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Grid DAP Data | Sub- set | Table DAP Data | Make A Graph | W M S | Source Data Files | Acces- sible | Title | Sum- mary | FGDC, ISO, Metadata | Back- ground Info | RSS | E | Institution | Dataset ID |
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data | graph | files | public | [carbonate chemistry and corals expt] - Results from OA/feeding experiment: carbonate chemistry and coral skeletal weight, symbiont density, and total tissue lipid content of samples collected from northwestern Bermuda patch reefs; 2010 (An Investigation of the Role of Nutrition in the Coral Calcification Response to Ocean Acidification) | I M | background | BCO-DMO | bcodmo_dataset_4040 |
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 | Experimental setup and conditions This experiment was conducted at the Bermuda Institute of Ocean Sciences (BIOS) in St. George\u2019s, Bermuda. The experimental treatments were two CO2 levels (high and ambient) and two feeding conditions (fed and unfed). The two pCO2 levels were established in static 5.5 gallon aquaria filled with serially filtered (50, 5 um) seawater prior to the addition of metamorphosed larvae. These conditions were achieved and maintained by directly bubbling air (in the ambient condition) or CO2 -enriched air (high CO2 treatment) through micropore bubble \"wands\" fixed horizontally approximately 5 cm from the base of each aquarium. A pair of Aalborg mass flow controllers maintained the CO2 concentration of the enriched treatment. The resultant average calculated pCO2 for ambient and high CO2 conditions were 421 \u00b1 35 and 1,311 \u00b1 76 uatm (mean \u00b1 SD), respectively, with corresponding average \u03a9ar of 3.66 \u00b1 0.15 and 1.63 \u00b1 0.08 (mean \u00b1 SD), respectively. \u03a9ar of the high CO2 treatments is within range of average global surface ocean \u03a9ar predicted by global climate models for the end of this century under the IPCC SRES A2 (Steinacher et al. 2009). Corals in fed treatments were isolated (every night for 2 weeks, every other night for the third week) for 3 h in 12.5 cm x 12.5 cm x 3 cm plastic containers filled with seawater from their respective treatment tanks and provided with 24-h-old Artemia nauplii (brine shrimp). Feeding took place at night, shortly after lights were switched off to mimic crepuscular feeding and temporal zooplankton abundance observed in local coral reef environments (Lewis and Price 1975). Unfed corals were not provided nauplii during the 3-week experiment and were not isolated in empty feeding containers. Each CO2 -feeding treatment was conducted in triplicate for a total of twelve aquaria, and all treatments were kept on a 12/12 h light\u2013dark cycle. Fluorescent aquarium lamps maintained maximum light levels of 62 \u00b1 8 umol quanta m-2 s-1 (mean \u00b1 SD), which were monitored using a LI-COR probe/meter assemblage. The compensation range for F. fragum spat on Bermuda is not yet known. The investigators used the low end of known compensation ranges for corals (e.g. 3\u2013233 umol quanta m-2 s-1 as reported by Mass et al. 2007) for two reasons. The first was to ensure that corals under elevated CO2 did not bleach (as experienced by Anthony et al. 2009), and the second was to minimize the potential for enhanced photosynthesis to overwhelm or inhibit the feeding-modulated calcification response to elevated CO2. Aquarium temperatures were maintained by in-line chiller/heater systems and monitored every 15 min (Hobo temperature loggers, Onset Corp.). Average temperature for all treatments over the course of the experiment was 27.6 \u00b1 0.1 degrees C (\u00b1 SD). Aquarium water was replaced with filtered seawater every week to prevent the build-up of dissolved inorganic nitrogen and other wastes. Prior to removing water from the aquaria, discrete water samples were collected for salinity, alkalinity (Alk), and dissolved inorganic carbon (DIC) from every aquarium. Salinity was measured at BIOS with an Autosal salinometer. The Alk/DIC samples were poisoned with mercuric chloride immediately after collection and analyzed using a Marianda VINDTA-3C analysis system at WHOI. Alkalinity was determined by nonlinear curve fitting of data obtained by open-cell titrations, and DIC concentrations were determined by coulometric analysis. Both measurements were standardized using certified reference materials obtained from Dr. A. Dickson (Scripps IO). The pH (NBS) of each tank was measured every 3\u20134 d (Orion pH meter and temperature- compensated electrode) to provide a real-time assessment of tank chemistry. Short-term variations in NBS pH were also assessed on a higher-resolution time scale: for one, 24-h period, by measuring pH in each aquarium at 3-h time intervals. The pH within each tank was maintained within \u00b1 a few hundredths of a pH unit on both sub-weekly and sub-daily time scales. The carbonate system parameters used to compare treatments (pCO2, [HCO3- ], [CO32-], and \u03a9ar) were calculated from the average temperature and discretely sampled salinity, Alk, and DIC data using the CO2SYS program (Lewis and Wallace 1998; Pelletier et al. 2007) with the constants of Mehrbach et al. (1973) as refit by Dickson and Millero (1987). Coral collection, spawning, and larval settlement In July 