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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,.esriCsv,.geoJson |
attribute | NC_GLOBAL | acquisition_description | String | Sample collection: \n Five Porites astreoides colonies and a sand patch were selected and marked\nwith flagging tape by divers on Ram Head reef (18\\u00ba18\\u201907.3\\u201d N,\n64\\u00ba42\\u201914.5\\u201d W; 8 m depth in sand) in St. John, U. S. Virgin\nIslands. Colonies of various sizes (3 \\u2013 16 inches in diameter) from a\nrange of heights above the seafloor (1 \\u2013 27 cm) were selected and these\ncolonies were labeled A through E. Additionally, colonies were evenly\ndistributed across the reef in order to minimize location effects (range of\n3.6 to 14 meters between each colony). All colonies were located directly next\nto sand patches based on colony size constraints and the space needed for\ndeployment of the custom made Coral Ecosphere Sampling Devices (CESD). Six\nCESD made out of aluminum strut material were deployed adjacent to each\nsampling location with sand screws. The last CESD was placed in a wide sand\npatch with no corals or benthic organisms located in its vicinity and this\nsampling location was used as a \\u2018no-coral\\u2019 control. Divers\npositioned the CESD so that a 60 ml syringe with an attached filter holder\ncould be placed 5 cm away from the middle of the colony. Light and temperature\nloggers (8K HOBO/PAR loggers; Onset, Wareham, MA) were zip-tied to the end of\neach CESD and programmed to collect temperature and relative light intensity\nmeasurements every 5 minutes over the course of the three-day study. An hour\nafter CESD deployment, scuba divers collected the first set of samples (Day 1,\n3:00 pm). Filter holders were pre-loaded with 0.22 \\u00b5m pore size\nSupor\\u00ae filters (Pall Corporation, Ann Arbor, MI, USA) and were contained\nwithin sterile Whirl-pack\\u00ae bags prior to sampling.\\u00a0 Divers also\ndescended with acid-washed polyethylene nutrient bottles (30 ml volume) to\ncollect seawater samples for unfiltered inorganic nutrient analysis and flow\ncytometry. At depth, seawater samples (60 ml) collected for amplicon-based\nmicrobial community analysis were conducted at 2 different stationary\nlocations relative to the CESD device (with the exception of collections\ncompleted at the sand-patch location). Reef-depth samples were collected first\nat the top of the CESD (2 m from the colony) in order to minimize stirring\nclose to the coral ecosphere sampling area. To collect the sample, a diver\nattached a piece of acid-cleaned Masterflex silicone tubing to connect the end\nof the filter holder to the mouth of the syringe and then used reverse\nfiltration to pull seawater through the filter. The filter-holder was then\nplaced in an individual Whirl-pack\\u00ae bag and sealed. After collection of\nmicrobial biomass with the syringe, a nutrient sample was collected. After\ncollection of the reef-depth sample, a diver attached the filter holder to the\nsyringe, slowly descended closer to the coral colony, but behind the CESD to\nmaintain sufficient distance from the sampling area and then placed the\nsyringe into the syringe holder located on the horizontal arm of the CESD. As\nbefore, the diver first collected the coral ecosphere sample (5 cm from the\ncolony) onto the filter followed by a nutrient sample in the same location.\nReplicate samples collected for DNA analysis were collected from both seawater\nenvironments surrounding each colony on the first dive, but were not collected\non the following dives due to time constraints. Surface seawater samples (< 1\nm) were collected using 60 mL syringes at each time point from the dive boat.\n \nThis sampling scheme was repeated at approximately 3 am and 3 pm for the next\nthree days, totaling up to 6 sampling time points. Divers sampled each colony\nand collected samples in the same order (reef-depth followed by coral\necosphere) during all time points. After collection, samples were placed in a\ncooler equipped with blue-ice packs for the transit from the reef to the lab\nand then samples were processed immediately. Over the course of sampling, 85\nseawater samples were collected.\n \nAfter the last time point, coral tissue was collected from each colony (close\nto the area where the coral ecosphere seawater was sampled) using a hammer and\nchisel and the CESD were removed. Sand was also collected in the location\nwhere the sand control CESD device was deployed.\n \nSample processing: \n In the laboratory, sterile syringes were used to remove residual seawater\ntrapped within filter holders and then filters were placed into cryovials,\nflash-frozen in a dry shipper charged with liquid nitrogen, and then\ntransferred into a\\u00a0 -20 C freezer.