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Row Type | Variable Name | Attribute Name | Data Type | Value |
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attribute | NC_GLOBAL | access_formats | String | .htmlTable,.csv,.json,.mat,.nc,.tsv |
attribute | NC_GLOBAL | acquisition_description | String | The study was conducted from November 2010 through February 2011 and between\nNovember 2011 and January 2012 on shallow (~1 m below the surface at low tide,\nequal or shallower than 2 m at high tide), intertidal fringing reefs platforms\n(up to 800-m wide) along the Coral Coast (18\\u00ba\\u00a013.05\\u2019S,\n177\\u00ba\\u00a042.97\\u2019E) of Viti Levu, Fiji\\u2019s main island. Many of\nthe owners of traditional fishing rights along the Coral Coast have\nestablished small, customary no-take MPAs to improve and sustain their\nadjacent fishing grounds. The MPAs in this region are delimited by surface\nmarkings and enforced by local villagers, and they have been closed to all\nfishing activities since their inception (about 10 years). The only exception\nto this closure was a small experimental hook and line fishing research\nproject that was conducted in the MPAs of Votua and\\u00a0Namada. In the\n\\u00a0non-MPAs, the main fishing targets are species of Acanthuridae\n(Nasinae), Epinephelidae, Labridae, Mullidae, and Lutjanidae. Permission for\nthe research was granted by the Fijian Ministry of Education, National\nHeritage, Culture & Arts, Youth & Sports, which is authorized to approve field\nstudies in Fijian waters. No animal collection or experimental procedures\ninvolving animals were conducted during the study, and no endangered species\nwere recorded during our assessments.\\u00a0\n \nTo assess the effects of MPAs on fish assemblages, fish feeding group\ncomposition, herbivory rates, benthic cover, and coral recruit density, we\ncompared three spatially paired MPA and adjacent, fished, areas (non-MPAs)\nassociated with the villages of\nVotua,\\u00a0Vatu-o-lalai\\u00a0and\\u00a0Namada.\\u00a0 Comparisons of fish\nassemblages inside and outside of closures are widely used for determining the\neffects of reserves, but it should be acknowledged that this approach does not\nreveal the state of an MPA relative to an undisturbed baseline.\\u00a0\n \nThe studied MPAs were established in 2002 (Vatu-o-lalai,\\u00a0Namada) and 2003\n(Votua), and shortly after establishment, coral cover was low (~7%),\nand\\u00a0macroalgal\\u00a0cover was high (~35\\u201345%) in both the MPAs and\n\\u00a0non-MPAs. All surveys and assays were conducted during the same season\n(austral summer) to minimize seasonal variation in sampling. The reef extends\napprox. 1 km from shore within each MPA and\\u00a0non-MPA,\\u00a0and all data\nwere collected between 30 and 700 m of the shore (i.e., shoreward of the reef\ncrest) parallel to the\\u00a0shoreline.\n \nFish assemblages: Underwater visual censuses (UVC) were used to assess fish\nassemblages in MPAs and non-MPAs at the three village sites. Underwater\nvisibility at all study sites (> 15 m) was appropriate for the use of UVC, but\ndue to the visual limitations of this method, we did not consider cryptic\nspecies or species with a maximum total length < 5 cm. During our surveys, we\ncategorized species into two major categories (Herbivores and Non-herbivores)\nthat were subdivided into ten sub-categories. Herbivores include the main\nroving nominally herbivorous fish clades, which play an important role in the\ncontrol of benthic algae, and these species were further divided into four\nsub-categories (browsers, grazers, scrapers, and excavators) according to\ndiet, feeding mode, and impact on the benthos. The category of Non-herbivores\nincludes all species that feed on other, non-algal resources.\n \nSeparate 30m x 4m belt transects were performed for Herbivores and Non-\nherbivores. While simultaneously deploying the transect line, a snorkeler\nrecorded all non-cryptic fishes (either Herbivores or Non-herbivores) within 2\nm of either side of the transect. Individual fish were identified to species\nand placed into 5-cm (total length) size classes, and the lengths were\nconverted to biomass using established length-weight relationships.\\u00a0\n \nTransects were conducted in each area within 2 h of high tide (approx. 