2010, approximately 1 week prior to anticipated peak larval release date (Goodbody-Gringley and de Putron 2009), the investigators collected 30 mature colonies of the brooding coral, F. fragum, from the Bailey\u2019s Bay patch reefs off the northwest Bermudan coast at approximately three to seven meters water depth. Adult colonies were maintained in outdoor flow-through seawater aquaria at BIOS under ambient light and temperature conditions. Parent colonies were kept isolated in glass jars during planula release, which occurred over the course of 6 nights. The live zooxanthellate planulae were collected from all parents and pooled together. Ceramic tiles, approximately 9 square cm, were left out on the reef for 2 months prior to the start of the experiment and further conditioned for larval settlement by scattering bits of freshly collected crustose coralline algae on the tiles. Immediately after collection, actively swimming larvae were transferred to small plastic tubs each containing ceramic tiles and filled with seawater preset to targeted CO2 levels. The tubs had mesh lids, allowing for water exchange, while they are submerged in the treatment aquaria. After 48 h, larvae had settled and metamorphosed into primary polyps (at this stage, larvae are \"spat\"). Spat on tiles were quickly counted, and tiles were pseudo-randomly distributed among the experimental aquaria so that each aquarium had approximately the same number of juvenile corals. Calcification was visible approximately 3 d after settlement. At the end of 3 weeks (\u00b1 1 d), 20\u201350 primary polyps (including their primary corallite) per treatment were removed from the tiles and frozen at- 80 degrees C for analysis of total lipid. Tiles were then removed from treatments and submerged in a 10% bleach solution for 1 h, which removed the polyp tissue from all of the remaining juvenile corals and exposed the calcified skeleton or primary corallite. Quantification of baby coral skeletal development, size, and weight Each bleached skeleton was digitally photographed, removed from the tile, and weighed using a Metro-Toledo micro-balance. Images of the baby corals (i.e. spat) were examined for skeletal development and size using Spot Imaging software. Length of the primary septa (present in all samples) was used to estimate corallite diameter (i.e., size). The septa are lateral CaCO3 plates that corals accrete in cycles. In our experiment, most spat accreted both primary and secondary septa; the tertiary septa were the last septal cycle accreted by any of the juvenile corals. Rate of skeletal development was defined as percent spat exhibiting tertiary septa, and a two-way ANOVA was used to test for differences in the mean proportion of spat with tertiary septa between the treatments. Feeding treatment and CO2 level were fixed effects. Data were arc sin square root transformed to homogenize variances prior to analyses. To test for differences in mean spat weight and diameter among treatments, a two-way, nested multivariate analysis of variance (MANOVA) was performed on natural log transformed weight data and square root transformed diameter data. Feeding treatment and CO2 levels were fixed main effects, while tank effect was the random factor nested within feeding and CO2 levels. Eight univariate F tests were conducted to test each of the dependent variables. A Bonferonni corrected alpha value of 0.0062 was used to declare significance of F statistics. It should be noted that the MANOVA only considers corals that have data for both diameter and weight. If part of a corallite is lost during weighing or was attached to coralline algae, both coral size and weight were excluded from the MANOVA analyses. Likewise, if the skeleton was irregularly shaped (i.e., primary septa did not lie in a straight line), the data for those corals were not included. In order to account for any bias that may have resulted from corallite exclusion in the MANOVA, ANOVAs for the dependent variables, weight, and diameter were conducted. These tests considered all data for a given dependent variable to compare with the MANOVA\u2019s univariate results. Quantification of baby coral total lipid and symbiont density Ten individual spat from each aquarium were pooled per tissue lipid sample for quantification of total lipid by gravimetric analysis. Pooling was necessary due to the small size of the spat at 3 weeks. Extraction methods follow that of Folch et al. (1957) and Cantin et al. (2007). Five individual spat from each aquarium were pooled per sample for quantification of symbiont density. Spat were homogenized, centrifuged and the resultant pellet was re- suspended in 250 l L filtered seawater. Symbionts from multiple (6\u20139) aliquot sub-samples of the slurry were counted on a known volume hemocytometer grid. Both total tissue lipid and symbiont counts were normalized to the circular area described by the average primary septa length (diameter) for a respective tank and then divided by the number of corals pooled in the sample (i.e., 10 or 5). Both area-normalized lipid content and symbiont density were compared among levels of CO2 and feeding conditions using two-way ANOVAs with tank as a random factor nested within the CO2 and feeding combinations. Total lipid concentration was transformed to - 1/x in order to homogenize the variances. All statistical analyses were conducted on SYSTAT. |