\n \nSeawater collected for flow cytometric analysis was subsampled from unfiltered\nnutrient samples and preserved with paraformaldehyde (Electron Microscopy\nSciences, Allentown, PA) to a final concentration of 1% (by volume). Nutrient,\nDNA, and flow cytometry samples were shipped frozen back to Woods Hole\nOceanographic Institution and ultimately stored at -80 C prior to analysis.\nThe coral tissue and sand samples were stored in a second dry shipper and\nultimately at -80 C until they were processed.\\u00a0\n \nMacronutrient analysis and flow cytometry: \n Frozen and unfiltered nutrient samples were analyzed with a continuous\nsegmented flow-system using previously described methods (as in Apprill and\nRappe 2011). The concentrations of NO2- + NO3-, NO2-, PO43-, NH4+, and\nsilicate were measured in all of the samples. Nitrate concentrations were\nobtained by subtracting the nitrite concentration from the nitrite + nitrate\nmeasurements for each sample.\n \nSamples collected for flow cytometry were analyzed using colinear analysis\n(laser excitation wavelength of 488 nm, UV) on an Altra flow cytometer\n(Beckman Coulter, Pasadena, CA.). Unstained subsamples were used to enumerate\nthe abundances of picocyanobacteria (Prochlorococcus, Synechococcus) and\npicoeukaryotes. Stained (Hoechst stain, 1 \\u00b5g ml-1 final concentration)\nsubsamples were analyzed to estimate the abundance of unpigmented cells (an\nestimate of heterotrophic bacterial abundance) (Marie et al. 1997). FlowJo (v.\n6.4.7) software was used to estimate the abundance of each cell type. The\nabundance of total cells was calculated by adding the cell counts obtained for\neach of the respective picoplankton classes together for each sample.\n \nDNA extraction, amplification, pooling, and sequencing: \n DNA was extracted from filters using a sucrose-lysis extraction method and\nQiagen spin-columns (Santoro et al. 2010) Control extractions were also\ncompleted with unused filters (control filters without biomass) in order to\naccount for contamination from the filters or extraction reagents. Lastly,\ndiluted DNA from a synthetic staggered mock community (BEI Resources,\nManassas, VA, USA) was used to account for amplification and sequencing errors\nin downstream microbial community analysis. Coral tissue was removed from the\nskeleton using air-brushing with autoclaved 1% phosphate-buffered-saline (PBS)\nsolution (Apprill et al. 2016; Weber et al. 2017). The coral tissue slurry was\npelleted using a centrifuge and the PBS supernatant was discarded. DNA was\nextracted from each pellet (300 mg of tissue) using a modified version of the\nDNeasy DNA extraction kit protocol (Qiagen, Germantown, MD). The lysis buffer\nin the kit was added to each tube followed by approximately 300 mg of garnet\nbeads (from a MOBIO DNA extraction kit) and 300 mg of Lysing B matrix beads\n(MP Biomedicals, Solon, OH). The tubes were subjected to a bead-beating step\nfor 15 minutes so that the beads could break up the coral tissue (Weber et al.\n2017). After bead-beating, 20 \\u00b5l of proteinase-k was added to each tube\nand the samples were incubated with gentle agitation for 10 minutes at 56\n\\u00b0C. After these modifications, the DNeasy protocol (Qiagen) was followed\nto complete extractions.\n \nExtracts were amplified with barcoded primers targeting the V4 hypervariable\nregion of the bacterial and archaeal small subunit ribosomal RNA gene (Kozich\net al. 2013). The forward primer: 5\\u2019 TATGGTAATTGTGTGYCAGCMGCCGCGGTAA\n3\\u2019 (Parada et al. 2016) and reverse primer: 3\\u2019\nAGTCAGTCAGCCGGACTACNVGGGTWTCTAAT 5\\u2019 (Apprill et al. 2015) were used,\nalong with the barcodes, to amplify and tag each sample prior to pooling. We\nused forward and reverse primers with degeneracies in order to eliminate\namplification biases against Crenarchaeota/ Thaumarchaeota (Parada et al.\n2016)\\u00a0 and SAR 11 (Apprill et al. 2015). Triplicate Polymerase Chain\nReactions (25 l volume) were run with 2 l of DNA template from each sample\nusing the same barcodes in order to minimize the formation of chimeras during\namplification. The reaction conditions included: a 2-minute hot start at 95\n\\u00b0C followed by 36 cycles of 95 \\u00b0C for 20 seconds, 55 \\u00b0C for 15\nseconds, and 72 \\u00b0C for 5 minutes. The final extension step was 72 \\u00b0C\nfor 10 minutes. Triplicate barcoded amplicons were pooled and screened using\ngel electrophoresis to assess the quality and the relative concentration of\namplicons. Amplicons were purified using the MinElute Gel Extraction Kit\n(Qiagen) and pooled to form the sequencing library. The library was sequenced\n(paired-end 2x250 bp) at the Georgia Genomics and Bioinformatics Core with a\nMiseq (Illumina, San Diego, CA) sequencer and raw sequence reads are available\nat the NCBI Sequence Read Archive under BioProject # PRJNA550343.