1.5 m\ndepth) and were equally distributed between the two sampling periods (Dec\n2010\\u2013Jan 2011 and Dec 2011\\u2013Jan 2012), the months within each sampled\nyear (December and January of each year). On each sampling day, four to six\ntransects were deployed on the reef parallel to the shoreline, with a minimum\nof 10m between adjacent transects. To ensure that transects were independent\nand non-overlapping, small numbered surface floats were placed at the start\nand end of each transect, and were left in position during all sampling. Care\nwas taken to avoid re-counting fishes that left and subsequently re-entered\nthe transect areas. The initial starting point of the transects for each day\nwas selected based on a map of the study sites with two constraints: (1) as to\na minimum distance from shore\\u00a0(at least 30 m), and a minimum distance\nfrom the MPA boundaries\\u00a0(150 m).\\u00a0 |
attribute | NC_GLOBAL | awards_0_award_nid | String | 480718 |
attribute | NC_GLOBAL | awards_0_award_number | String | OCE-0929119 |
attribute | NC_GLOBAL | awards_0_data_url | String | http://www.nsf.gov/awardsearch/showAward?AWD_ID=0929119 |
attribute | NC_GLOBAL | awards_0_funder_name | String | NSF Division of Ocean Sciences |
attribute | NC_GLOBAL | awards_0_funding_acronym | String | NSF OCE |
attribute | NC_GLOBAL | awards_0_funding_source_nid | String | 355 |
attribute | NC_GLOBAL | awards_0_program_manager | String | David L. Garrison |
attribute | NC_GLOBAL | awards_0_program_manager_nid | String | 50534 |
attribute | NC_GLOBAL | awards_1_award_nid | String | 674109 |
attribute | NC_GLOBAL | awards_1_award_number | String | U01-TW007401 |
attribute | NC_GLOBAL | awards_1_data_url | String | https://projectreporter.nih.gov/project_info_description.cfm?icde=0&aid=7741942 |
attribute | NC_GLOBAL | awards_1_funder_name | String | National Institutes of Health |
attribute | NC_GLOBAL | awards_1_funding_acronym | String | NIH |
attribute | NC_GLOBAL | awards_1_funding_source_nid | String | 636502 |
attribute | NC_GLOBAL | awards_1_program_manager | String | Flora Katz |
attribute | NC_GLOBAL | awards_1_program_manager_nid | String | 674108 |
attribute | NC_GLOBAL | cdm_data_type | String | Other |
attribute | NC_GLOBAL | comment | String | M. Hay \n Species Richness \n Version 6 January 2017 |
attribute | NC_GLOBAL | Conventions | String | COARDS, CF-1.6, ACDD-1.3 |
attribute | NC_GLOBAL | creator_email | String | info at bco-dmo.org |
attribute | NC_GLOBAL | creator_name | String | BCO-DMO |
attribute | NC_GLOBAL | creator_type | String | institution |
attribute | NC_GLOBAL | creator_url | String | https://www.bco-dmo.org/ |
attribute | NC_GLOBAL | data_source | String | extract_data_as_tsv version 2.3 19 Dec 2019 |
attribute | NC_GLOBAL | date_created | String | 2017-01-07T00:48:25Z |
attribute | NC_GLOBAL | date_modified | String | 2019-04-05T15:15:50Z |
attribute | NC_GLOBAL | defaultDataQuery | String | &time<now |
attribute | NC_GLOBAL | doi | String | 10.1575/1912/bco-dmo.674172.1 |
attribute | NC_GLOBAL | infoUrl | String | https://www.bco-dmo.org/dataset/674172 |
attribute | NC_GLOBAL | institution | String | BCO-DMO |
attribute | NC_GLOBAL | keywords | String | bco, bco-dmo, biological, chemical, data, dataset, day, dmo, erddap, management, oceanography, office, preliminary, site, species, status, transect, type, year |
attribute | NC_GLOBAL | license | String | https://www.bco-dmo.org/dataset/674172/license |
attribute | NC_GLOBAL | metadata_source | String | https://www.bco-dmo.org/api/dataset/674172 |
attribute | NC_GLOBAL | param_mapping | String | {'674172': {}} |
attribute | NC_GLOBAL | parameter_source | String | https://www.bco-dmo.org/mapserver/dataset/674172/parameters |
attribute | NC_GLOBAL | people_0_affiliation | String | Georgia Institute of Technology |
attribute | NC_GLOBAL | people_0_affiliation_acronym | String | Georgia Tech |
attribute | NC_GLOBAL | people_0_person_name | String | Mark Hay |
attribute | NC_GLOBAL | people_0_person_nid | String | 480720 |
attribute | NC_GLOBAL | people_0_role | String | Principal Investigator |
attribute | NC_GLOBAL | people_0_role_type | String | originator |
attribute | NC_GLOBAL | people_1_affiliation | String | Woods Hole Oceanographic Institution |
attribute | NC_GLOBAL | people_1_affiliation_acronym | String | WHOI BCO-DMO |
attribute | NC_GLOBAL | people_1_person_name | String | Hannah Ake |
attribute | NC_GLOBAL | people_1_person_nid | String | 650173 |
