue to be taken as proxies of plant health including: total shoot | 192 | continue to be taken as proxies of plant health including: total shoot | ||
193 | length, percent living tissue length, shoot growth, leaves per shoot, | 193 | length, percent living tissue length, shoot growth, leaves per shoot, | ||
194 | chlorophyll content , and chlorophyll fluorescence. Evaluation of | 194 | chlorophyll content , and chlorophyll fluorescence. Evaluation of | ||
195 | these parameters should yield information on the relative health of | 195 | these parameters should yield information on the relative health of | ||
196 | restored marsh plants as compared to natural marsh plants. No studies | 196 | restored marsh plants as compared to natural marsh plants. No studies | ||
197 | were found that evaluated the colonization rates of J. roemerianus or | 197 | were found that evaluated the colonization rates of J. roemerianus or | ||
198 | the cost effectiveness of any aspect of J. roemerianus marsh | 198 | the cost effectiveness of any aspect of J. roemerianus marsh | ||
199 | restoration. We hope to evaluate the effectiveness of 2 restoration | 199 | restoration. We hope to evaluate the effectiveness of 2 restoration | ||
200 | designs to produce colonizing shoots and compare these observed shoot | 200 | designs to produce colonizing shoots and compare these observed shoot | ||
201 | counts to the associated cost for each design. We will also transform | 201 | counts to the associated cost for each design. We will also transform | ||
202 | these counts into rates, extrapolating coverage areas over certain | 202 | these counts into rates, extrapolating coverage areas over certain | ||
203 | time periods for both designs and also run a cost effective analysis | 203 | time periods for both designs and also run a cost effective analysis | ||
204 | on these rates. Also if differences in rates exist between exterior | 204 | on these rates. Also if differences in rates exist between exterior | ||
205 | and interior colonization shoot lengths will be used to determine if | 205 | and interior colonization shoot lengths will be used to determine if | ||
206 | varying energy allocation strategies are apparent between interior and | 206 | varying energy allocation strategies are apparent between interior and | ||
207 | exterior shoots. The determination of shoot colonization rates between | 207 | exterior shoots. The determination of shoot colonization rates between | ||
208 | restoration designs as well as cost analysis for each design based on | 208 | restoration designs as well as cost analysis for each design based on | ||
209 | these rates will prove very useful for managers who need to balance | 209 | these rates will prove very useful for managers who need to balance | ||
210 | cost and results for restoration projects. An estimate of | 210 | cost and results for restoration projects. An estimate of | ||
211 | groundwater N partitioning and the capacity of marsh systems to | 211 | groundwater N partitioning and the capacity of marsh systems to | ||
212 | attenuate the ever increasing groundwater derived N loads into marshes | 212 | attenuate the ever increasing groundwater derived N loads into marshes | ||
213 | is a pressing need for managers. On the US Gulf Coast, J. roemerianus | 213 | is a pressing need for managers. On the US Gulf Coast, J. roemerianus | ||
214 | is a dominant marsh plant that is a prime candidate for restoration | 214 | is a dominant marsh plant that is a prime candidate for restoration | ||
215 | projects and is relatively understudied with regards to nutrient | 215 | projects and is relatively understudied with regards to nutrient | ||
216 | filtration capabilities. In this project we aim to quantify the amount | 216 | filtration capabilities. In this project we aim to quantify the amount | ||
217 | of groundwater introduced NO3- that can be attenuated within 2 | 217 | of groundwater introduced NO3- that can be attenuated within 2 | ||
218 | different restoration designs of a J. roemerianus marsh as well as | 218 | different restoration designs of a J. roemerianus marsh as well as | ||
219 | trace the processes that contribute to the attenuation. A high [NO3-] | 219 | trace the processes that contribute to the attenuation. A high [NO3-] | ||
220 | groundwater plume will be continuously pumped through the 2 J. | 220 | groundwater plume will be continuously pumped through the 2 J. | ||