attribute | NC_GLOBAL | awards_0_award_nid | String | 54741 |
attribute | NC_GLOBAL | awards_0_award_number | String | OCE-1041052 |
attribute | NC_GLOBAL | awards_0_data_url | String | http://www.nsf.gov/awardsearch/showAward.do?AwardNumber=1041052 |
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 | 54896 |
attribute | NC_GLOBAL | awards_1_award_number | String | OCE-1041106 |
attribute | NC_GLOBAL | awards_1_data_url | String | http://www.nsf.gov/awardsearch/showAward.do?AwardNumber=1041106 |
attribute | NC_GLOBAL | awards_1_funder_name | String | NSF Division of Ocean Sciences |
attribute | NC_GLOBAL | awards_1_funding_acronym | String | NSF OCE |
attribute | NC_GLOBAL | awards_1_funding_source_nid | String | 355 |
attribute | NC_GLOBAL | awards_1_program_manager | String | David L. Garrison |
attribute | NC_GLOBAL | awards_1_program_manager_nid | String | 50534 |
attribute | NC_GLOBAL | cdm_data_type | String | Other |
attribute | NC_GLOBAL | comment | String | Carbonate Chemistry and Coral Data from OA/Feeding Experiment PI: Anne Cohen (WHOI) Co-PIs: S. de Putron (BIOS), D. McCorkle (WHOI), A. Tarrant (WHOI) Contact: Elizabeth Drenkard (WHOI) Version: 10 Sept 2013 |
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 | 2013-09-10T19:55:40Z |
attribute | NC_GLOBAL | date_modified | String | 2019-11-14T19:47:17Z |
attribute | NC_GLOBAL | defaultDataQuery | String | &time<now |
attribute | NC_GLOBAL | doi | String | 10.1575/1912/bco-dmo.4040.1 |
attribute | NC_GLOBAL | infoUrl | String | https://www.bco-dmo.org/dataset/4040 |
attribute | NC_GLOBAL | institution | String | BCO-DMO |
attribute | NC_GLOBAL | instruments_0_acronym | String | salinometer |
attribute | NC_GLOBAL | instruments_0_dataset_instrument_description | String | Salinity was measured at BIOS with an Autosal salinometer. |
attribute | NC_GLOBAL | instruments_0_dataset_instrument_nid | String | 6286 |
attribute | NC_GLOBAL | instruments_0_description | String | The salinometer is an instrument for measuring the salinity of a water sample. |
attribute | NC_GLOBAL | instruments_0_instrument_external_identifier | String | https://vocab.nerc.ac.uk/collection/L05/current/LAB30/ |
attribute | NC_GLOBAL | instruments_0_instrument_name | String | Autosal salinometer |
attribute | NC_GLOBAL | instruments_0_instrument_nid | String | 576 |
attribute | NC_GLOBAL | instruments_0_supplied_name | String | Autosal salinometer |
attribute | NC_GLOBAL | instruments_1_acronym | String | Water Temp Sensor |
attribute | NC_GLOBAL | instruments_1_dataset_instrument_description | String | Aquarium temperatures were maintained by in-line chiller/heater systems and monitored every 15 min using Hobo temperature loggers (Onset Corp.). |
attribute | NC_GLOBAL | instruments_1_dataset_instrument_nid | String | 6285 |
attribute | NC_GLOBAL | instruments_1_description | String | General term for an instrument that measures the temperature of the water with which it is in contact (thermometer). |
attribute | NC_GLOBAL | instruments_1_instrument_external_identifier | String | https://vocab.nerc.ac.uk/collection/L05/current/134/ |
attribute | NC_GLOBAL | instruments_1_instrument_name | String | Water Temperature Sensor |
attribute | NC_GLOBAL | instruments_1_instrument_nid | String | 647 |
attribute | NC_GLOBAL | instruments_1_supplied_name | String | Water Temperature Sensor |
attribute | NC_GLOBAL | instruments_2_acronym | String | pH Sensor |
attribute | NC_GLOBAL | instruments_2_dataset_instrument_description | String | The pH (NBS) of each tank was measured using an Orion pH meter and temperature-compensated electrode. |
attribute | NC_GLOBAL | instruments_2_dataset_instrument_nid | String | 6288 |
attribute | NC_GLOBAL | instruments_2_description | String | General term for an instrument that measures the pH or how acidic or basic a solution is. |
attribute | NC_GLOBAL | instruments_2_instrument_name | String | pH Sensor |
attribute | NC_GLOBAL | instruments_2_instrument_nid | String | 674 |
attribute | NC_GLOBAL | instruments_2_supplied_name | String | pH Sensor |
attribute | NC_GLOBAL | instruments_3_acronym | String | inorganic carbon and alkalinity analyser |
attribute | NC_GLOBAL | instruments_3_dataset_instrument_description | String | The Alk/DIC samples were poisoned with mercuric chloride immediately after collection and analyzed using a Marianda VINDTA-3C analysis system at WHOI. |
attribute | NC_GLOBAL | instruments_3_dataset_instrument_nid | String | 6287 |
attribute | NC_GLOBAL | instruments_3_description | String | The Versatile INstrument for the Determination of Total inorganic carbon and titration Alkalinity (VINDTA) 3C is a laboratory alkalinity titration system combined with an extraction unit for coulometric titration, which simultaneously determines the alkalinity and dissolved inorganic carbon content of a sample. The sample transport is performed with peristaltic pumps and acid is added to the sample using a membrane pump. No pressurizing system is required and only one gas supply (nitrogen or dry and CO2-free air) is necessary. The system uses a Metrohm Titrino 719S, an ORION-Ross pH electrode and a Metrohm reference electrode. The burette, the pipette and the analysis cell have a water jacket around them. Precision is typically +/- 1 umol/kg for TA and/or DIC in open ocean water. |
