Changes
On October 10, 2022 at 9:19:51 PM UTC, c17a0114-fe1c-4191-986b-40c4b31b670a:
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Removed the following tags from The effects of oiling on salt marsh and mangrove macrofauna communities at the Chandeleur Islands, LA (June and September 2015)
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Changed value of field
ignore_hash
toTrue
in resource Macrofauna_biomass_ChandeleurIsland_2015.csv in The effects of oiling on salt marsh and mangrove macrofauna communities at the Chandeleur Islands, LA (June and September 2015) -
Changed value of field
task_created
of resource Macrofauna_biomass_ChandeleurIsland_2015.csv to2022-10-10 21:15:13.967423
(previously2022-07-27 14:34:53.469239
) in The effects of oiling on salt marsh and mangrove macrofauna communities at the Chandeleur Islands, LA (June and September 2015)
| f | 1 | { | f | 1 | { |
| 2 | "author": "Kenneth L. Heck", | 2 | "author": "Kenneth L. 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": "DOI", | 7 | "key": "DOI", | ||
| 8 | "value": "doi:10.7266/N7B8565W" | 8 | "value": "doi:10.7266/N7B8565W" | ||
| 9 | }, | 9 | }, | ||
| 10 | { | 10 | { | ||
| 11 | "key": "ISO.principalInvestigator", | 11 | "key": "ISO.principalInvestigator", | ||
| 12 | "value": "Kenneth L. Heck <kheck@disl.org>" | 12 | "value": "Kenneth L. Heck <kheck@disl.org>" | ||
| 13 | }, | 13 | }, | ||
| 14 | { | 14 | { | ||
| 15 | "key": "Place Keywords", | 15 | "key": "Place Keywords", | ||
| 16 | "value": "Chandeleur Islands, Louisiana, Chandeleur Sound, Gulf | 16 | "value": "Chandeleur Islands, Louisiana, Chandeleur Sound, Gulf | ||
| 17 | of Mexico" | 17 | of Mexico" | ||
| 18 | }, | 18 | }, | ||
| 19 | { | 19 | { | ||
| 20 | "key": "Temporal Begin", | 20 | "key": "Temporal Begin", | ||
| 21 | "value": "2015-06-29" | 21 | "value": "2015-06-29" | ||
| 22 | }, | 22 | }, | ||
| 23 | { | 23 | { | ||
| 24 | "key": "Temporal End", | 24 | "key": "Temporal End", | ||
| 25 | "value": "2015-09-22" | 25 | "value": "2015-09-22" | ||
| 26 | }, | 26 | }, | ||
| 27 | { | 27 | { | ||
| 28 | "key": "Theme Keywords", | 28 | "key": "Theme Keywords", | ||
| 29 | "value": "Spartina alterniflora, Avicennia germinans, Salt | 29 | "value": "Spartina alterniflora, Avicennia germinans, Salt | ||
| 30 | marsh, Macrofauna, Deepwater Horizon, Black mangrove" | 30 | marsh, Macrofauna, Deepwater Horizon, Black mangrove" | ||
| 31 | }, | 31 | }, | ||
| 32 | { | 32 | { | ||
| 33 | "key": "spatial", | 33 | "key": "spatial", | ||
| 34 | "value": "{ \"type\": \"Polygon\", \"coordinates\": [ [ [ | 34 | "value": "{ \"type\": \"Polygon\", \"coordinates\": [ [ [ | ||
| 35 | -88.84114, 29.93218 ], [ -88.82712, 29.93218 ], [ -88.82712, 29.86356 | 35 | -88.84114, 29.93218 ], [ -88.82712, 29.93218 ], [ -88.82712, 29.86356 | ||
| 36 | ], [ -88.84114, 29.86356 ], [ -88.84114, 29.93218 ] ] ] }" | 36 | ], [ -88.84114, 29.86356 ], [ -88.84114, 29.93218 ] ] ] }" | ||
| 37 | } | 37 | } | ||
| 38 | ], | 38 | ], | ||
| 39 | "groups": [], | 39 | "groups": [], | ||
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| 41 | "isopen": false, | 41 | "isopen": false, | ||
| 42 | "license_id": null, | 42 | "license_id": null, | ||
| 43 | "license_title": null, | 43 | "license_title": null, | ||
| 44 | "maintainer": "data@disl.org", | 44 | "maintainer": "data@disl.org", | ||
| 45 | "maintainer_email": "data@disl.org", | 45 | "maintainer_email": "data@disl.org", | ||
| 46 | "metadata_created": "2022-07-27T14:34:52.105574", | 46 | "metadata_created": "2022-07-27T14:34:52.105574", | ||
| n | 47 | "metadata_modified": "2022-07-27T14:38:46.819352", | n | 47 | "metadata_modified": "2022-10-10T21:19:50.882779", |
| 48 | "name": | 48 | "name": | ||
| 49 | rsh-and-mangrove-macrofauna-communities-at-the-chandeleur-isn7b8565w", | 49 | rsh-and-mangrove-macrofauna-communities-at-the-chandeleur-isn7b8565w", | ||
| 50 | "notes": "### Abstract\nTo determine the relative abundances, | 50 | "notes": "### Abstract\nTo determine the relative abundances, | ||