221 | roemerianus restoration designs and 1 unvegetated control for 31 days. | 221 | roemerianus restoration designs and 1 unvegetated control for 31 days. | ||
222 | Subsequent measurements of several N species concentrations, \u03b415N | 222 | Subsequent measurements of several N species concentrations, \u03b415N | ||
223 | value (N species, plants, animals) and conservative tracers will be | 223 | value (N species, plants, animals) and conservative tracers will be | ||
224 | taken to determine the magnitude and primary pathways of N removal | 224 | taken to determine the magnitude and primary pathways of N removal | ||
225 | from this groundwater plume. Spatial and temporal variability will be | 225 | from this groundwater plume. Spatial and temporal variability will be | ||
226 | taken into account by measurements being taken at multiple distances | 226 | taken into account by measurements being taken at multiple distances | ||
227 | from plume injection point on several sampling days. The exact | 227 | from plume injection point on several sampling days. The exact | ||
228 | location and frequency of these measurements differ according to the | 228 | location and frequency of these measurements differ according to the | ||
229 | target measurement. Knowledge of the regulatory mechanisms, | 229 | target measurement. Knowledge of the regulatory mechanisms, | ||
230 | specifically top-down, and its response to fertilization is needed for | 230 | specifically top-down, and its response to fertilization is needed for | ||
231 | J. roemerianus dominated marshes. In this study we try to alleviate | 231 | J. roemerianus dominated marshes. In this study we try to alleviate | ||
232 | the unknowns regarding potential grazer responses to fertilization and | 232 | the unknowns regarding potential grazer responses to fertilization and | ||
233 | the subsequent regulation of J. roemerianus through field and lab | 233 | the subsequent regulation of J. roemerianus through field and lab | ||
234 | experiments. We will determine if grazers preferentially choose | 234 | experiments. We will determine if grazers preferentially choose | ||
235 | fertilized areas of marsh and what potential fertilization level | 235 | fertilized areas of marsh and what potential fertilization level | ||
236 | triggers increased grazing through both field and lab experiments. | 236 | triggers increased grazing through both field and lab experiments. | ||
237 | Also a potential trophic cascade will be tested in which insectivorous | 237 | Also a potential trophic cascade will be tested in which insectivorous | ||
238 | marsh birds regulate insect grazer abundances thus reducing grazing | 238 | marsh birds regulate insect grazer abundances thus reducing grazing | ||
239 | pressures exerted on J. roemerianus. Overall the goals of the project | 239 | pressures exerted on J. roemerianus. Overall the goals of the project | ||
240 | are to understand if top-down control by grazing insects is occurring | 240 | are to understand if top-down control by grazing insects is occurring | ||
241 | in a J. roemerianus marsh and what potential mechanisms contribute to | 241 | in a J. roemerianus marsh and what potential mechanisms contribute to | ||
242 | the enhancement or reduction of this control.", | 242 | the enhancement or reduction of this control.", | ||
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317 | "state": "active", | 342 | "state": "active", | ||
318 | "vocabulary_id": null | 343 | "vocabulary_id": null | ||
319 | }, | 344 | }, | ||
320 | { | 345 | { | ||
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322 | "id": "a2e7290a-74f7-4e92-bd07-554f7270741d", | 347 | "id": "a2e7290a-74f7-4e92-bd07-554f7270741d", | ||
323 | "name": "Mississippi", | 348 | "name": "Mississippi", | ||
324 | "state": "active", | 349 | "state": "active", | ||
325 | "vocabulary_id": null | 350 | "vocabulary_id": null | ||
326 | }, | 351 | }, | ||
327 | { | 352 | { | ||
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329 | "id": "e7812dcd-767b-4877-a67a-1bbfcd453daa", | 354 | "id": "e7812dcd-767b-4877-a67a-1bbfcd453daa", | ||
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331 | "state": "active", | 356 | "state": "active", | ||
332 | "vocabulary_id": null | 357 | "vocabulary_id": null | ||
333 | }, | 358 | }, | ||
334 | { | 359 | { | ||