attribute | NC_GLOBAL | people_1_role | String | BCO-DMO Data Manager |
attribute | NC_GLOBAL | people_1_role_type | String | related |
attribute | NC_GLOBAL | project | String | Killer Seaweeds |
attribute | NC_GLOBAL | projects_0_acronym | String | Killer Seaweeds |
attribute | NC_GLOBAL | projects_0_description | String | Extracted from the NSF award abstract:\nCoral reefs are in dramatic global decline, with reefs commonly converting from species-rich and topographically-complex communities dominated by corals to species- poor and topographically-simplified communities dominated by seaweeds. These phase-shifts result in fundamental loss of ecosystem function. Despite debate about whether coral-to-algal transitions are commonly a primary cause, or simply a consequence, of coral mortality, rigorous field investigation of seaweed-coral competition has received limited attention. There is limited information on how the outcome of seaweed-coral competition varies among species or the relative importance of different competitive mechanisms in facilitating seaweed dominance. In an effort to address this topic, the PI will conduct field experiments in the tropical South Pacific (Fiji) to determine the effects of seaweeds on corals when in direct contact, which seaweeds are most damaging to corals, the role allelopathic lipids that are transferred via contact in producing these effects, the identity and surface concentrations of these metabolites, and the dynamic nature of seaweed metabolite production and coral response following contact. The herbivorous fishes most responsible for controlling allelopathic seaweeds will be identified, the roles of seaweed metabolites in allelopathy vs herbivore deterrence will be studied, and the potential for better managing and conserving critical reef herbivores so as to slow or reverse conversion of coral reef to seaweed meadows will be examined.\nPreliminary results indicate that seaweeds may commonly damage corals via lipid- soluble allelochemicals. Such chemically-mediated interactions could kill or damage adult corals and produce the suppression of coral fecundity and recruitment noted by previous investigators and could precipitate positive feedback mechanisms making reef recovery increasingly unlikely as seaweed abundance increases. Chemically-mediated seaweed-coral competition may play a critical role in the degradation of present-day coral reefs. Increasing information on which seaweeds are most aggressive to corals and which herbivores best limit these seaweeds may prove useful in better managing reefs to facilitate resilience and possible recovery despite threats of global-scale stresses. Fiji is well positioned to rapidly use findings from this project for better management of reef resources because it has already erected >260 MPAs, Fijian villagers have already bought-in to the value of MPAs, and the Fiji Locally-Managed Marine Area (FLMMA) Network is well organized to get information to villagers in a culturally sensitive and useful manner.\nThe broader impacts of this project are far reaching. The project provides training opportunities for 2-2.5 Ph.D students and 1 undergraduate student each year in the interdisciplinary areas of marine ecology, marine conservation, and marine chemical ecology. Findings from this project will be immediately integrated into classes at Ga Tech and made available throughout Fiji via a foundation and web site that have already set-up to support marine conservation efforts in Fiji and marine education efforts both within Fiji and internationally. Business and community leaders from Atlanta (via Rotary International Service efforts) have been recruited to help organize and fund community service and outreach projects in Fiji -- several of which are likely to involve marine conservation and education based in part on these efforts there. Media outlets (National Geographic, NPR, Animal Planet, Audubon Magazine, etc.) and local Rotary clubs will be used to better disseminate these discoveries to the public.\nPUBLICATIONS PRODUCED AS A RESULT OF THIS RESEARCH\nRasher DB, Stout EP, Engel S, Kubanek J, and ME Hay. \"Macroalgal terpenes function as allelopathic agents against reef corals\", Proceedings of the National Academy of Sciences, v. 108, 2011, p. 17726.\nBeattie AJ, ME Hay, B Magnusson, R de Nys, J Smeathers, JFV Vincent. \"Ecology and bioprospecting,\" Austral Ecology, v.36, 2011, p. 341.\nRasher DB and ME Hay. \"Seaweed allelopathy degrades the resilience and function of coral reefs,\" Communicative and Integrative Biology, v.3, 2010.\nHay ME, Rasher DB. \"Corals in crisis,\" The Scientist, v.24, 2010, p. 42.\nHay ME and DB Rasher. \"Coral reefs in crisis: reversing the biotic death spiral,\" Faculty 1000 Biology Reports 2010, v.2, 2010.\nRasher DB and ME Hay. \"Chemically rich seaweeds poison corals when not controlled by herbivores\", Proceedings of the National Academy of Sciences, v.107, 2010, p. 9683. |