\n \nMicrobial community analyses: \n Raw sequences were quality-filtered and grouped into amplicon sequence\nvariants (ASVs) using DADA2 (Callahan et al. 2016). Reads were filtered,\ntrimmed, dereplicated and error rates were calculated using the program\\u2019s\nparametric error model. The DADA2 algorithm was used to infer the number of\ndifferent ASVs (8357 distinct ASVs), paired reads were merged, an ASV table\nwas constructed, and chimeras were removed (1% of all ASVs). Taxonomy was\nassigned to each ASV using the Silva v.132 reference database (Quast et al.\n2013). Mock communities were used to assess the performance of the program as\nwell as sequencing error rates. DADA2 inferred 15, 17, and 17 strains within\nthe mock community (compared to the 20 expected stains present at different\nconcentrations within the staggered community) and 13, 14, and 14 of the\nstrains were exact matches to the expected sequences from the mock community\nreference file. Sequence recovery is slightly lower than expected, but is\ncomparable to normal performance of DADA2 on this staggered mock community\n(Callahan et al. 2016).\n \nThe R packages Phyloseq (McMurdie and Holmes 2013), Vegan (Oksanen et al.\n2017), DESeq2 (Love et al. 2014), and ggplot2 (Wickham 2016) were used for\ndownstream analysis of the microbial community. Sequences were not subsampled,\nbut samples with less than 1000 reads (2 samples) were removed. In addition,\nASVs identifying as chloroplasts were removed.\\u00a0 Sequences representing\nASVs that identified as \\u201cNA\\u201d at the Phylum level were checked using\nthe SINA aligner and classifier (v.1.2.11) (Pruesse et al. 2012) and then\nremoved if not identified as bacteria or archaea at 70% similarity. The\naverage number of reads across all seawater samples used in microbial\ncommunity analyses was 58,398 (\\u00b1 32,184 standard deviation) with a range\nof 11,502 \\u2013 206,689 reads. The average number of reads in coral tissue\nsamples was 38,096 (\\u00b123,854) with a range of 11,538 \\u2013 59,437 reads.\nDNA extraction control communities were initially inspected and then removed\nbecause they fell out as outliers compared to the highly similar seawater\nmicrobial communities. Taxonomic bar plots, metrics of alpha diversity\n(observed richness of ASVs), and boxplots of alpha diversity were made and\ncalculated using Phyloseq. Alpha diversity was also calculated for samples\nafter Prochlorococcus and Synechococcus ASVs were removed in order to\nunderstand how much their dynamics influenced observed richness. Constrained\nanalysis of principal coordinates (CAP) based on Bray \\u2013 Curtis\ndissimilarity was completed (using \\u2018capscale\\u2019 in Vegan) and variance\npartitioning was used to identify which of the measured environmental\nparameters significantly (p<0.01) contributed to shifts in the microbial\ncommunity composition over time. Permutational Multivariate Analysis of\nVariance using distance matrices (PERMANOVA/Adonis) tests identified\ncategorical factors that significantly (p<0.05) contributed to a similarity\nbetween the microbial communities. DESeq2 was used to identify differentially\nabundant ASVs between day and night as well as reef-associated (reef-depth and\ncoral ecosphere) compared to surface microbial communities (using the\n\\u201clocal\\u201d fitType parameter to estimate gene dispersion). Lastly, the\nRhythmicity Analysis Incorporating Non-parametric methods (RAIN)\\u00a0 R\npackage was used to identify ASVs that experienced rhythmic change in relative\nabundance over a period of 24 hours (Thaben and Westermark 2014). This\nanalysis was completed separately for reef-depth and coral ecosphere seawater\nand the input ASV matrix was center log-ratio transformed and detrended\nfollowing previous methods (Hu et al. 2018). Only ASVs with significant\np-values (p<0.05) after adaptive Benjamini-Hochberg correction were reported\nto control for false recovery rates (Benjamini and Hochberg 2000).\n \nStatistical analyses: \n A Principal Coordinates Analysis (PCA) was completed to summarize changes in\npicoplankton abundances, inorganic nutrient concentrations, and relative light\nand temperature information collected from the HOBO loggers and reduce the\ndimensionality of this data. Separate PCAs were also generated using samples\ncollected during either day or night to observe trends specific to these\ntimes. Kruskal-Wallis rank sums tests were used to test for significant\ndifferences (p<0.05) in alpha diversity between the different sample\ngroupings. Pairwise post-hoc Dunn\\u2019s tests with Bonferonni corrections\nwere used to identify which groups were significantly different from each\nother. These tests were also used to test for significant differences in\npicoplankton cell abundance overtime, between day and night samples, and\nbetween coral ecosphere and reef-depth samples. |
attribute | NC_GLOBAL | awards_0_award_nid | String | 746195 |
attribute | NC_GLOBAL | awards_0_award_number | String | OCE-1736288 |
attribute | NC_GLOBAL | awards_0_data_url | String | http://www.nsf.gov/awardsearch/showAward.do?AwardNumber=1736288 |