attribute | NC_GLOBAL | instruments_3_instrument_external_identifier | String | https://vocab.nerc.ac.uk/collection/L22/current/TOOL0481/ |
attribute | NC_GLOBAL | instruments_3_instrument_name | String | MARIANDA VINDTA 3C total inorganic carbon and titration alkalinity analyser |
attribute | NC_GLOBAL | instruments_3_instrument_nid | String | 686 |
attribute | NC_GLOBAL | instruments_3_supplied_name | String | MARIANDA VINDTA 3C total inorganic carbon and titration alkalinity analyser |
attribute | NC_GLOBAL | instruments_4_acronym | String | Aquarium |
attribute | NC_GLOBAL | instruments_4_dataset_instrument_nid | String | 6283 |
attribute | NC_GLOBAL | instruments_4_description | String | Aquarium - a vivarium consisting of at least one transparent side in which water-dwelling plants or animals are kept |
attribute | NC_GLOBAL | instruments_4_instrument_name | String | Aquarium |
attribute | NC_GLOBAL | instruments_4_instrument_nid | String | 711 |
attribute | NC_GLOBAL | instruments_4_supplied_name | String | Aquarium |
attribute | NC_GLOBAL | instruments_5_acronym | String | MFC |
attribute | NC_GLOBAL | instruments_5_dataset_instrument_description | String | A pair of Aalborg mass flow controllers maintained the CO2 concentration of the enriched treatment. |
attribute | NC_GLOBAL | instruments_5_dataset_instrument_nid | String | 6284 |
attribute | NC_GLOBAL | instruments_5_description | String | Mass Flow Controller (MFC) - A device used to measure and control the flow of fluids and gases |
attribute | NC_GLOBAL | instruments_5_instrument_name | String | Mass Flow Controller |
attribute | NC_GLOBAL | instruments_5_instrument_nid | String | 712 |
attribute | NC_GLOBAL | instruments_5_supplied_name | String | Mass Flow Controller |
attribute | NC_GLOBAL | instruments_6_acronym | String | Scale |
attribute | NC_GLOBAL | instruments_6_dataset_instrument_description | String | Bleached skeletons were weighed using a Metro-Toledo micro-balance. |
attribute | NC_GLOBAL | instruments_6_dataset_instrument_nid | String | 6289 |
attribute | NC_GLOBAL | instruments_6_description | String | An instrument used to measure weight or mass. |
attribute | NC_GLOBAL | instruments_6_instrument_external_identifier | String | https://vocab.nerc.ac.uk/collection/L05/current/LAB13/ |
attribute | NC_GLOBAL | instruments_6_instrument_name | String | Scale |
attribute | NC_GLOBAL | instruments_6_instrument_nid | String | 714 |
attribute | NC_GLOBAL | instruments_6_supplied_name | String | Scale |
attribute | NC_GLOBAL | keywords | String | alk, alk_sd, altimetry, arag, AragSat, AragSat_sd, area, bco, bco-dmo, biological, carbonate, chemical, chemistry, co3, CO3_sd, corallite, CoralliteWt, CoralliteWt_se, data, dataset, density, diam, dic, DIC_sd, dmo, earth, Earth Science > Oceans > Ocean Chemistry > pH, erddap, hco3, HCO3_sd, laboratory, lipid, management, ocean, oceanography, oceans, office, pcnt, PcntSpat3oSepta, PcntSpat3oSepta_se, per, pH_sd, preliminary, reported, sal, sal_sd, sat, satellite, scale, science, sea, sea_water_ph_reported_on_total_scale, seawater, septa, SeptaDiam, SeptaDiam_se, spat3o, symbiont, SymbiontDensity, SymbiontDensity_se, tank, TankAragSat, TankAragSat_se, TankCoralliteWt, TankCoralliteWt_se, tot, total, TotLipid_per_area, TotLipid_per_area_se, treatment, water |
attribute | NC_GLOBAL | keywords_vocabulary | String | GCMD Science Keywords |
attribute | NC_GLOBAL | license | String | https://www.bco-dmo.org/dataset/4040/license |
attribute | NC_GLOBAL | metadata_source | String | https://www.bco-dmo.org/api/dataset/4040 |
attribute | NC_GLOBAL | param_mapping | String | {'4040': {}} |
attribute | NC_GLOBAL | parameter_source | String | https://www.bco-dmo.org/mapserver/dataset/4040/parameters |
attribute | NC_GLOBAL | people_0_affiliation | String | Woods Hole Oceanographic Institution |
attribute | NC_GLOBAL | people_0_affiliation_acronym | String | WHOI BCO-DMO |
attribute | NC_GLOBAL | people_0_person_name | String | Anne L Cohen |
attribute | NC_GLOBAL | people_0_person_nid | String | 51428 |
attribute | NC_GLOBAL | people_0_role | String | Lead Principal Investigator |
attribute | NC_GLOBAL | people_0_role_type | String | originator |
attribute | NC_GLOBAL | people_1_affiliation | String | Bermuda Institute of Ocean Sciences |
attribute | NC_GLOBAL | people_1_affiliation_acronym | String | BIOS |
attribute | NC_GLOBAL | people_1_person_name | String | Samantha J. de Putron |
attribute | NC_GLOBAL | people_1_person_nid | String | 51431 |
attribute | NC_GLOBAL | people_1_role | String | Co-Principal Investigator |
attribute | NC_GLOBAL | people_1_role_type | String | originator |
attribute | NC_GLOBAL | people_2_affiliation | String | Woods Hole Oceanographic Institution |
attribute | NC_GLOBAL | people_2_affiliation_acronym | String | WHOI |
attribute | NC_GLOBAL | people_2_person_name | String | Daniel C McCorkle |
attribute | NC_GLOBAL | people_2_person_nid | String | 51429 |
attribute | NC_GLOBAL | people_2_role | String | Co-Principal Investigator |
attribute | NC_GLOBAL | people_2_role_type | String | originator |
attribute | NC_GLOBAL | people_3_affiliation | String | Woods Hole Oceanographic Institution |
attribute | NC_GLOBAL | people_3_affiliation_acronym | String | WHOI |
