Changes
On October 10, 2022 at 9:20:25 PM UTC, c17a0114-fe1c-4191-986b-40c4b31b670a:
-
Removed the following tags from Effects of oil exposure on multiple predator effects in coastal food webs, a mesocosm study from 2017-09-18 to 2017-12-04
- Callinectes sapidus
- Gulf toadfish
- Hardhead catfish
- Fundulus grandis
- polycyclic aromatic hydrocarbons PAH
- Fundulus xenicus
- Palaemonetes
- Opsanus beta
- Blue crab
- Biodiversity
- total petroleum hydrocarbons TPH
- Grass shrimp
- Ariopsis felis
- Gulf killifish
- Emergent Effects
- Ecosystem Resiliency
- Multiple Predator Effects
- Predator-prey interactions
- oil exposure
- Replacement Design
- Diamond killifish
-
Changed value of field
ignore_hash
toTrue
in resource Oil Biodiversity Recovery.csv in Effects of oil exposure on multiple predator effects in coastal food webs, a mesocosm study from 2017-09-18 to 2017-12-04 -
Changed value of field
task_created
of resource Oil Biodiversity Recovery.csv to2022-10-10 21:15:15.438322
(previously2022-07-27 14:34:26.303222
) in Effects of oil exposure on multiple predator effects in coastal food webs, a mesocosm study from 2017-09-18 to 2017-12-04
f | 1 | { | f | 1 | { |
2 | "author": "John Valentine", | 2 | "author": "John Valentine", | ||
3 | "author_email": "jvalentine@disl.org", | 3 | "author_email": "jvalentine@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/n7-s9jq-n263" | 8 | "value": "doi:10.7266/n7-s9jq-n263" | ||
9 | }, | 9 | }, | ||
10 | { | 10 | { | ||
11 | "key": "ISO.pointOfContact", | 11 | "key": "ISO.pointOfContact", | ||
12 | "value": "John Valentine <jvalentine@disl.org>" | 12 | "value": "John Valentine <jvalentine@disl.org>" | ||
13 | }, | 13 | }, | ||
14 | { | 14 | { | ||
15 | "key": "Theme Keywords", | 15 | "key": "Theme Keywords", | ||
16 | "value": "Predator-prey interactions, oil exposure, | 16 | "value": "Predator-prey interactions, oil exposure, | ||
17 | Biodiversity, Multiple Predator Effects, Ecosystem Resiliency, | 17 | Biodiversity, Multiple Predator Effects, Ecosystem Resiliency, | ||
18 | Replacement Design, Emergent Effects, Hardhead catfish, Ariopsis | 18 | Replacement Design, Emergent Effects, Hardhead catfish, Ariopsis | ||
19 | felis, Diamond killifish, Fundulus xenicus, Callinectes sapidus, Gulf | 19 | felis, Diamond killifish, Fundulus xenicus, Callinectes sapidus, Gulf | ||
20 | killifish, Fundulus grandis, Grass shrimp, Palaemonetes, Opsanus beta, | 20 | killifish, Fundulus grandis, Grass shrimp, Palaemonetes, Opsanus beta, | ||
21 | Gulf toadfish, total petroleum hydrocarbons (TPH), polycyclic aromatic | 21 | Gulf toadfish, total petroleum hydrocarbons (TPH), polycyclic aromatic | ||
22 | hydrocarbons (PAH), Blue crab" | 22 | hydrocarbons (PAH), Blue crab" | ||
23 | } | 23 | } | ||
24 | ], | 24 | ], | ||
25 | "groups": [], | 25 | "groups": [], | ||
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27 | "isopen": false, | 27 | "isopen": false, | ||
28 | "license_id": null, | 28 | "license_id": null, | ||
29 | "license_title": null, | 29 | "license_title": null, | ||
30 | "maintainer": "data@disl.org", | 30 | "maintainer": "data@disl.org", | ||
31 | "maintainer_email": "data@disl.org", | 31 | "maintainer_email": "data@disl.org", | ||
32 | "metadata_created": "2022-07-27T14:34:24.943728", | 32 | "metadata_created": "2022-07-27T14:34:24.943728", | ||
n | 33 | "metadata_modified": "2022-07-27T14:37:54.638017", | n | 33 | "metadata_modified": "2022-10-10T21:20:25.434979", |
34 | "name": | 34 | "name": | ||
35 | ple-predator-effects-in-coastal-food-webs-a-mesocosm-stun7-s9jq-n263", | 35 | ple-predator-effects-in-coastal-food-webs-a-mesocosm-stun7-s9jq-n263", | ||
36 | "notes": "### Abstract\nThis collection of datasets was generated | 36 | "notes": "### Abstract\nThis collection of datasets was generated | ||
37 | from mesocosm experiments conducted from September to December 2017 to | 37 | from mesocosm experiments conducted from September to December 2017 to | ||
38 | examine the effects of oil exposure on trophic interactions of fish | 38 | examine the effects of oil exposure on trophic interactions of fish | ||