| 51 | species number, and composition of macrofauna, all plots were sampled | 51 | species number, and composition of macrofauna, all plots were sampled | ||
| 52 | at high tide during the growing season (June and October) in 2015 in | 52 | at high tide during the growing season (June and October) in 2015 in | ||
| 53 | the Chandeleur Islands, LA. At each sampling location, water depth was | 53 | the Chandeleur Islands, LA. At each sampling location, water depth was | ||
| 54 | measured and density differences between marsh plants (Spartina | 54 | measured and density differences between marsh plants (Spartina | ||
| 55 | shoots) and black mangrove pneumatophores were also quantified. | 55 | shoots) and black mangrove pneumatophores were also quantified. | ||
| 56 | Macrofauna were collected within 1 m of the plant/water interface, | 56 | Macrofauna were collected within 1 m of the plant/water interface, | ||
| 57 | which is the area known to harbor high organism abundances in salt | 57 | which is the area known to harbor high organism abundances in salt | ||
| 58 | marsh systems. We haphazardly tossed three 0.17 m^2 plastic cylinders | 58 | marsh systems. We haphazardly tossed three 0.17 m^2 plastic cylinders | ||
| 59 | in each plot, whose lower edge was embedded in the sediment. The | 59 | in each plot, whose lower edge was embedded in the sediment. The | ||
| 60 | contents of the cylinders were collected using a gasoline-powered | 60 | contents of the cylinders were collected using a gasoline-powered | ||
| 61 | suction pump and all material was retained in a 0.5 mm mesh collection | 61 | suction pump and all material was retained in a 0.5 mm mesh collection | ||
| 62 | bag. Following collection, samples were removed from the bag and | 62 | bag. Following collection, samples were removed from the bag and | ||
| 63 | rinsed over a 0.5 mm sieve to remove any extraneous material, then | 63 | rinsed over a 0.5 mm sieve to remove any extraneous material, then | ||
| 64 | were placed on ice and frozen. Animals were later identified to the | 64 | were placed on ice and frozen. Animals were later identified to the | ||
| 65 | lowest practical taxonomic level. Portunid crabs and penaeid shrimp | 65 | lowest practical taxonomic level. Portunid crabs and penaeid shrimp | ||
| 66 | were measured for total length. Biomass (DW = dry weight, \u00b1 | 66 | were measured for total length. Biomass (DW = dry weight, \u00b1 | ||
| 67 | 0.0001 g) was determined by drying organisms at 70\u00b0C to a | 67 | 0.0001 g) was determined by drying organisms at 70\u00b0C to a | ||
| 68 | constant weight. Samples were then muffled at 500\u00b0C to obtain ash | 68 | constant weight. Samples were then muffled at 500\u00b0C to obtain ash | ||
| 69 | weight (AW, \u00b1 0.0001 g). Ash-free dry weight was calculated as | 69 | weight (AW, \u00b1 0.0001 g). Ash-free dry weight was calculated as | ||
| 70 | DW-AW. Samples were placed in a desiccator to cool before any weights | 70 | DW-AW. Samples were placed in a desiccator to cool before any weights | ||
| 71 | were recorded.\n\n### Purpose\nThe purpose of this field study was to | 71 | were recorded.\n\n### Purpose\nThe purpose of this field study was to | ||
| 72 | evaluate any lasting impacts of the Deepwater Horizon oil spill on | 72 | evaluate any lasting impacts of the Deepwater Horizon oil spill on | ||
| 73 | relative abundances and community composition of salt marsh and | 73 | relative abundances and community composition of salt marsh and | ||
| 74 | mangrove macrofaunal communities in the Chandeleur Islands, | 74 | mangrove macrofaunal communities in the Chandeleur Islands, | ||
| 75 | LA\n\n**DOI: | 75 | LA\n\n**DOI: | ||
| 76 | [doi:10.7266/N7B8565W](https://www.doi.org/10.7266/N7B8565W)**\n\n### | 76 | [doi:10.7266/N7B8565W](https://www.doi.org/10.7266/N7B8565W)**\n\n### | ||
| 77 | Suggested Citation\nHeck, Kenneth. 2017. The effects of oiling on salt | 77 | Suggested Citation\nHeck, Kenneth. 2017. The effects of oiling on salt | ||