attribute | NC_GLOBAL | people_3_person_name | String | Ann M. Tarrant |
attribute | NC_GLOBAL | people_3_person_nid | String | 51430 |
attribute | NC_GLOBAL | people_3_role | String | Co-Principal Investigator |
attribute | NC_GLOBAL | people_3_role_type | String | originator |
attribute | NC_GLOBAL | people_4_affiliation | String | Woods Hole Oceanographic Institution |
attribute | NC_GLOBAL | people_4_affiliation_acronym | String | WHOI |
attribute | NC_GLOBAL | people_4_person_name | String | Elizabeth Drenkard |
attribute | NC_GLOBAL | people_4_person_nid | String | 51723 |
attribute | NC_GLOBAL | people_4_role | String | Contact |
attribute | NC_GLOBAL | people_4_role_type | String | related |
attribute | NC_GLOBAL | people_5_affiliation | String | Woods Hole Oceanographic Institution |
attribute | NC_GLOBAL | people_5_affiliation_acronym | String | WHOI BCO-DMO |
attribute | NC_GLOBAL | people_5_person_name | String | Shannon Rauch |
attribute | NC_GLOBAL | people_5_person_nid | String | 51498 |
attribute | NC_GLOBAL | people_5_role | String | BCO-DMO Data Manager |
attribute | NC_GLOBAL | people_5_role_type | String | related |
attribute | NC_GLOBAL | project | String | OA Nutrition and Coral Calcification |
attribute | NC_GLOBAL | projects_0_acronym | String | OA Nutrition and Coral Calcification |
attribute | NC_GLOBAL | projects_0_description | String | The project description is a modification of the original NSF award abstract. This research project is part of the larger NSF funded CRI-OA collaborative research initiative and was funded as an Ocean Acidification-Category 1, 2010 award. Over the course of this century, all tropical coral reef ecosystems, whether fringing heavily populated coastlines or lining remote islands and atolls, face unprecedented threat from ocean acidification caused by rising levels of atmospheric CO2. In many laboratory experiments conducted to date, calcium carbonate production (calcification) by scleractinian (stony) corals showed an inverse correlation to seawater saturation state OMEGAar), whether OMEGAar was manipulated by acid or CO2 addition. Based on these data, it is predicted that coral calcification rates could decline by up to 80% of modern values by the end of this century. A growing body of new experimental data however, suggests that the coral calcification response to ocean acidification may be less straightforward and a lot more variable than previously recognized. In at least 10 recent experiments including our own, 8 different tropical and temperate species reared under nutritionally-replete but significantly elevated CO2 conditions (780-1200 ppm, OMEAGar ~1.5-2), continued to calcify at rates comparable to conspecifics reared under ambient CO2. These experimental results are consistent with initial field data collected on reefs in the eastern Pacific and southern Oman, where corals today live and accrete their skeletons under conditions equivalent to 2X and 3X pre-industrial CO2. On these high CO2, high nutrient reefs (where nitrate concentrations typically exceed 2.5 micro-molar), coral growth rates rival, and sometimes even exceed, those of conspecifics in low CO2, oligotrophic reef environments. The investigators propose that a coral's energetic status, tightly coupled to the availability of inorganic nutrients and/or food, is a key factor in the calcification response to CO2-induced ocean acidification. Their hypothesis, if confirmed by the proposed laboratory investigations, implies that predicted changes in coastal and open ocean nutrient concentrations over the course of this century, driven by both climate impacts on ocean stratification and by increased human activity in coastal regions, could play a critical role in exacerbating and in some areas, modulating the coral reef response to ocean acidification. This research program builds on the investigators initial results and observations. The planned laboratory experiments will test the hypothesis that: (1) The coral calcification response to ocean acidification is linked to the energetic status of the coral host. The relative contribution of symbiont photosynthesis and heterotrophic feeding to a coral's energetic status varies amongst species. Enhancing the energetic status of corals reared under high CO2, either by stimulating photosynthesis with inorganic nutrients or by direct heterotrophic feeding of the host lowers the sensitivity of calcification to decreased seawater OMEGAar; (2) A species-specific threshold CO2 level exists over which enhanced energetic status can no longer compensate for decreased OMEGAar of the external seawater. Similarly, we will test the hypothesis that a nutrient threshold exists over which nutrients become detrimental for calcification even under high CO2 conditions; and (3) Temperature-induced reduction of algal symbionts is one stressor that can reduce the energetic reserve of the coral host and exacerbate the calcification response to ocean acidification. The investigator's initial findings highlight the critical importance of energetic status in the coral calcification response to ocean acidification. Verification of these findings in the laboratory, and identification of nutrient and CO2 thresholds for a range of species will have immediate, direct impact on predictions of reef resilience in a high CO2 world. The research project brings together a diverse group of expertise in coral biogeochemistry, chemical oceanography, molecular biology and coral reproductive ecology to focus on a problem that has enormous societal, economic and conservation relevance. |
