Contributors | Affiliation | Role |
---|---|---|
Lasker, Howard | State University of New York at Buffalo (SUNY Buffalo) | Principal Investigator |
Edmunds, Peter J. | California State University Northridge (CSUN) | Co-Principal Investigator |
Wells, Christopher | Bowdoin College (Bowdoin-Schiller) | Scientist |
York, Amber D. | Woods Hole Oceanographic Institution (WHOI BCO-DMO) | BCO-DMO Data Manager |
Survey design:
All sites were located at 6 to 9 meters depth.
Censuses at East Cabritte, Europa, and Tektite were based on 50x10m areas that were arbitrarily selected and permanently marked with stainless steel eyebolts at the corners of the sites. A total of six transect lines, also marked with eyebolts, were laid out at 10 m intervals. All octocorals present in 1 x 1 m quadrats along the 10-meter long transects were scored. The transect identifier "transect_pos" has values 0, 10, 20, 30, 40 or 50 which represent position in meters within the 50x10 survey area corresponding to each of the 6 transects (e.g. 20 = 20m).
The census at Booby Rock was conducted in a single day in which transects were randomly placed along a 50 m line that was arbitrarily placed on a constant depth contour. The transect identifier (transect_pos) for transects at Booby Rock refers to position along the 50 m line.
Yawzi and Deep Tektite surveys: 20 quadrats at each transect (3 transects). Yawzi transects were censused over two field trips, July/August and September.
Sampling methods:
Identifications were based on traits visible in the field, and samples of representative colonies were collected for further analysis in cases in which field identification was uncertain. Sclerites from those samples were examined for species identification.
Two height measures are present, height of living tissue, which only includes that part of the axis with living tissue and total height which is the distance from the base to the tip of the farthest branch from the base (i.e. not necessarily perpendicular to the substrate), regardless of whether the tips or base had living tissue. (Only colonies with some living tissue were measured). All measures rounded to the nearest cm with the exception of 5 cm which only includes colonies >= 5 cm. Starting in 2016, measures less than 5 cm reflect colonies with thick branches which could only have <5 cm heights due to partial mortality.
Notes about identifications/codes:
Octocoral adults are defined as individuals >= 5 cm height. With height determined to the nearest cm
LINES WITH NO SPECIES ENTRY IDENTIFY QUADRATS IN WHICH NO OCTOCORALS WERE PRESENT- This is also noted in the comment columns as "No colonies present."
Field identifications of Eunicea mammosa, E. laxispica and E. succinea are sometimes difficult, thus, for analysis purposes the three species are lumped as a single group.
Field identifications of Pseudoplexaura flagellosa and P. wagenaari are difficult, thus, for analysis purposes the three species are lumped as a single group.
Species_Code aa2 is an undescribed Antillogorgia sp. that is very similar to A. americana and is lumped with A. american for analysis purposes.
Field identifications of Muricea muricata and M. atlantica are difficult, thus, for analysis purposes the three species are lumped as a single group.
Notes about Comments columns in this dataset:
Millepora present: Inicates millepora overgrowing naked axis
Cyanobacteria present: Indicates Cyanobacteria growing on the colony.
Spo or Sponge indicates sponge growing on the colony, most commonly on bare axis
"pale" or "bleached" indicates partial or complete bleaching of some branches on the colony
"ophio" or "Ophiothela" indicates the presence of Ophiothela mirabilis on the colony
oyster indicates the presence of oyster(s) growing on the axis of the colony
"fallen" indicates the colony has fallen over but there is living tissue. Heights are based on the length of the living tissue on the substrate measured as if the colony were erect.
"Ophiothrix" indicates the presences of an "Ophiothrix sp." on the colony
"damselfish" indicates the colony was in a damselfish territory and some branches were being "farmed" by the damselfish
See "Parameters" section for more information about each column in this dataset.
* Sheet 1 "Adult_Surveys" of submitted file "2024_St John_adult_censuses for BCO-DMO.xlsx" was imported into the BCO-DMO data system as the main table for this dataset. Table will appear as Data File: 956712_v1_st-john-octocoral-height-2024.csv (along with other download format options).
* Column names adjusted to conform to BCO-DMO naming conventions designed to support broad re-use by a variety of research tools and scripting languages. [Only numbers, letters, and underscores. Can not start with a number]
* Date converted to ISO 8601 format
* Site name in the data table was revised from "Yawzi" to "Yawzi Point" as described in the provided site list and for consistency with other datasets. Latitude and Longitude joined into the octocoral height data table using this site list (joined on site name).
