Changes
On July 23, 2022 at 3:04:16 AM UTC, 851c91e4-6343-45af-967a-20a33797707e:
-
Added resource 28.html to Use of N stable isotope and microbial analyses to define wastewater influence in Mobile Bay, AL (2007)
f | 1 | { | f | 1 | { |
2 | "author": "Dr. Ruth Carmichael", | 2 | "author": "Dr. Ruth Carmichael", | ||
3 | "author_email": "rcarmichael@disl.org", | 3 | "author_email": "rcarmichael@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 | Ruth Carmichael of the Dauphin Island Sea Lab's Marine Organism and | 9 | Ruth Carmichael of the Dauphin Island Sea Lab's Marine Organism and | ||
10 | Ecosystem Response Lab." | 10 | Ecosystem Response Lab." | ||
11 | }, | 11 | }, | ||
12 | { | 12 | { | ||
13 | "key": "ISO 19115 Topic Categories", | 13 | "key": "ISO 19115 Topic Categories", | ||
14 | "value": "biota, 002, environment, 007, inlandWaters, 012, | 14 | "value": "biota, 002, environment, 007, inlandWaters, 012, | ||
15 | utilitiesCommunication, 019" | 15 | utilitiesCommunication, 019" | ||
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17 | { | 17 | { | ||
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19 | "value": "Mobile, Alabama, Mobile Bay, McDuffie Island, Dauphin | 19 | "value": "Mobile, Alabama, Mobile Bay, McDuffie Island, Dauphin | ||
20 | Island Sea Lab" | 20 | Island Sea Lab" | ||
21 | }, | 21 | }, | ||
22 | { | 22 | { | ||
23 | "key": "Theme Keywords", | 23 | "key": "Theme Keywords", | ||
24 | "value": "fecal coliforms, male-specific bacteriophage, MSB, | 24 | "value": "fecal coliforms, male-specific bacteriophage, MSB, | ||
25 | eastern oysters, virus, bacteria, growth, Nitrogen, N stable isotope, | 25 | eastern oysters, virus, bacteria, growth, Nitrogen, N stable isotope, | ||
26 | wastewater, shellfish, wastewater treatment plants, WTP, effluent, | 26 | wastewater, shellfish, wastewater treatment plants, WTP, effluent, | ||
27 | contamination" | 27 | contamination" | ||
28 | }, | 28 | }, | ||
29 | { | 29 | { | ||
30 | "key": "Use_Constraints", | 30 | "key": "Use_Constraints", | ||
31 | "value": "Acknowledgment of the DISL: Marine Organism and | 31 | "value": "Acknowledgment of the DISL: Marine Organism and | ||
32 | Ecosystem Response Lab, the National Science Foundation REU program | 32 | Ecosystem Response Lab, the National Science Foundation REU program | ||
33 | and the U.S.A. Oyster Restoration Program would be appreciated in | 33 | and the U.S.A. Oyster Restoration Program would be appreciated in | ||
34 | products developed from these data, and such acknowledgment as is | 34 | products developed from these data, and such acknowledgment as is | ||
35 | standard for citation and legal practices for data source is expected | 35 | standard for citation and legal practices for data source is expected | ||
36 | by users of these data. Users should be aware that comparison with | 36 | by users of these data. Users should be aware that comparison with | ||
37 | other data sets for the same area from other time periods may be | 37 | other data sets for the same area from other time periods may be | ||
38 | inaccurate due to inconsistencies resulting from changes in mapping | 38 | inaccurate due to inconsistencies resulting from changes in mapping | ||
39 | conventions, data collection, and computer processes over time. The | 39 | conventions, data collection, and computer processes over time. The | ||
40 | distributor shall not be liable for improper or incorrect use of these | 40 | distributor shall not be liable for improper or incorrect use of these | ||
41 | data, based on the description of appropriate/inappropriate uses | 41 | data, based on the description of appropriate/inappropriate uses | ||
