Changes
On July 27, 2022 at 2:38:44 PM UTC, 87c31ae9-4db0-41e4-958b-b38aa813b77a:
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Added the following fields to resource Macrofauna_rawabundance_ChandeleurIsland_2015.csv in The effects of oiling on salt marsh and mangrove macrofauna communities at the Chandeleur Islands, LA (June and September 2015)
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original_url with value
resource_id with value
task_created with value
set_url_type with value
ignore_hash with value
ckan_url with value
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Changed value of field
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toTrue
in resource Macrofauna_rawabundance_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
datastore_contains_all_records_of_source_file
toTrue
in resource Macrofauna_rawabundance_ChandeleurIsland_2015.csv 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 | ], | ||
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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": "2022-07-27T14:38:39.025705", | n | 47 | "metadata_modified": "2022-07-27T14:38:43.971480", |
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", | ||
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89 | "created": "2022-07-22T03:25:13.329710", | 89 | "created": "2022-07-22T03:25:13.329710", | ||
90 | "description": "The Dauphin Island Sea Lab organization.", | 90 | "description": "The Dauphin Island Sea Lab organization.", | ||
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96 | "title": "Dauphin Island Sea Lab", | 96 | "title": "Dauphin Island Sea Lab", | ||
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