* World Register of Marine Species taxa match tool used (on 2025-03-21) to verify the correct spelling of species names were used and to match them to a Life Science Identifier (LSID). Not all matched the currently accepted name which may change over time. However all names were matched to identifiers for curation purposes. Incorrect spellings of species names were brought to the attention of the data submitter and were corrected in the octocoral height data:
The BCO-DMO data manager made two changes in the octocoral height data table 956712_v1_st-john-octocoral-height-2024.csv
Spelling of name: "Plexaura kukenthali"
corrected to: "Plexaura kuekenthali" (urn:lsid:marinespecies.org:taxname:290798) which is the currently accepted name of the junior synonym "Plexaura homomalla f. kuekenthali Moser, 1921" (see more at World Register of Marine Species (WoRMS) https://www.marinespecies.org/aphia.php?p=taxdetails&id=290798
Category: "Eunicea lacinata"
corrected to: "Eunicea laciniata" (urn:lsid:marinespecies.org:taxname:283250)
Additional columns for lowest identifiable taxon for the identified categories and the LSID for that lowest taxon were added to the data table. LSIDs for the Genus column were also added.
Supplemental species code tables (species_code_table1.csv, and species_code_tabld2.csv):
These were two different species code tables provided in sheet "Species codes" in provided excel file "2024_St John_adult_censuses for BCO-DMO.xlsx." The two tables were extracted from the sheet and added to this dataset as two separate supplemental files.
Disambiguation and usage of the two tables has been requested of the data submitter. Since there are more categories listed than are in the dataset it is assumed these are lists the project used and only the categories that appeared in 2024 are in the dataset. There were identified issues with inconsistent names and misspelled species names. They have been attached to this dataset as provided to BCO-DMO.
Parameter | Description | Units |
line | Transect line identifier | unitless |
Census_Year | year in which the data were collected | unitless |
Date | Date on which data were collected | unitless |
Site | Site name (Census location name) | unitless |
latitude | Site latitude | decimal degrees |
longitude | Site longitude | decimal degrees |
Transect_Position | Transect postiion. At Grootpan Bay, Europa, and Tektite transects positioned in a marked 50x10m area, with stainless steel eye bolts marking each corner, and each of the 6 transect. Transects were 10m long across the 50x10m area, with transect poistions at 0m; 10m; 20m; 30m; 40m; 50m. - Transect position at Booby Rock corresponds to the randomly selected meter mark along a transect line laid parallel to the 7 m depth contour. Transect postion at Deep Tektite and Yawzi are numbered 1 to 3, corresponding to parallel transects that had been set up approximately 10 m from each other. | unitless |
Meter_on_transect | From 0m to 9m. 1x1m quadrats were positioned randomly along the 10 m transect. The values refer to the position of the "shoreward" edge of the quadrat. Thus "0"refers to the quadrat placed between the 0 and 1 meter marks | unitless |
Side_of_transect | Side of the transect tape (Left or Right), orientation looking towards open ocean, with the nearest shore to the back. | unitless |
Meter_Side | undocumented | unitless |
Quadrat | Quadrat identifier | unitless |
Genus | Genus of the category provided in column Revised_species | unitless |
Species_code | Octocorals species code (corresponds to "Field_Code" in supplmental code lists) | unitless |
Revised_Species_code | Octocorals species acronyms (revised). | unitless |
Revised_species | Identification category associated with the revised code, includes taxonomic name and may also include category description such as "Briareum asbestinum (encrusting)" | unitless |
Maximun_height_from_base | Total height. Maximum distance from the base of the octocoral colony until the farthest tips of the longest branch regardless of whether there was living tissue on the branch. The measurement was not necessarily perpendicular to the substrate. All measures rounded to the nearest cm. | centimeters (cm) |
Height_of_living_tissue | Height of Living Tissue (cm): Maximum distance from the base of the octocoral colony to the farthest tips of the longest branch with living tissue (i.e. not necessarily perpendicular to the substrate). All measures rounded to the nearest cm with the exception of 5 cm which only includes colonies >= 5 cm. Measures less than 5 cm reflect colonies with thick branches which could only have <5 cm heights due to partial mortality. | centimeters (cm) |
Basal_damage | Basal damage. height (cm) from the base of the colony to living tissue. This value is 0.0 for colonies that have no damage to their base. | centimeters (cm) |
Colony_damage_score | Damage score. Damage = 1 when < 25% of the colony have injuries, Damage = 2 when injuries are in > 25% but < 50% of the colony , Damage = 3 when in juries are > 50% of the colony but < 75%, and Damage = 4 when a colony has injuries in > 75% of the colony. | unitless |
Number_of_Cyphoma | Number of Cyphoma spp. present on the colony. Unless noted in Comments individuals are C. gibbosum per colony | unitless |