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339 | "vocabulary_id": null | 364 | "vocabulary_id": null | ||
340 | }, | 365 | }, | ||
341 | { | 366 | { | ||
342 | "display_name": "biota", | 367 | "display_name": "biota", | ||
343 | "id": "8697f957-08f7-4539-8025-fcb58cb28994", | 368 | "id": "8697f957-08f7-4539-8025-fcb58cb28994", | ||
344 | "name": "biota", | 369 | "name": "biota", | ||
345 | "state": "active", | 370 | "state": "active", | ||
346 | "vocabulary_id": null | 371 | "vocabulary_id": null | ||
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348 | { | 373 | { | ||
349 | "display_name": "black needlerush", | 374 | "display_name": "black needlerush", | ||
350 | "id": "d4b85e8e-b42f-42b2-b699-47c62145dd66", | 375 | "id": "d4b85e8e-b42f-42b2-b699-47c62145dd66", | ||
351 | "name": "black needlerush", | 376 | "name": "black needlerush", | ||
352 | "state": "active", | 377 | "state": "active", | ||
353 | "vocabulary_id": null | 378 | "vocabulary_id": null | ||
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358 | "name": "colonization", | 383 | "name": "colonization", | ||
359 | "state": "active", | 384 | "state": "active", | ||
360 | "vocabulary_id": null | 385 | "vocabulary_id": null | ||
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362 | { | 387 | { | ||
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364 | "id": "13d7d537-d828-4987-9aef-d853bec3f7f5", | 389 | "id": "13d7d537-d828-4987-9aef-d853bec3f7f5", | ||
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367 | "vocabulary_id": null | 392 | "vocabulary_id": null | ||
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369 | { | 394 | { | ||
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372 | "name": "environment", | 397 | "name": "environment", | ||
373 | "state": "active", | 398 | "state": "active", | ||
374 | "vocabulary_id": null | 399 | "vocabulary_id": null | ||
375 | }, | 400 | }, | ||
376 | { | 401 | { | ||
377 | "display_name": "full density restoration", | 402 | "display_name": "full density restoration", | ||
378 | "id": "1412c8fe-799f-4dcc-b2d4-c339a6c0e81b", | 403 | "id": "1412c8fe-799f-4dcc-b2d4-c339a6c0e81b", | ||
379 | "name": "full density restoration", | 404 | "name": "full density restoration", | ||
380 | "state": "active", | 405 | "state": "active", | ||
381 | "vocabulary_id": null | 406 | "vocabulary_id": null | ||
382 | }, | 407 | }, | ||
383 | { | 408 | { | ||
384 | "display_name": "grazing", | 409 | "display_name": "grazing", | ||
385 | "id": "d67d1c84-6168-40b5-8cb2-1956ce38fd90", | 410 | "id": "d67d1c84-6168-40b5-8cb2-1956ce38fd90", | ||
386 | "name": "grazing", | 411 | "name": "grazing", | ||
387 | "state": "active", | 412 | "state": "active", | ||
388 | "vocabulary_id": null | 413 | "vocabulary_id": null | ||
389 | }, | 414 | }, | ||
390 | { | 415 | { | ||
391 | "display_name": "groundwater", | 416 | "display_name": "groundwater", | ||
392 | "id": "abd49818-de6f-40cc-b853-328d19e494db", | 417 | "id": "abd49818-de6f-40cc-b853-328d19e494db", | ||
393 | "name": "groundwater", | 418 | "name": "groundwater", | ||
394 | "state": "active", | 419 | "state": "active", | ||
395 | "vocabulary_id": null | 420 | "vocabulary_id": null | ||
396 | }, | 421 | }, | ||
397 | { | 422 | { | ||
398 | "display_name": "half density restoration", | 423 | "display_name": "half density restoration", | ||
399 | "id": "4de5e2b3-0a0f-4842-90d8-0712b3baf9ab", | 424 | "id": "4de5e2b3-0a0f-4842-90d8-0712b3baf9ab", | ||
400 | "name": "half density restoration", | 425 | "name": "half density restoration", | ||
401 | "state": "active", | 426 | "state": "active", | ||
402 | "vocabulary_id": null | 427 | "vocabulary_id": null | ||
403 | }, | 428 | }, | ||
404 | { | 429 | { | ||
405 | "display_name": "inlandWaters", | 430 | "display_name": "inlandWaters", | ||
406 | "id": "4de5a18a-988f-4e2a-a4dc-796b40220f97", | 431 | "id": "4de5a18a-988f-4e2a-a4dc-796b40220f97", | ||
407 | "name": "inlandWaters", | 432 | "name": "inlandWaters", | ||
408 | "state": "active", | 433 | "state": "active", | ||
409 | "vocabulary_id": null | 434 | "vocabulary_id": null | ||
410 | }, | 435 | }, | ||
411 | { | 436 | { | ||
412 | "display_name": "marsh restoration", | 437 | "display_name": "marsh restoration", | ||
413 | "id": "b444eb07-9402-4159-8047-429cad7fafad", | 438 | "id": "b444eb07-9402-4159-8047-429cad7fafad", | ||
414 | "name": "marsh restoration", | 439 | "name": "marsh restoration", | ||