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 | Daniel Thornhill |
attribute | NC_GLOBAL | awards_0_program_manager_nid | String | 722161 |
attribute | NC_GLOBAL | cdm_data_type | String | Other |
attribute | NC_GLOBAL | comment | String | Diel, daily, and spatial variation of coral reef seawater microbial communities, US Virgin Islands, 2017 \n PI: A. Apprill (WHOI) \n version date: 2019-08-12 |
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 | 2019-08-14T13:23:09Z |
attribute | NC_GLOBAL | date_modified | String | 2019-08-19T12:17:28Z |
attribute | NC_GLOBAL | defaultDataQuery | String | &time<now |
attribute | NC_GLOBAL | doi | String | 10.1575/1912/bco-dmo.775229.1 |
attribute | NC_GLOBAL | Easternmost_Easting | double | -64.70403 |
attribute | NC_GLOBAL | geospatial_lat_max | double | 41.5265 |
attribute | NC_GLOBAL | geospatial_lat_min | double | 18.30204 |
attribute | NC_GLOBAL | geospatial_lat_units | String | degrees_north |
attribute | NC_GLOBAL | geospatial_lon_max | double | -64.70403 |
attribute | NC_GLOBAL | geospatial_lon_min | double | -70.6731 |
attribute | NC_GLOBAL | geospatial_lon_units | String | degrees_east |
attribute | NC_GLOBAL | infoUrl | String | https://www.bco-dmo.org/dataset/775229 |
attribute | NC_GLOBAL | institution | String | BCO-DMO |
attribute | NC_GLOBAL | instruments_0_acronym | String | Nutrient Autoanalyzer |
attribute | NC_GLOBAL | instruments_0_dataset_instrument_description | String | Used to analyze nutrient samples. |
attribute | NC_GLOBAL | instruments_0_dataset_instrument_nid | String | 775252 |
attribute | NC_GLOBAL | instruments_0_description | String | Nutrient Autoanalyzer is a generic term used when specific type, make and model were not specified. In general, a Nutrient Autoanalyzer is an automated flow-thru system for doing nutrient analysis (nitrate, ammonium, orthophosphate, and silicate) on seawater samples. |
attribute | NC_GLOBAL | instruments_0_instrument_external_identifier | String | https://vocab.nerc.ac.uk/collection/L05/current/LAB04/ |
attribute | NC_GLOBAL | instruments_0_instrument_name | String | Nutrient Autoanalyzer |
attribute | NC_GLOBAL | instruments_0_instrument_nid | String | 558 |
attribute | NC_GLOBAL | instruments_0_supplied_name | String | A continuous segmented flow-system |
attribute | NC_GLOBAL | instruments_1_acronym | String | Automated Sequencer |
attribute | NC_GLOBAL | instruments_1_dataset_instrument_description | String | Used to obtain genetic data. |
attribute | NC_GLOBAL | instruments_1_dataset_instrument_nid | String | 775254 |
attribute | NC_GLOBAL | instruments_1_description | String | General term for a laboratory instrument used for deciphering the order of bases in a strand of DNA. Sanger sequencers detect fluorescence from different dyes that are used to identify the A, C, G, and T extension reactions. Contemporary or Pyrosequencer methods are based on detecting the activity of DNA polymerase (a DNA synthesizing enzyme) with another chemoluminescent enzyme. Essentially, the method allows sequencing of a single strand of DNA by synthesizing the complementary strand along it, one base pair at a time, and detecting which base was actually added at each step. |
attribute | NC_GLOBAL | instruments_1_instrument_name | String | Automated DNA Sequencer |
attribute | NC_GLOBAL | instruments_1_instrument_nid | String | 649 |
attribute | NC_GLOBAL | instruments_1_supplied_name | String | Miseq (Illumina, San Diego, CA) sequencer |
attribute | NC_GLOBAL | instruments_2_acronym | String | Flow Cytometer |
attribute | NC_GLOBAL | instruments_2_dataset_instrument_description | String | Used for measuring cell concentrations. Samples collected for flow cytometry were analyzed using colinear analysis (laser excitation wavelength of 488 nm, UV) on an Altra flow cytometer (Beckman Coulter, Pasadena, CA.). |
attribute | NC_GLOBAL | instruments_2_dataset_instrument_nid | String | 775253 |
attribute | NC_GLOBAL | instruments_2_description | String | Flow cytometers (FC or FCM) are automated instruments that quantitate properties of single cells, one cell at a time. They can measure cell size, cell granularity, the amounts of cell components such as total DNA, newly synthesized DNA, gene expression as the amount messenger RNA for a particular gene, amounts of specific surface receptors, amounts of intracellular proteins, or transient signalling events in living cells.\n(from: http://www.bio.umass.edu/micro/immunology/facs542/facswhat.htm) |
attribute | NC_GLOBAL | instruments_2_instrument_external_identifier | String | https://vocab.nerc.ac.uk/collection/L05/current/LAB37/ |
attribute | NC_GLOBAL | instruments_2_instrument_name | String | Flow Cytometer |
attribute | NC_GLOBAL | instruments_2_instrument_nid | String | 660 |
attribute | NC_GLOBAL | instruments_3_dataset_instrument_description | String | Measured temperature and relative light level. |