39 | and crustaceans in the northern Gulf of Mexico. Four predator species | 39 | and crustaceans in the northern Gulf of Mexico. Four predator species | ||
40 | were used in this experiment: hardhead catfish (Ariopsis felis), Gulf | 40 | were used in this experiment: hardhead catfish (Ariopsis felis), Gulf | ||
41 | killifish (Fundulus grandis), Gulf toadfish (Opsanus beta), and adult | 41 | killifish (Fundulus grandis), Gulf toadfish (Opsanus beta), and adult | ||
42 | blue crabs (Callinectes sapidus). Prey assemblages composed of 3 | 42 | blue crabs (Callinectes sapidus). Prey assemblages composed of 3 | ||
43 | common prey species (diamond killifish (Fundulus xenicus), juvenile | 43 | common prey species (diamond killifish (Fundulus xenicus), juvenile | ||
44 | blue crabs (C. sapidus), and grass shrimp (Palaemonetes spp.)) were | 44 | blue crabs (C. sapidus), and grass shrimp (Palaemonetes spp.)) were | ||
45 | exposed to predator assemblages composed of 4 individuals from a | 45 | exposed to predator assemblages composed of 4 individuals from a | ||
46 | single species (monoculture), from two species (2 individuals from | 46 | single species (monoculture), from two species (2 individuals from | ||
47 | each species), or from four species (1 individual from each species) | 47 | each species), or from four species (1 individual from each species) | ||
48 | to manipulate potential effects of predator diversity. Experimental | 48 | to manipulate potential effects of predator diversity. Experimental | ||
49 | replicates were run in pairs consisting of 1 oiled tank and 1 un-oiled | 49 | replicates were run in pairs consisting of 1 oiled tank and 1 un-oiled | ||
50 | tank. Oiled tanks were inoculated at the initiation of each experiment | 50 | tank. Oiled tanks were inoculated at the initiation of each experiment | ||
51 | and 24 hours after initiation. Water samples were collected from oiled | 51 | and 24 hours after initiation. Water samples were collected from oiled | ||
52 | and un-oiled tanks one hour after each inoculation and at the | 52 | and un-oiled tanks one hour after each inoculation and at the | ||
53 | termination of the experiment from 5 randomly selected replicate pairs | 53 | termination of the experiment from 5 randomly selected replicate pairs | ||
54 | to measure the concentration of total petroleum hydrocarbons (TPH) and | 54 | to measure the concentration of total petroleum hydrocarbons (TPH) and | ||
55 | polycyclic aromatic hydrocarbons (PAH) in the water. Prey survival was | 55 | polycyclic aromatic hydrocarbons (PAH) in the water. Prey survival was | ||
56 | recorded at the end of each 48-hour replicate.\n\n### Purpose\nThese | 56 | recorded at the end of each 48-hour replicate.\n\n### Purpose\nThese | ||
57 | datasets show the results of an experiment examining the effects of | 57 | datasets show the results of an experiment examining the effects of | ||
58 | oil exposure on trophic interactions of common Gulf of Mexico. | 58 | oil exposure on trophic interactions of common Gulf of Mexico. | ||
59 | Analysis of these data will examine the role of biodiversity in | 59 | Analysis of these data will examine the role of biodiversity in | ||
60 | ecosystem resiliency to large scale disturbances, such as oil | 60 | ecosystem resiliency to large scale disturbances, such as oil | ||
61 | spills.\n\n**DOI: | 61 | spills.\n\n**DOI: | ||
62 | .7266/n7-s9jq-n263](https://www.doi.org/10.7266/n7-s9jq-n263)**\n\n### | 62 | .7266/n7-s9jq-n263](https://www.doi.org/10.7266/n7-s9jq-n263)**\n\n### | ||
63 | Suggested Citation\nValentine, John F.; Martin, Charles W.; Alford, | 63 | Suggested Citation\nValentine, John F.; Martin, Charles W.; Alford, | ||
64 | Scott B.. 2019. Effects of oil exposure on multiple predator effects | 64 | Scott B.. 2019. Effects of oil exposure on multiple predator effects | ||
65 | in coastal food webs, a mesocosm study from 2017-09-18 to 2017-12-04. | 65 | in coastal food webs, a mesocosm study from 2017-09-18 to 2017-12-04. | ||