Comments_1 | Comments (See Methods & Sampling section for more information) | unitless |
Comments_2_sample_tag_num | undocumented | unitless |
Lowest_Taxon_For_Category | Lowest identifiable taxon for the category provided in "Revised_species" column. For example "Briareum asbestinum" for Revised_species category "Briareum asbestinum (encrusting)." | unitless |
Lowest_Taxon_LSID | Life Science Identifier (LSID) corresponding to Lowest_Taxon_For_Category | unitless |
Genus_LSID | Life Science Identifier (LSID) for the name in the Genus column | unitless |
NSF Award Abstract:
Coral reefs are exposed to a diversity of natural and anthropogenic disturbances, and the consequences for ecosystem degradation have been widely publicized. However, the reported changes have been biased towards fishes and stony corals, and for Caribbean reefs, the most notable example of this bias are octocorals ("soft corals"). Although they are abundant and dominate many Caribbean reefs, they are rarely included in studies due to the difficulty of both identifying them and in quantifying their abundances. In some places there is compelling evidence that soft corals have increased in abundance, even while stony corals have become less common. This suggests that soft corals are more resilient than stony corals to the wide diversity of disturbances that have been impacting coral corals. The best coral reefs on which to study these changes are those that have been studied for decades and can provide a decadal context to more recent events, and in this regard the reefs of St. John, US Virgin Islands are unique. Stony corals on the reefs have been studied since 1987, and the soft corals from 2014. This provides unrivalled platform to evaluate patterns of octocoral abundance and recruitment; identify the patterns of change that are occurring on these reefs, and identify the processes responsible for the resilience of octocoral populations. The project will extend soft coral monitoring from 4 years to 8 years, and within this framework will examine the roles of baby corals, and their response to seafloor roughness, seawater flow, and seaweed, in determining the success of soft corals. The work will also assess whether the destructive effects of Hurricanes Irma and Maria have modified the pattern of change. In concert with these efforts the project will be closely integrated with local high schools at which the investigators will host marine biology clubs and provide independent study opportunities for their students and teachers. Unique training opportunities will be provided to undergraduate and graduate students, as well as a postdoctoral researcher, all of whom will study and work in St. John, and the investigators will train coral reef researchers to identify the species of soft corals through a hands-on workshop to be conducted in the Florida Keys.
Understanding how changing environmental conditions will affect the community structure of major biomes is the ecological objective defining the 21st century. The holistic effects of these conditions on coral reefs will be studied on shallow reefs within the Virgin Islands National Park in St. John, US Virgin Islands, which is the site of one of the longest-running, long-term studies of coral reef community dynamics in the region. With NSF-LTREB support, the investigators have been studying long-term changes in stony coral communities in this location since 1987, and in 2014 NSF-OCE support was used to build an octocoral "overlay" to this decadal perspective. The present project extends from this unique history, which has been punctuated by the effects of Hurricanes Irma and Maria, to place octocoral synecology in a decadal context, and the investigators exploit a rich suite of legacy data to better understand the present and immediate future of Caribbean coral reefs. This four-year project will advance on two concurrent fronts: first, to extend time-series analyses of octocoral communities from four to eight years to characterize the pattern and pace of change in community structure, and second, to conduct a program of hypothesis-driven experiments focused on octocoral settlement that will uncover the mechanisms allowing octocorals to more effectively colonize substrata than scleractinian corals on present day reefs. Specifically, the investigators will conduct mensurative and manipulative experiments addressing four hypotheses focusing on the roles of: (1) habitat complexity in distinguishing between octocoral and scleractinian recruitment niches, (2) the recruitment niche in mediating post-settlement success, (3) competition in algal turf and macroalgae in determining the success of octocoral and scleractian recruits, and (4) role of octocoral canopies in modulating the flux of particles and larvae to the seafloor beneath. The results of this study will be integrated to evaluate the factors driving higher ecological resilience of octocorals versus scleractinians on present-day Caribbean reefs.
This award reflects NSF's statutory mission and has been deemed worthy of support through evaluation using the Foundation's intellectual merit and broader impacts review criteria.
Funding Source | Award |
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NSF Division of Ocean Sciences (NSF OCE) |