attribute | NC_GLOBAL | instruments_3_dataset_instrument_nid | String | 775251 |
attribute | NC_GLOBAL | instruments_3_description | String | Records temperature data over a period of time. |
attribute | NC_GLOBAL | instruments_3_instrument_name | String | Temperature Logger |
attribute | NC_GLOBAL | instruments_3_instrument_nid | String | 639396 |
attribute | NC_GLOBAL | instruments_3_supplied_name | String | Light temperature loggers (8K HOBO/PAR loggers; Onset, Wareham, MA) |
attribute | NC_GLOBAL | keywords | String | accession, ammonia, ammonium, Ammonium_uM, bco, bco-dmo, bio, biological, cells, chemical, chemistry, collection, Collection_Date, Collection_location, Collection_time, colony, concentration, coral, Coral_Colony_or_sand, data, dataset, date, depth, Depth_Feet, dmo, earth, Earth Science > Oceans > Ocean Chemistry > Ammonia, Earth Science > Oceans > Ocean Chemistry > Nitrate, Earth Science > Oceans > Ocean Chemistry > Phosphate, Earth Science > Oceans > Ocean Chemistry > Silicate, erddap, latitude, levels, light, longitude, management, mass, mass_concentration_of_phosphate_in_sea_water, mass_concentration_of_silicate_in_sea_water, mole, mole_concentration_of_ammonium_in_sea_water, mole_concentration_of_nitrate_in_sea_water, mole_concentration_of_nitrite_in_sea_water, n02, ncbi, NCBI_BioProject_accession_number, NCBI_BioSample_accession_number, nh4, nitrate, Nitrate_uM, nitrite, Nitrite_uM, no3, number, ocean, oceanography, oceans, office, phosphate, Phosphate_uM, picoeukaryotes, Picoeukaryotes_cells_mL, po4, preliminary, prochlorococcus, Prochlorococcus_cells_mL, project, relative, Relative_light_levels, sample, Sample_ID, Sample_type, sand, science, sea, seawater, silicate, Silicate_uM, synechococcus, Synechococcus_cells_mL, temperature, Temperature_F, time, type, unpigmented, Unpigmented_cells_cells_mL, water |
attribute | NC_GLOBAL | keywords_vocabulary | String | GCMD Science Keywords |
attribute | NC_GLOBAL | license | String | https://www.bco-dmo.org/dataset/775229/license |
attribute | NC_GLOBAL | metadata_source | String | https://www.bco-dmo.org/api/dataset/775229 |
attribute | NC_GLOBAL | Northernmost_Northing | double | 41.5265 |
attribute | NC_GLOBAL | param_mapping | String | {'775229': {'Depth_Feet': 'master - depth', 'lat': 'master - latitude', 'lon': 'master - longitude'}} |
attribute | NC_GLOBAL | parameter_source | String | https://www.bco-dmo.org/mapserver/dataset/775229/parameters |
attribute | NC_GLOBAL | people_0_affiliation | String | Woods Hole Oceanographic Institution |
attribute | NC_GLOBAL | people_0_affiliation_acronym | String | WHOI |
attribute | NC_GLOBAL | people_0_person_name | String | Amy Apprill |
attribute | NC_GLOBAL | people_0_person_nid | String | 553489 |
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 |
attribute | NC_GLOBAL | people_1_person_name | String | Laura Weber |
attribute | NC_GLOBAL | people_1_person_nid | String | 662109 |
attribute | NC_GLOBAL | people_1_role | String | Contact |
attribute | NC_GLOBAL | people_1_role_type | String | related |
attribute | NC_GLOBAL | people_2_affiliation | String | Woods Hole Oceanographic Institution |
attribute | NC_GLOBAL | people_2_affiliation_acronym | String | WHOI BCO-DMO |
attribute | NC_GLOBAL | people_2_person_name | String | Nancy Copley |
attribute | NC_GLOBAL | people_2_person_nid | String | 50396 |
attribute | NC_GLOBAL | people_2_role | String | BCO-DMO Data Manager |
attribute | NC_GLOBAL | people_2_role_type | String | related |
attribute | NC_GLOBAL | project | String | Coral Exometabolomes |
attribute | NC_GLOBAL | projects_0_acronym | String | Coral Exometabolomes |
attribute | NC_GLOBAL | projects_0_description | String | NSF abstract:\nCoral reefs are some of the most diverse and productive ecosystems in the ocean. Globally, reefs have declined in stony (reef-building) coral abundance due to environmental variations, and in the Caribbean this decline has coincided with an increase in octocoral (soft coral) abundance. This phase shift occurring on Caribbean reefs may be impacting the interactions between the sea floor and water column and particularly between corals and picoplankton. Picoplankton are the microorganisms in the water column that utilize organic matter released from corals to support their growth. These coral-picoplankton interactions are relatively unstudied, but could have major implications for reef ecology and coral health. This project will take place in the U.S. territory of the Virgin Islands (USVI) and will produce the first detailed knowledge about the chemical diversity and composition of organic matter released from diverse stony coral and octocoral species. This project will advance our understanding of coral reef microbial ecology by allowing us to understand how different coral metabolites impact picoplankton growth and dynamics over time. The results from this project will be made publically accessible in a freely available online magazine, and USVI minority middle and high school students will be exposed to a lesson about chemical-biological interactions on coral reefs through established summer camps. This project will also contribute to the training of USVI minority undergraduates as well as a graduate student.