attribute | NC_GLOBAL | projects_0_end_date | String | 2013-09 |
attribute | NC_GLOBAL | projects_0_geolocation | String | global; experimental |
attribute | NC_GLOBAL | projects_0_name | String | An Investigation of the Role of Nutrition in the Coral Calcification Response to Ocean Acidification |
attribute | NC_GLOBAL | projects_0_project_nid | String | 2183 |
attribute | NC_GLOBAL | projects_0_start_date | String | 2010-10 |
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 | Results from OA/feeding experiment: carbonate chemistry and coral skeletal weight, symbiont density, and total tissue lipid content of samples collected from northwestern Bermuda patch reefs; 2010 |
attribute | NC_GLOBAL | title | String | [carbonate chemistry and corals expt] - Results from OA/feeding experiment: carbonate chemistry and coral skeletal weight, symbiont density, and total tissue lipid content of samples collected from northwestern Bermuda patch reefs; 2010 (An Investigation of the Role of Nutrition in the Coral Calcification Response to Ocean Acidification) |
attribute | NC_GLOBAL | version | String | 1 |
attribute | NC_GLOBAL | xml_source | String | osprey2erddap.update_xml() v1.3 |
variable | treatment | String | ||
attribute | treatment | bcodmo_name | String | treatment |
attribute | treatment | description | String | Experimental treatment/condition. |
attribute | treatment | long_name | String | Treatment |
attribute | treatment | units | String | text |
variable | sal | float | ||
attribute | sal | _FillValue | float | NaN |
attribute | sal | actual_range | float | 37.0, 37.6 |
attribute | sal | bcodmo_name | String | sal |
attribute | sal | description | String | Salinity; average of all replicate tanks for the given experimental treatment. |
attribute | sal | long_name | String | Sal |
attribute | sal | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P01/current/PSALST01/ |
attribute | sal | units | String | psu |
variable | sal_sd | float | ||
attribute | sal_sd | _FillValue | float | NaN |
attribute | sal_sd | actual_range | float | 0.2, 0.3 |
attribute | sal_sd | bcodmo_name | String | standard deviation |
attribute | sal_sd | colorBarMaximum | double | 50.0 |
attribute | sal_sd | colorBarMinimum | double | 0.0 |
attribute | sal_sd | description | String | Standard deviation of 'sal'. |
attribute | sal_sd | long_name | String | Sal Sd |
attribute | sal_sd | units | String | psu |
variable | alk | short | ||
attribute | alk | _FillValue | short | 32767 |
attribute | alk | actual_range | short | 2324, 2332 |
attribute | alk | bcodmo_name | String | unknown |
attribute | alk | description | String | Alkalinity; average of all replicate tanks for the given experimental treatment. |
attribute | alk | long_name | String | Alk |
attribute | alk | units | String | microequivalent per kilogram (ueq/kg) |
variable | alk_sd | byte | ||
attribute | alk_sd | _FillValue | byte | 127 |
attribute | alk_sd | actual_range | byte | 9, 23 |
attribute | alk_sd | bcodmo_name | String | standard deviation |
attribute | alk_sd | colorBarMaximum | double | 50.0 |
attribute | alk_sd | colorBarMinimum | double | 0.0 |
attribute | alk_sd | description | String | Standard deviation of 'alk'. |
attribute | alk_sd | long_name | String | Alk Sd |
attribute | alk_sd | units | String | microequivalent per kilogram (ueq/kg) |
variable | DIC | short | ||
attribute | DIC | _FillValue | short | 32767 |
attribute | DIC | actual_range | short | 1984, 2213 |
attribute | DIC | bcodmo_name | String | DIC |
attribute | DIC | description | String | Concentration of dissolved inorganic carbon; average of all replicate tanks for the given experimental treatment. |
attribute | DIC | long_name | String | DIC |
attribute | DIC | units | String | micromoles per kilogram (umol/kg) |
variable | DIC_sd | byte | ||
attribute | DIC_sd | _FillValue | byte | 127 |
attribute | DIC_sd | actual_range | byte | 16, 33 |
attribute | DIC_sd | bcodmo_name | String | standard deviation |
attribute | DIC_sd | colorBarMaximum | double | 50.0 |
attribute | DIC_sd | colorBarMinimum | double | 0.0 |
attribute | DIC_sd | description | String | Standard deviation of 'DIC'. |
attribute | DIC_sd | long_name | String | DIC Sd |
attribute | DIC_sd | units | String | micromoles per kilogram (umol/kg) |
variable | pH | float | ||
attribute | pH | _FillValue | float | NaN |
attribute | pH | actual_range | float | 7.72, 8.2 |
attribute | pH | bcodmo_name | String | pH |
attribute | pH | colorBarMaximum | double | 9.0 |
attribute | pH | colorBarMinimum | double | 7.0 |
attribute | pH | description | String | pH; average of all replicate tanks for the given experimental treatment. |
attribute | pH | long_name | String | Sea Water Ph Reported On Total Scale |
attribute | pH | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P01/current/PHXXZZXX/ |
attribute | pH | units | String | NBS |
variable | pH_sd | float | ||
attribute | pH_sd | _FillValue | float | NaN |
attribute | pH_sd | actual_range | float | 0.0, 0.02 |
attribute | pH_sd | bcodmo_name | String | standard deviation |