66 | Distributed by: Gulf of Mexico Research Initiative Information and | 66 | Distributed by: Gulf of Mexico Research Initiative Information and | ||
67 | Data Cooperative (GRIIDC), Harte Research Institute, Texas A&M | 67 | Data Cooperative (GRIIDC), Harte Research Institute, Texas A&M | ||
68 | University\u2013Corpus Christi. doi:10.7266/n7-s9jq-n263\n\n**Funded | 68 | University\u2013Corpus Christi. doi:10.7266/n7-s9jq-n263\n\n**Funded | ||
69 | by:** Gulf of Mexico Research Initiative (GoMRI)\n\n**Funding cycle:** | 69 | by:** Gulf of Mexico Research Initiative (GoMRI)\n\n**Funding cycle:** | ||
70 | RFP-IV\n\n**Research group:** Alabama Center for Ecological Resilience | 70 | RFP-IV\n\n**Research group:** Alabama Center for Ecological Resilience | ||
71 | (ACER)\n\n", | 71 | (ACER)\n\n", | ||
72 | "num_resources": 6, | 72 | "num_resources": 6, | ||
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75 | "approval_status": "approved", | 75 | "approval_status": "approved", | ||
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n | 77 | "description": "The Dauphin Island Sea Lab organization.", | n | 77 | "description": "The Dauphin Island Sea Lab's (DISL) mission is to |
78 | become a center for transformative U.S. oceanic and coastal research | ||||
79 | and education.. Founded in 1971 by the State of Alabama Legislature to | ||||
80 | maximize the marine sciences capabilities of several Alabama | ||||
81 | institutions and minimize duplication. \r\n\r\nLocated on the eastern | ||||
82 | tip of Dauphin Island, a barrier island in the northern Gulf of | ||||
83 | Mexico, DISL is surrounded by Mobile Bay, the Mississippi Sound, and | ||||
84 | the waters of the Gulf, making it a perfect location to conduct a wide | ||||
85 | range of marine science activity. \r\n\r\n[The University Programs | ||||
86 | (UP)](https://www.disl.edu/univ-prog/) serves the students of the | ||||
87 | Marine Environmental Sciences Consortium\u2019s (MESC) 22 public and | ||||
88 | private four-year colleges and universities through graduate and | ||||
89 | undergraduate programs. Throughout the year, graduate students conduct | ||||
90 | research, and attend classes while completing their degree under the | ||||
91 | mentorship of faculty and staff at the Dauphin Island Sea Lab. | ||||
92 | \r\n\r\n[The Discovery Hall Programs (DHP)](https://www.disl.edu/dhp/) | ||||
93 | oversees educational programs for K-12 field programs, | ||||
94 | teacher-training, and community outreach opportunities. \r\n[The | ||||
95 | Estuarium](https://www.disl.edu/aquarium/), our public aquarium | ||||
96 | located on the Dauphin Island Sea Lab campus, is a part of DHP's | ||||
97 | educational outreach mission. The Estuarium focuses solely on the | ||||
98 | Mobile-Tensaw Estuary System. The BayMobile allows DHP educators to | ||||
99 | bring marine science to students across Alabama in the classroom and | ||||
100 | at community events. \r\n\r\nResearch programs at the Dauphin Island | ||||
101 | Sea Lab range from biogeochemistry and oceanography to ecosystem | ||||
102 | ecology. While much of our research focuses on the near-shore and | ||||
103 | estuarine processes of the northern Gulf of Mexico, field sites of our | ||||
104 | internationally-renowned faculty also include the Arctic, Mexico, | ||||
105 | Australia, and other countries.\r\n\r\nThe Dauphin Island Sea Lab also | ||||
106 | offers state and local government, industry, and agency | ||||
107 | decision-makers a range of coastal zone management services, including | ||||
108 | access to the nationally acclaimed data management center. Armed with | ||||
109 | data through the DISL data management center, entities can make | ||||
110 | well-informed decisions and sound policies while considering | ||||
111 | environmental impact. Another key contributor to successful coastal | ||||
112 | zone management is the Mobile Bay National Estuary Program, which | ||||
113 | falls within the services of DISL.\r\n\r\n", | ||||
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