\nCoral exometabolomes, which are the sum of metabolic products of the coral together with its microbiome, are thought to structure picoplankton communities in a species-specific manner. However, a detailed understanding of coral exometabolomes, and their influences on reef picoplankton, has not yet been obtained. This project will utilize controlled aquaria-based experiments with stony corals and octocorals, foundational species of Caribbean reef ecosystems, to examine how the exometabolomes of diverse coral species differentially influence the reef picoplankton community. Specifically, this project will capitalize on recent developments in mass spectrometry-based metabolomics to define the signature exometabolomes of ecologically important and diverse stony corals and octocorals. Secondly, this project will determine how the exometabolomes of these corals vary with factors linked to coral taxonomy as well as the coral-associated microbiome (Symbiodinium algae, bacteria and archaea). With this new understanding of coral exometabolomes, the project will then apply a stable isotope probe labeling approach to the coral exometabolome and will examine if and how (through changes in growth and activity) the seawater picoplankton community incorporates coral exometabolomes from different coral species over time. This project will advance our ability to evaluate the role that coral exometabolomes play in contributing to benthic-picoplankton interactions on changing Caribbean reefs. |
attribute | NC_GLOBAL | projects_0_end_date | String | 2020-09 |
attribute | NC_GLOBAL | projects_0_geolocation | String | U.S. Virgin Islands |
attribute | NC_GLOBAL | projects_0_name | String | Signature exometabolomes of Caribbean corals and influences on reef picoplankton |
attribute | NC_GLOBAL | projects_0_project_nid | String | 746196 |
attribute | NC_GLOBAL | projects_0_start_date | String | 2017-10 |
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 | Southernmost_Northing | double | 18.30204 |
attribute | NC_GLOBAL | standard_name_vocabulary | String | CF Standard Name Table v55 |
attribute | NC_GLOBAL | subsetVariables | String | NCBI_BioProject_accession_number |
attribute | NC_GLOBAL | summary | String | Bacterial and archaeal diversity and composition, microbial cell abundances, inorganic nutrient concentrations, and physicochemical conditions were determined and measured in coral reef seawater over a three-day, diel time series on one reef in St. John, U.S. Virgin Islands. |
attribute | NC_GLOBAL | title | String | [Coral reef seawater microbial communities] - Diel, daily, and spatial variation of coral reef seawater microbial communities from US Virgin Islands, 2017 (Signature exometabolomes of Caribbean corals and influences on reef picoplankton) |
attribute | NC_GLOBAL | version | String | 1 |
attribute | NC_GLOBAL | Westernmost_Easting | double | -70.6731 |
attribute | NC_GLOBAL | xml_source | String | osprey2erddap.update_xml() v1.3 |
variable | Sample_ID | String | ||
attribute | Sample_ID | bcodmo_name | String | sample |
attribute | Sample_ID | description | String | sample identifier |
attribute | Sample_ID | long_name | String | Sample ID |
attribute | Sample_ID | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P02/current/ACYC/ |
attribute | Sample_ID | units | String | unitless |
variable | NCBI_BioProject_accession_number | String | ||
attribute | NCBI_BioProject_accession_number | bcodmo_name | String | accession number |
attribute | NCBI_BioProject_accession_number | description | String | NCBI BioProject accession number |
attribute | NCBI_BioProject_accession_number | long_name | String | NCBI Bio Project Accession Number |
attribute | NCBI_BioProject_accession_number | units | String | unitless |
variable | NCBI_BioSample_accession_number | String | ||
attribute | NCBI_BioSample_accession_number | bcodmo_name | String | accession number |
attribute | NCBI_BioSample_accession_number | description | String | NCBI BioSample accession number |
attribute | NCBI_BioSample_accession_number | long_name | String | NCBI Bio Sample Accession Number |
attribute | NCBI_BioSample_accession_number | units | String | unitless |
variable | Sample_type | String | ||
attribute | Sample_type | bcodmo_name | String | sample_type |
attribute | Sample_type | description | String | Sample type |
attribute | Sample_type | long_name | String | Sample Type |
attribute | Sample_type | units | String | unitless |
variable | Coral_Colony_or_sand | String | ||
attribute | Coral_Colony_or_sand | bcodmo_name | String | sample |