attribute | pH_sd | colorBarMaximum | double | 50.0 |
attribute | pH_sd | colorBarMinimum | double | 0.0 |
attribute | pH_sd | description | String | Standard deviation of 'pH'. |
attribute | pH_sd | long_name | String | P H SD |
attribute | pH_sd | units | String | NBS |
variable | HCO3 | short | ||
attribute | HCO3 | _FillValue | short | 32767 |
attribute | HCO3 | actual_range | short | 1735, 2076 |
attribute | HCO3 | bcodmo_name | String | bicarbonate |
attribute | HCO3 | description | String | Concentration of bicarbonate ions; average of all replicate tanks for the given experimental treatment. |
attribute | HCO3 | long_name | String | HCO3 |
attribute | HCO3 | units | String | micromoles per kilogram (umol/kg) |
variable | HCO3_sd | byte | ||
attribute | HCO3_sd | _FillValue | byte | 127 |
attribute | HCO3_sd | actual_range | byte | 13, 39 |
attribute | HCO3_sd | bcodmo_name | String | standard deviation |
attribute | HCO3_sd | colorBarMaximum | double | 50.0 |
attribute | HCO3_sd | colorBarMinimum | double | 0.0 |
attribute | HCO3_sd | description | String | Standard deviation of 'HCO3'. |
attribute | HCO3_sd | long_name | String | HCO3 Sd |
attribute | HCO3_sd | units | String | micromoles per kilogram (umol/kg) |
variable | CO3 | short | ||
attribute | CO3 | _FillValue | short | 32767 |
attribute | CO3 | actual_range | short | 101, 238 |
attribute | CO3 | bcodmo_name | String | carbonate |
attribute | CO3 | description | String | Concentration of carbonate ions; average of all replicate tanks for the given experimental treatment. |
attribute | CO3 | long_name | String | CO3 |
attribute | CO3 | units | String | micromoles per kilogram (umol/kg) |
variable | CO3_sd | byte | ||
attribute | CO3_sd | _FillValue | byte | 127 |
attribute | CO3_sd | actual_range | byte | 3, 9 |
attribute | CO3_sd | bcodmo_name | String | standard deviation |
attribute | CO3_sd | colorBarMaximum | double | 50.0 |
attribute | CO3_sd | colorBarMinimum | double | 0.0 |
attribute | CO3_sd | description | String | Standard deviation of 'CO3'. |
attribute | CO3_sd | long_name | String | CO3 Sd |
attribute | CO3_sd | units | String | micromoles per kilogram (umol/kg) |
variable | AragSat | float | ||
attribute | AragSat | _FillValue | float | NaN |
attribute | AragSat | actual_range | float | 1.6, 3.76 |
attribute | AragSat | bcodmo_name | String | OM_ar |
attribute | AragSat | description | String | Aragonite saturation state; average of all replicate tanks for the given experimental treatment. (The saturation state of seawater with respect to aragonite is a measure of the thermodynamic potential for aragonite to form or to dissolve, and is defined as the product of the concentrations of dissolved calcium and carbonate ions in seawater, divided by their product at equilibrium.) |
attribute | AragSat | long_name | String | Arag Sat |
attribute | AragSat | units | String | dimensionless |
variable | AragSat_sd | float | ||
attribute | AragSat_sd | _FillValue | float | NaN |
attribute | AragSat_sd | actual_range | float | 0.03, 0.15 |
attribute | AragSat_sd | bcodmo_name | String | standard deviation |
attribute | AragSat_sd | colorBarMaximum | double | 50.0 |
attribute | AragSat_sd | colorBarMinimum | double | 0.0 |
attribute | AragSat_sd | description | String | Standard deviation of 'AragSat'. |
attribute | AragSat_sd | long_name | String | Arag Sat Sd |
attribute | AragSat_sd | units | String | dimensionless |
variable | PcntSpat3oSepta | byte | ||
attribute | PcntSpat3oSepta | _FillValue | byte | 127 |
attribute | PcntSpat3oSepta | actual_range | byte | 7, 82 |
attribute | PcntSpat3oSepta | bcodmo_name | String | unknown |
attribute | PcntSpat3oSepta | description | String | Percent of spat with tertiary septat; average of all replicate tanks for the given experimental treatment. |
attribute | PcntSpat3oSepta | long_name | String | Pcnt Spat3o Septa |
attribute | PcntSpat3oSepta | units | String | % |
variable | PcntSpat3oSepta_se | byte | ||
attribute | PcntSpat3oSepta_se | _FillValue | byte | 127 |
attribute | PcntSpat3oSepta_se | actual_range | byte | 4, 7 |
attribute | PcntSpat3oSepta_se | bcodmo_name | String | standard error |
attribute | PcntSpat3oSepta_se | description | String | Standard error of 'PcntSpat3oSepta'. |
attribute | PcntSpat3oSepta_se | long_name | String | Pcnt Spat3o Septa Se |
attribute | PcntSpat3oSepta_se | units | String | % |
variable | SeptaDiam | short | ||
attribute | SeptaDiam | _FillValue | short | 32767 |
attribute | SeptaDiam | actual_range | short | 1323, 2133 |
attribute | SeptaDiam | bcodmo_name | String | unknown |
attribute | SeptaDiam | description | String | Septa diameter; average of all replicate tanks for the given experimental treatment. |
attribute | SeptaDiam | long_name | String | Septa Diam |
attribute | SeptaDiam | units | String | micrometers (um) |
variable | SeptaDiam_se | byte | ||
attribute | SeptaDiam_se | _FillValue | byte | 127 |
attribute | SeptaDiam_se | actual_range | byte | 23, 35 |
attribute | SeptaDiam_se | bcodmo_name | String | standard error |
attribute | SeptaDiam_se | description | String | Standard error of 'SeptaDiam'. |
attribute | SeptaDiam_se | long_name | String | Septa Diam Se |
attribute | SeptaDiam_se | units | String | micrometers (um) |
variable | CoralliteWt | short | ||