415 | "state": "active", | 440 | "state": "active", | ||
416 | "vocabulary_id": null | 441 | "vocabulary_id": null | ||
417 | }, | 442 | }, | ||
418 | { | 443 | { | ||
419 | "display_name": "morphology", | 444 | "display_name": "morphology", | ||
420 | "id": "8c9f53a7-0089-4db1-8655-c37f11acf6f1", | 445 | "id": "8c9f53a7-0089-4db1-8655-c37f11acf6f1", | ||
421 | "name": "morphology", | 446 | "name": "morphology", | ||
422 | "state": "active", | 447 | "state": "active", | ||
423 | "vocabulary_id": null | 448 | "vocabulary_id": null | ||
424 | }, | 449 | }, | ||
425 | { | 450 | { | ||
426 | "display_name": "nitrogen", | 451 | "display_name": "nitrogen", | ||
427 | "id": "b543fdc1-f51b-45aa-a0e5-3bd859c9036c", | 452 | "id": "b543fdc1-f51b-45aa-a0e5-3bd859c9036c", | ||
428 | "name": "nitrogen", | 453 | "name": "nitrogen", | ||
429 | "state": "active", | 454 | "state": "active", | ||
430 | "vocabulary_id": null | 455 | "vocabulary_id": null | ||
431 | }, | 456 | }, | ||
432 | { | 457 | { | ||
433 | "display_name": "nutrient filtration", | 458 | "display_name": "nutrient filtration", | ||
434 | "id": "7594086e-f404-407c-9f18-aaa01c4eab7e", | 459 | "id": "7594086e-f404-407c-9f18-aaa01c4eab7e", | ||
435 | "name": "nutrient filtration", | 460 | "name": "nutrient filtration", | ||
436 | "state": "active", | 461 | "state": "active", | ||
437 | "vocabulary_id": null | 462 | "vocabulary_id": null | ||
438 | }, | 463 | }, | ||
439 | { | 464 | { | ||
440 | "display_name": "oceans", | 465 | "display_name": "oceans", | ||
441 | "id": "a6963a6f-1b79-4724-a263-d5f1bebec382", | 466 | "id": "a6963a6f-1b79-4724-a263-d5f1bebec382", | ||
442 | "name": "oceans", | 467 | "name": "oceans", | ||
443 | "state": "active", | 468 | "state": "active", | ||
444 | "vocabulary_id": null | 469 | "vocabulary_id": null | ||
445 | }, | 470 | }, | ||
446 | { | 471 | { | ||
447 | "display_name": "physiology", | 472 | "display_name": "physiology", | ||
448 | "id": "6ab93ce8-4018-41dd-8e9d-de300ebd0287", | 473 | "id": "6ab93ce8-4018-41dd-8e9d-de300ebd0287", | ||
449 | "name": "physiology", | 474 | "name": "physiology", | ||
450 | "state": "active", | 475 | "state": "active", | ||
451 | "vocabulary_id": null | 476 | "vocabulary_id": null | ||
452 | }, | 477 | }, | ||
453 | { | 478 | { | ||
454 | "display_name": "regulation", | 479 | "display_name": "regulation", | ||
455 | "id": "b99680c3-e783-4112-949e-3969940b1635", | 480 | "id": "b99680c3-e783-4112-949e-3969940b1635", | ||
456 | "name": "regulation", | 481 | "name": "regulation", | ||
457 | "state": "active", | 482 | "state": "active", | ||
458 | "vocabulary_id": null | 483 | "vocabulary_id": null | ||
459 | }, | 484 | }, | ||
460 | { | 485 | { | ||
461 | "display_name": "salt marsh", | 486 | "display_name": "salt marsh", | ||
462 | "id": "5c257f3f-a48e-47b6-a1cc-4113dc5cea33", | 487 | "id": "5c257f3f-a48e-47b6-a1cc-4113dc5cea33", | ||
463 | "name": "salt marsh", | 488 | "name": "salt marsh", | ||
464 | "state": "active", | 489 | "state": "active", | ||
465 | "vocabulary_id": null | 490 | "vocabulary_id": null | ||
466 | }, | 491 | }, | ||
467 | { | 492 | { | ||
468 | "display_name": "top-down effects", | 493 | "display_name": "top-down effects", | ||
469 | "id": "46b58414-e502-4914-bf4a-a4db7a352635", | 494 | "id": "46b58414-e502-4914-bf4a-a4db7a352635", | ||
470 | "name": "top-down effects", | 495 | "name": "top-down effects", | ||
471 | "state": "active", | 496 | "state": "active", | ||
472 | "vocabulary_id": null | 497 | "vocabulary_id": null | ||
473 | }, | 498 | }, | ||
474 | { | 499 | { | ||
475 | "display_name": "vegetation", | 500 | "display_name": "vegetation", | ||
476 | "id": "e1caac2e-bdca-4a1c-bb2d-1a2c3351fe1a", | 501 | "id": "e1caac2e-bdca-4a1c-bb2d-1a2c3351fe1a", | ||
477 | "name": "vegetation", | 502 | "name": "vegetation", | ||
478 | "state": "active", | 503 | "state": "active", | ||
479 | "vocabulary_id": null | 504 | "vocabulary_id": null | ||
480 | } | 505 | } | ||
481 | ], | 506 | ], | ||
482 | "title": "Evaluating Success and Function of Marsh (Juncus | 507 | "title": "Evaluating Success and Function of Marsh (Juncus | ||
483 | roemerianus) Restoration (2006-2011)", | 508 | roemerianus) Restoration (2006-2011)", | ||
484 | "type": "dataset", | 509 | "type": "dataset", | ||
485 | "url": null, | 510 | "url": null, | ||
486 | "version": null | 511 | "version": null | ||
487 | } | 512 | } |