attribute | Coral_Colony_or_sand | description | String | Coral Colony or sand identifier |
attribute | Coral_Colony_or_sand | long_name | String | Coral Colony Or Sand |
attribute | Coral_Colony_or_sand | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P02/current/ACYC/ |
attribute | Coral_Colony_or_sand | units | String | unitless |
variable | Collection_time | String | ||
attribute | Collection_time | bcodmo_name | String | time |
attribute | Collection_time | description | String | Collection time (day or night) and day relative to the start of the study |
attribute | Collection_time | long_name | String | Collection Time |
attribute | Collection_time | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P01/current/AHMSAA01/ |
attribute | Collection_time | units | String | unitless |
variable | Collection_Date | String | ||
attribute | Collection_Date | bcodmo_name | String | date |
attribute | Collection_Date | description | String | Collection Date; fomatted as Mon-yyyy |
attribute | Collection_Date | long_name | String | Collection Date |
attribute | Collection_Date | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P01/current/ADATAA01/ |
attribute | Collection_Date | units | String | unitless |
variable | Collection_location | String | ||
attribute | Collection_location | bcodmo_name | String | site |
attribute | Collection_location | description | String | Collection location |
attribute | Collection_location | long_name | String | Collection Location |
attribute | Collection_location | units | String | unitless |
variable | latitude | double | ||
attribute | latitude | _CoordinateAxisType | String | Lat |
attribute | latitude | _FillValue | double | NaN |
attribute | latitude | actual_range | double | 18.30204, 41.5265 |
attribute | latitude | axis | String | Y |
attribute | latitude | bcodmo_name | String | latitude |
attribute | latitude | colorBarMaximum | double | 90.0 |
attribute | latitude | colorBarMinimum | double | -90.0 |
attribute | latitude | description | String | latitude; north is positive |
attribute | latitude | ioos_category | String | Location |
attribute | latitude | long_name | String | Latitude |
attribute | latitude | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P09/current/LATX/ |
attribute | latitude | standard_name | String | latitude |
attribute | latitude | units | String | degrees_north |
variable | longitude | double | ||
attribute | longitude | _CoordinateAxisType | String | Lon |
attribute | longitude | _FillValue | double | NaN |
attribute | longitude | actual_range | double | -70.6731, -64.70403 |
attribute | longitude | axis | String | X |
attribute | longitude | bcodmo_name | String | longitude |
attribute | longitude | colorBarMaximum | double | 180.0 |
attribute | longitude | colorBarMinimum | double | -180.0 |
attribute | longitude | description | String | longitude; east is postive |
attribute | longitude | ioos_category | String | Location |
attribute | longitude | long_name | String | Longitude |
attribute | longitude | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P09/current/LONX/ |
attribute | longitude | standard_name | String | longitude |
attribute | longitude | units | String | degrees_east |
variable | Prochlorococcus_cells_mL | int | ||
attribute | Prochlorococcus_cells_mL | _FillValue | int | 2147483647 |
attribute | Prochlorococcus_cells_mL | actual_range | int | 11250, 47419 |
attribute | Prochlorococcus_cells_mL | bcodmo_name | String | cell_concentration |
attribute | Prochlorococcus_cells_mL | description | String | concentration of Prochlorococcus |
attribute | Prochlorococcus_cells_mL | long_name | String | Prochlorococcus Cells M L |
attribute | Prochlorococcus_cells_mL | units | String | cell/milliliter |
variable | Synechococcus_cells_mL | int | ||
attribute | Synechococcus_cells_mL | _FillValue | int | 2147483647 |
attribute | Synechococcus_cells_mL | actual_range | int | 27721, 79875 |
attribute | Synechococcus_cells_mL | bcodmo_name | String | cell_concentration |
attribute | Synechococcus_cells_mL | description | String | concentration of Synechococcus |
attribute | Synechococcus_cells_mL | long_name | String | Synechococcus Cells M L |
attribute | Synechococcus_cells_mL | units | String | cell/milliliter |
variable | Picoeukaryotes_cells_mL | short | ||
attribute | Picoeukaryotes_cells_mL | _FillValue | short | 32767 |
attribute | Picoeukaryotes_cells_mL | actual_range | short | 440, 4331 |
attribute | Picoeukaryotes_cells_mL | bcodmo_name | String | cell_concentration |
attribute | Picoeukaryotes_cells_mL | description | String | concentration of Picoeukaryotes |
attribute | Picoeukaryotes_cells_mL | long_name | String | Picoeukaryotes Cells M L |
attribute | Picoeukaryotes_cells_mL | units | String | cell/milliliter |
variable | Unpigmented_cells_cells_mL | int | ||
attribute | Unpigmented_cells_cells_mL | _FillValue | int | 2147483647 |
attribute | Unpigmented_cells_cells_mL | actual_range | int | 397448, 802850 |