42 | described in the metadata document. These data are not legal documents | 42 | described in the metadata document. These data are not legal documents | ||
43 | and are not to be used as such." | 43 | and are not to be used as such." | ||
44 | }, | 44 | }, | ||
45 | { | 45 | { | ||
46 | "key": "dc.coverage.placeName", | 46 | "key": "dc.coverage.placeName", | ||
47 | "value": "Mobile Alabama Mobile Bay McDuffie Island Dauphin | 47 | "value": "Mobile Alabama Mobile Bay McDuffie Island Dauphin | ||
48 | Island Sea Lab" | 48 | Island Sea Lab" | ||
49 | }, | 49 | }, | ||
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74 | { | 74 | { | ||
75 | "key": "dc.creator", | 75 | "key": "dc.creator", | ||
76 | "value": "Dauphin Island Sea Lab's Marine Organism and Ecosystem | 76 | "value": "Dauphin Island Sea Lab's Marine Organism and Ecosystem | ||
77 | Response Lab" | 77 | Response Lab" | ||
78 | }, | 78 | }, | ||
79 | { | 79 | { | ||
80 | "key": "dc.date", | 80 | "key": "dc.date", | ||
81 | "value": "2008" | 81 | "value": "2008" | ||
82 | }, | 82 | }, | ||
83 | { | 83 | { | ||
84 | "key": "dc.description", | 84 | "key": "dc.description", | ||
85 | "value": "We assessed short-term ecological and potential human | 85 | "value": "We assessed short-term ecological and potential human | ||
86 | health effects of wastewater treatment plant (WTP) effluent by | 86 | health effects of wastewater treatment plant (WTP) effluent by | ||
87 | measuring \u03b415N\u2030 and microbial concentrations in oysters and | 87 | measuring \u03b415N\u2030 and microbial concentrations in oysters and | ||
88 | suspended particulate matter (SPM). We also tested male-specific | 88 | suspended particulate matter (SPM). We also tested male-specific | ||
89 | bacteriophage (MSB) as an alternative to fecal coliforms, to assess | 89 | bacteriophage (MSB) as an alternative to fecal coliforms, to assess | ||
90 | potential influence of wastewater contamination on shellfish. WTP | 90 | potential influence of wastewater contamination on shellfish. WTP | ||
91 | effluent did not affect oyster growth or survival, but SPM and oysters | 91 | effluent did not affect oyster growth or survival, but SPM and oysters | ||
92 | acquired wastewater-specific \u03b415N\u2030. \u03b415N values were | 92 | acquired wastewater-specific \u03b415N\u2030. \u03b415N values were | ||
93 | depleted near the WTP, typical of low-level processed wastewater. | 93 | depleted near the WTP, typical of low-level processed wastewater. | ||
94 | Fecal coliform and MSB concentrations were higher in samples taken | 94 | Fecal coliform and MSB concentrations were higher in samples taken | ||
95 | closest to the WTP, and MSB values were significantly correlated with | 95 | closest to the WTP, and MSB values were significantly correlated with | ||
96 | \u03b415N\u2030 in oyster tissues. Overall, oysters demonstrated | 96 | \u03b415N\u2030 in oyster tissues. Overall, oysters demonstrated | ||
97 | relatively rapid integration and accumulation of wastewater-specific | 97 | relatively rapid integration and accumulation of wastewater-specific | ||
98 | \u03b415N\u2030 and indicator microorganisms compared to water | 98 | \u03b415N\u2030 and indicator microorganisms compared to water | ||
99 | samples. These data suggest oysters were superior sentinels compared | 99 | samples. These data suggest oysters were superior sentinels compared | ||
100 | to water, and MSB was a more reliable indicator of wastewater | 100 | to water, and MSB was a more reliable indicator of wastewater | ||
101 | influence on shellfish than fecal coliforms." | 101 | influence on shellfish than fecal coliforms." | ||
102 | }, | 102 | }, | ||
103 | { | 103 | { | ||
104 | "key": "dc.language", | 104 | "key": "dc.language", | ||
