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of resource Macrofauna_totallength_ChandeleurIsland_2016.csv to2022-10-10 21:15:23.873669
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) in The effects of oiling on salt marsh and mangrove macrofauna communities at the Chandeleur Islands, LA (June and September 2016) -
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in resource Macrofauna_totallength_ChandeleurIsland_2016.csv in The effects of oiling on salt marsh and mangrove macrofauna communities at the Chandeleur Islands, LA (June and September 2016)
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/N7M32SVH" | 8 | "value": "doi:10.7266/N7M32SVH" | ||
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": "2016-06-13" | 21 | "value": "2016-06-13" | ||
22 | }, | 22 | }, | ||
23 | { | 23 | { | ||
24 | "key": "Temporal End", | 24 | "key": "Temporal End", | ||
25 | "value": "2016-09-16" | 25 | "value": "2016-09-16" | ||
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, 29.93216 ], [ -88.82712, 29.93216 ], [ -88.82712, 29.86356 | 35 | -88.84114, 29.93216 ], [ -88.82712, 29.93216 ], [ -88.82712, 29.86356 | ||
36 | ], [ -88.84114, 29.86356 ], [ -88.84114, 29.93216 ] ] ] }" | 36 | ], [ -88.84114, 29.86356 ], [ -88.84114, 29.93216 ] ] ] }" | ||
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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": "2022-07-27T14:33:20.202498", | 46 | "metadata_created": "2022-07-27T14:33:20.202498", | ||
n | 47 | "metadata_modified": "2022-10-10T21:23:04.447490", | n | 47 | "metadata_modified": "2022-10-10T21:23:06.837633", |
48 | "name": | 48 | "name": | ||
49 | rsh-and-mangrove-macrofauna-communities-at-the-chandeleur-isn7m32svh", | 49 | rsh-and-mangrove-macrofauna-communities-at-the-chandeleur-isn7m32svh", | ||
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 September) in 2016 in | 52 | at high tide during the growing season (June and September) in 2016 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/N7M32SVH](https://www.doi.org/10.7266/N7M32SVH)**\n\n### | 76 | [doi:10.7266/N7M32SVH](https://www.doi.org/10.7266/N7M32SVH)**\n\n### | ||
77 | Suggested Citation\nKen Heck. 2017. The effects of oiling on salt | 77 | Suggested Citation\nKen Heck. 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 2016). Distributed by: Gulf of Mexico Research | 79 | LA (June and September 2016). 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/N7M32SVH\n\n**Funded by:** Gulf of Mexico Research | 82 | doi:10.7266/N7M32SVH\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": 6, | 85 | "num_resources": 6, | ||
86 | "num_tags": 0, | 86 | "num_tags": 0, | ||
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90 | "description": "The Dauphin Island Sea Lab's (DISL) mission is to | 90 | "description": "The Dauphin Island Sea Lab's (DISL) mission is to | ||
91 | become a center for transformative U.S. oceanic and coastal research | 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 | 92 | and education.. Founded in 1971 by the State of Alabama Legislature to | ||
93 | maximize the marine sciences capabilities of several Alabama | 93 | maximize the marine sciences capabilities of several Alabama | ||
94 | institutions and minimize duplication. \r\n\r\nLocated on the eastern | 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 | 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 | 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 | 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 | 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 | 99 | (UP)](https://www.disl.edu/univ-prog/) serves the students of the | ||
100 | Marine Environmental Sciences Consortium\u2019s (MESC) 22 public and | 100 | Marine Environmental Sciences Consortium\u2019s (MESC) 22 public and | ||
101 | private four-year colleges and universities through graduate and | 101 | private four-year colleges and universities through graduate and | ||
102 | undergraduate programs. Throughout the year, graduate students conduct | 102 | undergraduate programs. Throughout the year, graduate students conduct | ||
103 | research, and attend classes while completing their degree under the | 103 | research, and attend classes while completing their degree under the | ||
104 | mentorship of faculty and staff at the Dauphin Island Sea Lab. | 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/) | 105 | \r\n\r\n[The Discovery Hall Programs (DHP)](https://www.disl.edu/dhp/) | ||
106 | oversees educational programs for K-12 field programs, | 106 | oversees educational programs for K-12 field programs, | ||
107 | teacher-training, and community outreach opportunities. \r\n[The | 107 | teacher-training, and community outreach opportunities. \r\n[The | ||
108 | Estuarium](https://www.disl.edu/aquarium/), our public aquarium | 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 | 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 | 110 | educational outreach mission. The Estuarium focuses solely on the | ||
111 | Mobile-Tensaw Estuary System. The BayMobile allows DHP educators to | 111 | Mobile-Tensaw Estuary System. The BayMobile allows DHP educators to | ||
112 | bring marine science to students across Alabama in the classroom and | 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 | 113 | at community events. \r\n\r\nResearch programs at the Dauphin Island | ||
114 | Sea Lab range from biogeochemistry and oceanography to ecosystem | 114 | Sea Lab range from biogeochemistry and oceanography to ecosystem | ||
115 | ecology. While much of our research focuses on the near-shore and | 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 | 116 | estuarine processes of the northern Gulf of Mexico, field sites of our | ||
117 | internationally-renowned faculty also include the Arctic, Mexico, | 117 | internationally-renowned faculty also include the Arctic, Mexico, | ||
118 | Australia, and other countries.\r\n\r\nThe Dauphin Island Sea Lab also | 118 | Australia, and other countries.\r\n\r\nThe Dauphin Island Sea Lab also | ||
119 | offers state and local government, industry, and agency | 119 | offers state and local government, industry, and agency | ||
120 | decision-makers a range of coastal zone management services, including | 120 | decision-makers a range of coastal zone management services, including | ||
121 | access to the nationally acclaimed data management center. Armed with | 121 | access to the nationally acclaimed data management center. Armed with | ||
122 | data through the DISL data management center, entities can make | 122 | data through the DISL data management center, entities can make | ||
123 | well-informed decisions and sound policies while considering | 123 | well-informed decisions and sound policies while considering | ||
124 | environmental impact. Another key contributor to successful coastal | 124 | environmental impact. Another key contributor to successful coastal | ||
125 | zone management is the Mobile Bay National Estuary Program, which | 125 | zone management is the Mobile Bay National Estuary Program, which | ||
126 | falls within the services of DISL.\r\n\r\n", | 126 | falls within the services of DISL.\r\n\r\n", | ||
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