attribute | Unpigmented_cells_cells_mL | bcodmo_name | String | cell_concentration |
attribute | Unpigmented_cells_cells_mL | description | String | concentration of unpigmented cells |
attribute | Unpigmented_cells_cells_mL | long_name | String | Unpigmented Cells Cells M L |
attribute | Unpigmented_cells_cells_mL | units | String | cell/milliliter |
variable | Phosphate_uM | float | ||
attribute | Phosphate_uM | _FillValue | float | NaN |
attribute | Phosphate_uM | actual_range | float | 0.13, 1.465 |
attribute | Phosphate_uM | bcodmo_name | String | PO4 |
attribute | Phosphate_uM | description | String | concentration of Phosphate_uM |
attribute | Phosphate_uM | long_name | String | Mass Concentration Of Phosphate In Sea Water |
attribute | Phosphate_uM | units | String | micromoles |
variable | Silicate_uM | float | ||
attribute | Silicate_uM | _FillValue | float | NaN |
attribute | Silicate_uM | actual_range | float | 0.3, 13.7 |
attribute | Silicate_uM | bcodmo_name | String | SiOH_4 |
attribute | Silicate_uM | description | String | concentration of Silicate_uM |
attribute | Silicate_uM | long_name | String | Mass Concentration Of Silicate In Sea Water |
attribute | Silicate_uM | units | String | micromoles |
variable | Nitrate_uM | float | ||
attribute | Nitrate_uM | _FillValue | float | NaN |
attribute | Nitrate_uM | actual_range | float | -0.001, 0.4004 |
attribute | Nitrate_uM | bcodmo_name | String | NO3 |
attribute | Nitrate_uM | colorBarMaximum | double | 50.0 |
attribute | Nitrate_uM | colorBarMinimum | double | 0.0 |
attribute | Nitrate_uM | description | String | concentration of Nitrate_uM |
attribute | Nitrate_uM | long_name | String | Mole Concentration Of Nitrate In Sea Water |
attribute | Nitrate_uM | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P01/current/NTRAIGGS/ |
attribute | Nitrate_uM | units | String | micromoles |
variable | Nitrite_uM | float | ||
attribute | Nitrite_uM | _FillValue | float | NaN |
attribute | Nitrite_uM | actual_range | float | -0.02, 0.08 |
attribute | Nitrite_uM | bcodmo_name | String | NO2 |
attribute | Nitrite_uM | colorBarMaximum | double | 1.0 |
attribute | Nitrite_uM | colorBarMinimum | double | 0.0 |
attribute | Nitrite_uM | description | String | concentration of Nitrite_uM |
attribute | Nitrite_uM | long_name | String | Mole Concentration Of Nitrite In Sea Water |
attribute | Nitrite_uM | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P01/current/NTRIAAZX/ |
attribute | Nitrite_uM | units | String | micromoles |
variable | Ammonium_uM | float | ||
attribute | Ammonium_uM | _FillValue | float | NaN |
attribute | Ammonium_uM | actual_range | float | 0.13, 2.23 |
attribute | Ammonium_uM | bcodmo_name | String | Ammonium |
attribute | Ammonium_uM | colorBarMaximum | double | 5.0 |
attribute | Ammonium_uM | colorBarMinimum | double | 0.0 |
attribute | Ammonium_uM | description | String | concentration of Ammonium_uM |
attribute | Ammonium_uM | long_name | String | Mole Concentration Of Ammonium In Sea Water |
attribute | Ammonium_uM | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P01/current/AMONAAZX/ |
attribute | Ammonium_uM | units | String | micromoles |
variable | Temperature_F | float | ||
attribute | Temperature_F | _FillValue | float | NaN |
attribute | Temperature_F | actual_range | float | 85.014, 86.641 |
attribute | Temperature_F | bcodmo_name | String | temperature |
attribute | Temperature_F | description | String | Temperature |
attribute | Temperature_F | long_name | String | Temperature F |
attribute | Temperature_F | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P01/current/TEMPP901/ |
attribute | Temperature_F | units | String | degrees Fahrenheit |
variable | Depth_Feet | double | ||
attribute | Depth_Feet | _FillValue | double | NaN |
attribute | Depth_Feet | actual_range | double | 23.0, 28.0 |
attribute | Depth_Feet | bcodmo_name | String | depth |
attribute | Depth_Feet | colorBarMaximum | double | 8000.0 |
attribute | Depth_Feet | colorBarMinimum | double | -8000.0 |
attribute | Depth_Feet | colorBarPalette | String | TopographyDepth |
attribute | Depth_Feet | description | String | Depth |
attribute | Depth_Feet | long_name | String | Depth |
attribute | Depth_Feet | nerc_identifier | String | https://vocab.nerc.ac.uk/collection/P09/current/DEPH/ |
attribute | Depth_Feet | standard_name | String | depth |
attribute | Depth_Feet | units | String | feet |
variable | Relative_light_levels | short | ||
attribute | Relative_light_levels | _FillValue | short | 32767 |
attribute | Relative_light_levels | actual_range | short | 0, 864 |
attribute | Relative_light_levels | bcodmo_name | String | unknown |
attribute | Relative_light_levels | description | String | Relative_light_levels |
attribute | Relative_light_levels | long_name | String | Relative Light Levels |
attribute | Relative_light_levels | units | String | lumens/foot^2 |