105 | "value": "en" | 105 | "value": "en" | ||
106 | }, | 106 | }, | ||
107 | { | 107 | { | ||
108 | "key": "dc.source", | 108 | "key": "dc.source", | ||
109 | "value": "Josh Daskin's Summer 2007 REU project" | 109 | "value": "Josh Daskin's Summer 2007 REU project" | ||
110 | }, | 110 | }, | ||
111 | { | 111 | { | ||
112 | "key": "dc.subject", | 112 | "key": "dc.subject", | ||
113 | "value": "fecal coliforms male-specific bacteriophage MSB | 113 | "value": "fecal coliforms male-specific bacteriophage MSB | ||
114 | eastern oysters virus bacteria growth Nitrogen N stable isotope | 114 | eastern oysters virus bacteria growth Nitrogen N stable isotope | ||
115 | wastewater shellfish wastewater treatment plants WTP effluent | 115 | wastewater shellfish wastewater treatment plants WTP effluent | ||
116 | contamination" | 116 | contamination" | ||
117 | }, | 117 | }, | ||
118 | { | 118 | { | ||
119 | "key": "dc.title", | 119 | "key": "dc.title", | ||
120 | "value": "Use of N stable isotope and microbial analyses to | 120 | "value": "Use of N stable isotope and microbial analyses to | ||
121 | define wastewater influence in Mobile Bay, AL (2007)" | 121 | define wastewater influence in Mobile Bay, AL (2007)" | ||
122 | }, | 122 | }, | ||
123 | { | 123 | { | ||
124 | "key": "dc.type", | 124 | "key": "dc.type", | ||
125 | "value": "spreadsheet" | 125 | "value": "spreadsheet" | ||
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131 | ], [ -88.03313, 30.61250 ], [ -88.03313, 30.65788 ] ] ] }" | 131 | ], [ -88.03313, 30.61250 ], [ -88.03313, 30.65788 ] ] ] }" | ||
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145 | "notes": "We assessed short-term ecological and potential human | 145 | "notes": "We assessed short-term ecological and potential human | ||
146 | health effects of wastewater treatment plant (WTP) effluent by | 146 | health effects of wastewater treatment plant (WTP) effluent by | ||
147 | measuring \u03b415N\u2030 and microbial concentrations in oysters and | 147 | measuring \u03b415N\u2030 and microbial concentrations in oysters and | ||
148 | suspended particulate matter (SPM). We also tested male-specific | 148 | suspended particulate matter (SPM). We also tested male-specific | ||
149 | bacteriophage (MSB) as an alternative to fecal coliforms, to assess | 149 | bacteriophage (MSB) as an alternative to fecal coliforms, to assess | ||
150 | potential influence of wastewater contamination on shellfish. WTP | 150 | potential influence of wastewater contamination on shellfish. WTP | ||
151 | effluent did not affect oyster growth or survival, but SPM and oysters | 151 | effluent did not affect oyster growth or survival, but SPM and oysters | ||
152 | acquired wastewater-specific \u03b415N\u2030. \u03b415N values were | 152 | acquired wastewater-specific \u03b415N\u2030. \u03b415N values were | ||
153 | depleted near the WTP, typical of low-level processed wastewater. | 153 | depleted near the WTP, typical of low-level processed wastewater. | ||
154 | Fecal coliform and MSB concentrations were higher in samples taken | 154 | Fecal coliform and MSB concentrations were higher in samples taken | ||
155 | closest to the WTP, and MSB values were significantly correlated with | 155 | closest to the WTP, and MSB values were significantly correlated with | ||
156 | \u03b415N\u2030 in oyster tissues. Overall, oysters demonstrated | 156 | \u03b415N\u2030 in oyster tissues. Overall, oysters demonstrated | ||
157 | relatively rapid integration and accumulation of wastewater-specific | 157 | relatively rapid integration and accumulation of wastewater-specific | ||
158 | \u03b415N\u2030 and indicator microorganisms compared to water | 158 | \u03b415N\u2030 and indicator microorganisms compared to water | ||