| 78 | marsh and mangrove macrofauna communities at the Chandeleur Islands, | 78 | marsh and mangrove macrofauna communities at the Chandeleur Islands, | ||
| 79 | LA (June and September 2015). Distributed by: Gulf of Mexico Research | 79 | LA (June and September 2015). Distributed by: Gulf of Mexico Research | ||
| 80 | Initiative Information and Data Cooperative (GRIIDC), Harte Research | 80 | Initiative Information and Data Cooperative (GRIIDC), Harte Research | ||
| 81 | Institute, Texas A&M University\u2013Corpus Christi. | 81 | Institute, Texas A&M University\u2013Corpus Christi. | ||
| 82 | doi:10.7266/N7B8565W\n\n**Funded by:** Gulf of Mexico Research | 82 | doi:10.7266/N7B8565W\n\n**Funded by:** Gulf of Mexico Research | ||
| 83 | Initiative (GoMRI)\n\n**Funding cycle:** RFP-IV\n\n**Research group:** | 83 | Initiative (GoMRI)\n\n**Funding cycle:** RFP-IV\n\n**Research group:** | ||
| 84 | Alabama Center for Ecological Resilience (ACER)\n\n", | 84 | Alabama Center for Ecological Resilience (ACER)\n\n", | ||
| 85 | "num_resources": 7, | 85 | "num_resources": 7, | ||
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| 91 | become a center for transformative U.S. oceanic and coastal research | ||||
| 92 | and education.. Founded in 1971 by the State of Alabama Legislature to | ||||
| 93 | maximize the marine sciences capabilities of several Alabama | ||||
| 94 | institutions and minimize duplication. \r\n\r\nLocated on the eastern | ||||
| 95 | tip of Dauphin Island, a barrier island in the northern Gulf of | ||||
| 96 | Mexico, DISL is surrounded by Mobile Bay, the Mississippi Sound, and | ||||
| 97 | the waters of the Gulf, making it a perfect location to conduct a wide | ||||
| 98 | range of marine science activity. \r\n\r\n[The University Programs | ||||
| 99 | (UP)](https://www.disl.edu/univ-prog/) serves the students of the | ||||
| 100 | Marine Environmental Sciences Consortium\u2019s (MESC) 22 public and | ||||
| 101 | private four-year colleges and universities through graduate and | ||||
| 102 | undergraduate programs. Throughout the year, graduate students conduct | ||||
| 103 | research, and attend classes while completing their degree under the | ||||
| 104 | mentorship of faculty and staff at the Dauphin Island Sea Lab. | ||||
| 105 | \r\n\r\n[The Discovery Hall Programs (DHP)](https://www.disl.edu/dhp/) | ||||
| 106 | oversees educational programs for K-12 field programs, | ||||
| 107 | teacher-training, and community outreach opportunities. \r\n[The | ||||
| 108 | Estuarium](https://www.disl.edu/aquarium/), our public aquarium | ||||
| 109 | located on the Dauphin Island Sea Lab campus, is a part of DHP's | ||||
| 110 | educational outreach mission. The Estuarium focuses solely on the | ||||
| 111 | Mobile-Tensaw Estuary System. The BayMobile allows DHP educators to | ||||
| 112 | bring marine science to students across Alabama in the classroom and | ||||
| 113 | at community events. \r\n\r\nResearch programs at the Dauphin Island | ||||
| 114 | Sea Lab range from biogeochemistry and oceanography to ecosystem | ||||
| 115 | ecology. While much of our research focuses on the near-shore and | ||||
| 116 | estuarine processes of the northern Gulf of Mexico, field sites of our | ||||
| 117 | internationally-renowned faculty also include the Arctic, Mexico, | ||||
| 118 | Australia, and other countries.\r\n\r\nThe Dauphin Island Sea Lab also | ||||
| 119 | offers state and local government, industry, and agency | ||||
| 120 | decision-makers a range of coastal zone management services, including | ||||
| 121 | access to the nationally acclaimed data management center. Armed with | ||||
| 122 | data through the DISL data management center, entities can make | ||||
| 123 | well-informed decisions and sound policies while considering | ||||
| 124 | environmental impact. Another key contributor to successful coastal | ||||
| 125 | zone management is the Mobile Bay National Estuary Program, which | ||||
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