attribute | NC_GLOBAL | projects_0_end_date | String | 2014-08 |
attribute | NC_GLOBAL | projects_0_geolocation | String | Viti Levu, Fiji (18º13.049’S, 177º42.968’E) |
attribute | NC_GLOBAL | projects_0_name | String | Killer Seaweeds: Allelopathy against Fijian Corals |
attribute | NC_GLOBAL | projects_0_project_nid | String | 480717 |
attribute | NC_GLOBAL | projects_0_start_date | String | 2009-09 |
attribute | NC_GLOBAL | publisher_name | String | Biological and Chemical Oceanographic Data Management Office (BCO-DMO) |
attribute | NC_GLOBAL | publisher_type | String | institution |
attribute | NC_GLOBAL | sourceUrl | String | (local files) |
attribute | NC_GLOBAL | standard_name_vocabulary | String | CF Standard Name Table v55 |
attribute | NC_GLOBAL | summary | String | Species richness in and out of MPAs in Viti Levu, Fiji from 2010-2012 (Killer Seaweeds project) |
attribute | NC_GLOBAL | title | String | [Species richness] - Species richness in and out of MPAs in Viti Levu, Fiji from 2010-2012 (Killer Seaweeds project) (Killer Seaweeds: Allelopathy against Fijian Corals) |
attribute | NC_GLOBAL | version | String | 1 |
attribute | NC_GLOBAL | xml_source | String | osprey2erddap.update_xml() v1.3 |
variable | type | String | ||
attribute | type | bcodmo_name | String | sample |
attribute | type | description | String | Category of fish assemblage sampled; Herbivores include the main roving nominally herbivorous fish clades; non-herbivores includes all species that feed on other, non-algal resources. |
attribute | type | long_name | String | Type |
attribute | type | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P02/current/ACYC/ |
attribute | type | units | String | unitless |
variable | site | String | ||
attribute | site | bcodmo_name | String | site |
attribute | site | description | String | Site name |
attribute | site | long_name | String | Site |
attribute | site | units | String | unitless |
variable | status | String | ||
attribute | status | bcodmo_name | String | site_descrip |
attribute | status | description | String | Status of area where sampling was done; Marine Protected Area (MPA) or non-MPA (NON) |
attribute | status | long_name | String | Status |
attribute | status | units | String | unitless |
variable | species | byte | ||
attribute | species | _FillValue | byte | 127 |
attribute | species | actual_range | byte | 0, 21 |
attribute | species | bcodmo_name | String | species |
attribute | species | description | String | Number of different species counted on each transect for each category of fish assemblage; herbivore or non-herbivore |
attribute | species | long_name | String | Species |
attribute | species | units | String | count |
variable | year | String | ||
attribute | year | bcodmo_name | String | date_range |
attribute | year | description | String | (A) Sampling took place between December 2010 and January 2011; (B) Sampling took place between December 2011 and January 2012 |
attribute | year | long_name | String | Year |
attribute | year | units | String | unitless |
variable | day | String | ||
attribute | day | bcodmo_name | String | time_point |
attribute | day | description | String | Day that sampling took place within each year's sampling event. A, B, and C all took place in during year A (Dec 2010 - Jan 2011); D, E, and F all took place during year B (Dec 2011 - Jan 2012). |
attribute | day | long_name | String | Day |
attribute | day | units | String | unitless |
variable | transect | byte | ||
attribute | transect | _FillValue | byte | 127 |
attribute | transect | actual_range | byte | 1, 18 |
attribute | transect | bcodmo_name | String | transect |
attribute | transect | description | String | Transect number; 1-15 |
attribute | transect | long_name | String | Transect |
attribute | transect | units | String | unitless |