159 | samples. These data suggest oysters were superior sentinels compared | 159 | samples. These data suggest oysters were superior sentinels compared | ||
160 | to water, and MSB was a more reliable indicator of wastewater | 160 | to water, and MSB was a more reliable indicator of wastewater | ||
161 | influence on shellfish than fecal coliforms.", | 161 | influence on shellfish than fecal coliforms.", | ||
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275 | "display_name": "bacteria", | 300 | "display_name": "bacteria", | ||
276 | "id": "8881ee23-e368-4cbc-909f-573eb50ea166", | 301 | "id": "8881ee23-e368-4cbc-909f-573eb50ea166", | ||
277 | "name": "bacteria", | 302 | "name": "bacteria", | ||
278 | "state": "active", | 303 | "state": "active", | ||
279 | "vocabulary_id": null | 304 | "vocabulary_id": null | ||
280 | }, | 305 | }, | ||
281 | { | 306 | { | ||
282 | "display_name": "biota", | 307 | "display_name": "biota", | ||
283 | "id": "8697f957-08f7-4539-8025-fcb58cb28994", | 308 | "id": "8697f957-08f7-4539-8025-fcb58cb28994", | ||
284 | "name": "biota", | 309 | "name": "biota", | ||
285 | "state": "active", | 310 | "state": "active", | ||
286 | "vocabulary_id": null | 311 | "vocabulary_id": null | ||
287 | }, | 312 | }, | ||
288 | { | 313 | { | ||
289 | "display_name": "contamination", | 314 | "display_name": "contamination", | ||
290 | "id": "4903c835-1644-4680-8eb1-dff3cfa8e6d8", | 315 | "id": "4903c835-1644-4680-8eb1-dff3cfa8e6d8", | ||
291 | "name": "contamination", | 316 | "name": "contamination", | ||
292 | "state": "active", | 317 | "state": "active", | ||
293 | "vocabulary_id": null | 318 | "vocabulary_id": null | ||
294 | }, | 319 | }, | ||
295 | { | 320 | { | ||
296 | "display_name": "eastern oysters", | 321 | "display_name": "eastern oysters", | ||
297 | "id": "142a5bd6-b45e-45c0-bef3-44042ead2b75", | 322 | "id": "142a5bd6-b45e-45c0-bef3-44042ead2b75", | ||
298 | "name": "eastern oysters", | 323 | "name": "eastern oysters", | ||
299 | "state": "active", | 324 | "state": "active", | ||
300 | "vocabulary_id": null | 325 | "vocabulary_id": null | ||
301 | }, | 326 | }, | ||
302 | { | 327 | { | ||
303 | "display_name": "effluent", | 328 | "display_name": "effluent", | ||
304 | "id": "f7ebcf13-7ab5-488a-8f53-3aef60a27aa0", | 329 | "id": "f7ebcf13-7ab5-488a-8f53-3aef60a27aa0", | ||
305 | "name": "effluent", | 330 | "name": "effluent", | ||
306 | "state": "active", | 331 | "state": "active", | ||
307 | "vocabulary_id": null | 332 | "vocabulary_id": null | ||
308 | }, | 333 | }, | ||
309 | { | 334 | { | ||
310 | "display_name": "environment", | 335 | "display_name": "environment", | ||
311 | "id": "c1a667ee-c399-4f70-a7cb-449fb05391a4", | 336 | "id": "c1a667ee-c399-4f70-a7cb-449fb05391a4", | ||
312 | "name": "environment", | 337 | "name": "environment", | ||
313 | "state": "active", | 338 | "state": "active", | ||
314 | "vocabulary_id": null | 339 | "vocabulary_id": null | ||
315 | }, | 340 | }, | ||
316 | { | 341 | { | ||
317 | "display_name": "fecal coliforms", | 342 | "display_name": "fecal coliforms", | ||
318 | "id": "961f1bf9-30e0-4f31-b0d0-9b9778d29ca0", | 343 | "id": "961f1bf9-30e0-4f31-b0d0-9b9778d29ca0", | ||
319 | "name": "fecal coliforms", | 344 | "name": "fecal coliforms", | ||
320 | "state": "active", | 345 | "state": "active", | ||
321 | "vocabulary_id": null | 346 | "vocabulary_id": null | ||
322 | }, | 347 | }, | ||
323 | { | 348 | { | ||
324 | "display_name": "growth", | 349 | "display_name": "growth", | ||
325 | "id": "5f6bba8f-5bc7-4ffb-99c7-b87a56573c2b", | 350 | "id": "5f6bba8f-5bc7-4ffb-99c7-b87a56573c2b", | ||
326 | "name": "growth", | 351 | "name": "growth", | ||