attribute | CoralliteWt | _FillValue | short | 32767 |
attribute | CoralliteWt | actual_range | short | 250, 547 |
attribute | CoralliteWt | bcodmo_name | String | weight |
attribute | CoralliteWt | description | String | Total corallite weight; average of all replicate tanks for the given experimental treatment. |
attribute | CoralliteWt | long_name | String | Corallite Wt |
attribute | CoralliteWt | units | String | micrograms (ug) |
variable | CoralliteWt_se | byte | ||
attribute | CoralliteWt_se | _FillValue | byte | 127 |
attribute | CoralliteWt_se | actual_range | byte | 7, 29 |
attribute | CoralliteWt_se | bcodmo_name | String | standard error |
attribute | CoralliteWt_se | description | String | Standard error of 'CoralliteWt'. |
attribute | CoralliteWt_se | long_name | String | Corallite Wt Se |
attribute | CoralliteWt_se | units | String | micrograms (ug) |
variable | TotLipid_per_area | byte | ||
attribute | TotLipid_per_area | _FillValue | byte | 127 |
attribute | TotLipid_per_area | actual_range | byte | 10, 13 |
attribute | TotLipid_per_area | bcodmo_name | String | unknown |
attribute | TotLipid_per_area | description | String | Area-normalized total tissue lipid weight; average of all replicate tanks for the given experimental treatment. |
attribute | TotLipid_per_area | long_name | String | Tot Lipid Per Area |
attribute | TotLipid_per_area | units | String | micrograms per square millimeter (ug/mm^2) |
variable | TotLipid_per_area_se | byte | ||
attribute | TotLipid_per_area_se | _FillValue | byte | 127 |
attribute | TotLipid_per_area_se | actual_range | byte | 0, 2 |
attribute | TotLipid_per_area_se | bcodmo_name | String | standard error |
attribute | TotLipid_per_area_se | description | String | Standard error of 'TotLipid_per_area'. |
attribute | TotLipid_per_area_se | long_name | String | Tot Lipid Per Area Se |
attribute | TotLipid_per_area_se | units | String | micrograms per square millimeter (ug/mm^2) |
variable | SymbiontDensity | byte | ||
attribute | SymbiontDensity | _FillValue | byte | 127 |
attribute | SymbiontDensity | actual_range | byte | 14, 23 |
attribute | SymbiontDensity | bcodmo_name | String | unknown |
attribute | SymbiontDensity | description | String | Symbionts per area; average of all replicate tanks for the given experimental treatment. |
attribute | SymbiontDensity | long_name | String | Symbiont Density |
attribute | SymbiontDensity | units | String | x1000 cells per square millimeter (x10^3 cells/mm^2) |
variable | SymbiontDensity_se | byte | ||
attribute | SymbiontDensity_se | _FillValue | byte | 127 |
attribute | SymbiontDensity_se | actual_range | byte | 2, 4 |
attribute | SymbiontDensity_se | bcodmo_name | String | unknown |
attribute | SymbiontDensity_se | description | String | Standard error of 'SymbiontDensity'. |
attribute | SymbiontDensity_se | long_name | String | Symbiont Density Se |
attribute | SymbiontDensity_se | units | String | x1000 cells per square millimeter (x10^3 cells/mm^2) |
variable | tank | byte | ||
attribute | tank | _FillValue | byte | 127 |
attribute | tank | actual_range | byte | 1, 12 |
attribute | tank | bcodmo_name | String | tank |
attribute | tank | description | String | Identification number of the experimental tank. |
attribute | tank | long_name | String | Tank |
attribute | tank | units | String | integer |
variable | TankAragSat | float | ||
attribute | TankAragSat | _FillValue | float | NaN |
attribute | TankAragSat | actual_range | float | 1.54, 3.79 |
attribute | TankAragSat | bcodmo_name | String | OM_ar |
attribute | TankAragSat | description | String | Aragonite saturation state in the specified tank. |
attribute | TankAragSat | long_name | String | Tank Arag Sat |
attribute | TankAragSat | units | String | dimensionless |
variable | TankAragSat_se | float | ||
attribute | TankAragSat_se | _FillValue | float | NaN |
attribute | TankAragSat_se | actual_range | float | 0.01, 0.26 |
attribute | TankAragSat_se | bcodmo_name | String | standard error |
attribute | TankAragSat_se | description | String | Standard error of 'TankAragSat'. |
attribute | TankAragSat_se | long_name | String | Tank Arag Sat Se |
attribute | TankAragSat_se | units | String | dimensionless |
variable | TankCoralliteWt | short | ||
attribute | TankCoralliteWt | _FillValue | short | 32767 |
attribute | TankCoralliteWt | actual_range | short | 237, 578 |
attribute | TankCoralliteWt | bcodmo_name | String | weight |
attribute | TankCoralliteWt | description | String | Total corallite weight in the specified tank. |
attribute | TankCoralliteWt | long_name | String | Tank Corallite Wt |
attribute | TankCoralliteWt | units | String | micrograms (ug) |
variable | TankCoralliteWt_se | byte | ||
attribute | TankCoralliteWt_se | _FillValue | byte | 127 |
attribute | TankCoralliteWt_se | actual_range | byte | 11, 59 |
attribute | TankCoralliteWt_se | bcodmo_name | String | standard error |
attribute | TankCoralliteWt_se | description | String | Standard error of 'TankCoralliteWt'. |
attribute | TankCoralliteWt_se | long_name | String | Tank Corallite Wt Se |
attribute | TankCoralliteWt_se | units | String | micrograms (ug) |
The information in the table above is also available in other file formats (.csv, .htmlTable, .itx, .json, .jsonlCSV1, .jsonlCSV, .jsonlKVP, .mat, .nc, .nccsv, .tsv, .xhtml) via a RESTful web service.