327 | "state": "active", | 352 | "state": "active", | ||
328 | "vocabulary_id": null | 353 | "vocabulary_id": null | ||
329 | }, | 354 | }, | ||
330 | { | 355 | { | ||
331 | "display_name": "inlandWaters", | 356 | "display_name": "inlandWaters", | ||
332 | "id": "4de5a18a-988f-4e2a-a4dc-796b40220f97", | 357 | "id": "4de5a18a-988f-4e2a-a4dc-796b40220f97", | ||
333 | "name": "inlandWaters", | 358 | "name": "inlandWaters", | ||
334 | "state": "active", | 359 | "state": "active", | ||
335 | "vocabulary_id": null | 360 | "vocabulary_id": null | ||
336 | }, | 361 | }, | ||
337 | { | 362 | { | ||
338 | "display_name": "male-specific bacteriophage", | 363 | "display_name": "male-specific bacteriophage", | ||
339 | "id": "ba975719-3387-4dd4-b0ec-7c4df5ddc5ac", | 364 | "id": "ba975719-3387-4dd4-b0ec-7c4df5ddc5ac", | ||
340 | "name": "male-specific bacteriophage", | 365 | "name": "male-specific bacteriophage", | ||
341 | "state": "active", | 366 | "state": "active", | ||
342 | "vocabulary_id": null | 367 | "vocabulary_id": null | ||
343 | }, | 368 | }, | ||
344 | { | 369 | { | ||
345 | "display_name": "shellfish", | 370 | "display_name": "shellfish", | ||
346 | "id": "553ffdef-6b7e-4fc1-be90-04941c03f138", | 371 | "id": "553ffdef-6b7e-4fc1-be90-04941c03f138", | ||
347 | "name": "shellfish", | 372 | "name": "shellfish", | ||
348 | "state": "active", | 373 | "state": "active", | ||
349 | "vocabulary_id": null | 374 | "vocabulary_id": null | ||
350 | }, | 375 | }, | ||
351 | { | 376 | { | ||
352 | "display_name": "utilitiesCommunication", | 377 | "display_name": "utilitiesCommunication", | ||
353 | "id": "b11dd346-c4fd-4d61-8238-be8034ff9763", | 378 | "id": "b11dd346-c4fd-4d61-8238-be8034ff9763", | ||
354 | "name": "utilitiesCommunication", | 379 | "name": "utilitiesCommunication", | ||
355 | "state": "active", | 380 | "state": "active", | ||
356 | "vocabulary_id": null | 381 | "vocabulary_id": null | ||
357 | }, | 382 | }, | ||
358 | { | 383 | { | ||
359 | "display_name": "virus", | 384 | "display_name": "virus", | ||
360 | "id": "338a9376-3a29-4815-88c7-af6154ad73fa", | 385 | "id": "338a9376-3a29-4815-88c7-af6154ad73fa", | ||
361 | "name": "virus", | 386 | "name": "virus", | ||
362 | "state": "active", | 387 | "state": "active", | ||
363 | "vocabulary_id": null | 388 | "vocabulary_id": null | ||
364 | }, | 389 | }, | ||
365 | { | 390 | { | ||
366 | "display_name": "wastewater", | 391 | "display_name": "wastewater", | ||
367 | "id": "89dcc77d-4cbb-4548-bd16-9a5e9df91af0", | 392 | "id": "89dcc77d-4cbb-4548-bd16-9a5e9df91af0", | ||
368 | "name": "wastewater", | 393 | "name": "wastewater", | ||
369 | "state": "active", | 394 | "state": "active", | ||
370 | "vocabulary_id": null | 395 | "vocabulary_id": null | ||
371 | }, | 396 | }, | ||
372 | { | 397 | { | ||
373 | "display_name": "wastewater treatment plants", | 398 | "display_name": "wastewater treatment plants", | ||
374 | "id": "8c7e15e5-b973-493e-9c71-c2d104aa09c1", | 399 | "id": "8c7e15e5-b973-493e-9c71-c2d104aa09c1", | ||
375 | "name": "wastewater treatment plants", | 400 | "name": "wastewater treatment plants", | ||
376 | "state": "active", | 401 | "state": "active", | ||
377 | "vocabulary_id": null | 402 | "vocabulary_id": null | ||
378 | } | 403 | } | ||
379 | ], | 404 | ], | ||
380 | "title": "Use of N stable isotope and microbial analyses to define | 405 | "title": "Use of N stable isotope and microbial analyses to define | ||
381 | wastewater influence in Mobile Bay, AL (2007)", | 406 | wastewater influence in Mobile Bay, AL (2007)", | ||
382 | "type": "dataset", | 407 | "type": "dataset", | ||
383 | "url": null, | 408 | "url": null, | ||
384 | "version": null | 409 | "version": null | ||
385 | } | 410 | } |