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        <gco:CharacterString>NCRMP CORAL DEMOGRAPHIC DATA HAS NOW BEEN MERGED INTO A PACIFIC-WIDE METADATA RECORD -- PLEASE REFER TO https://www.fisheries.noaa.gov/inport/item/71550 FOR MOST UPDATED DATA.  

The data described here result from benthic coral demographic surveys within belt transects of specified length and width for two life stages (juveniles and adults) across American Samoa since 2015. The data provide information on adult coral colony counts, morphology, size, partial mortality (old and recent dead), presence and causation of disease and other compromised health conditions, including bleaching. Juvenile colony surveys include morphology and size. Taxonomic identification of adult colonies is to the species level and genus level for juveniles. In 2023, some segment observations were repeated for internal quality control; to filter for non-repeated data, be certain filter for TRANSECTNUM = 1. 

A two-stage stratified random sampling (StRS) design was employed to survey the coral reef ecosystems of American Samoa in 2015, and starting in 2018 a one-stage StRS design was employed. The survey domain encompassed the majority of the mapped area of reef and hard bottom habitats in the 0 - 30 m depth range. The stratification scheme included island, reef zone, and depth (i.e., shallow: &gt;0 -  6 m; mid-depth: &gt; 6 -18 m; and deep: &gt;18 - 30 m), as well as reef zone (i.e., forereef, backreef, and lagoon; backreef only at Rose Atoll and Tutuila, and lagoon only at Rose Atoll). Sampling effort allocation was determined based on strata area and sites randomly located within strata. 

The StRS design effectively reduces estimate variance through stratification using environmental covariates and by sampling more sites rather than more transects per site. Therefore, site-level estimates and site-to-site comparisons should proceed with caution.

The data were collected as part of the NOAA Pacific Islands Fisheries Science Center (PIFSC) and Ecosystem Sciences Division (ESD; formerly the Coral Reef Ecosystem Division) led National Coral Reef Monitoring Program (NCRMP) missions to American Samoa.</gco:CharacterString>
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                <gco:CharacterString>At each site, benthic Rapid Ecological Assessment (REA) surveys were conducted within two 10 sq. meter belt transects in 2015 and within one 10 sq. meter belt transect after 2018. Transects were 18 meters in length. Adult coral colonies (&gt;=5 cm) were surveyed within four (1.0 x 2.5 m) segments at 5 meter increments along the 18 meter transect in the following manner: 0-2.5 m (segment 1); 5.0-7.5 m (segment 3); 10-12.5 m (segment 5); and 15-17.5 m (segment 7). All colonies whose center fell within 0.5 m on either side of each transect line were identified to lowest taxonomic level possible (species or genus), measured for size (maximum diameter to nearest cm), and morphology was noted. In addition, partial mortality and condition of each colony was assessed. Partial mortality was estimated as percent of the colony in terms of old dead and recent dead. The cause of recent mortality was identified if possible. The condition of each colony including disease (not attributed to recent tissue loss) and bleaching was noted along with the extent (percent of colony affected) and level of severity (range from moderate to acute). The lowest taxonomic level of coral identification was genus except for a select number of species consistently identified to species by all divers conducting the surveys.  The number of species may change for each survey year depending on the experience and training of the benthic divers conducting the surveys. The list of coral species is included for each survey year.

Within the same four segments per transect as the adult coral surveys, crustose coralline algae (CCA) diseases and Alcyonarian disease are surveyed. In each segment, each occurrence of a specific disease is identified and the lesion is measured (maximum diameter). In addition to the adult coral surveys, CCA diseases, and Alcyonarian disease, the presence of other Anthozoans (other cnidarians including Alcyonareans, Zoantharians, coralliomorphs and Antipatharians) are also noted. These data exist as individual records coded for each group. This portion of the survey was not conducted after 2018.

Juvenile coral colonies (&lt;5 cm) were surveyed within three (1.0 x 1.0 m) segments along the same two transects in 2015 or along the single transect in 2018: 0-1.0 m (segment 1); 5.0-6.0 m (segment 3); and 10.0-11.0 m (segment 5). Juvenile colonies were distinguished in the field by a distinct tissue and skeletal boundary (not a fragment of a larger colony). Each juvenile colony was identified to lowest taxonomic level (genus or species) and measured for size by recording both the maximum and perpendicular diameter to the nearest 2 mm.</gco:CharacterString>
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                <gco:CharacterString>Raw data include individual colony records with the corresponding physical data which reflect the description of the site. An individual colony record for adult corals includes colony species/genus identification, morphology, maximum diameter (cm), percent old dead, percent recent dead, cause of recent dead general category, cause of recent dead specific category, condition, extent and severity. 

Juvenile coral colony records include colony species/genus identification, morphology, maximum diameter (cm) and perpendicular diameter (cm). 

For species level identification of adult and juvenile corals, check the species list for each year to ensure species identification across all divers conducting the surveys.

Individual records for crustose coralline algae diseases use the taxon code CALG and the Alcyonarian disease uses the taxon code for the octocoral genus.  The colony length measurement is the maximum diameter of the lesion for both disease types.

The raw presence/absence data for other Anthozoans include the general identification code and 0 or -1 to represent absence or presence respectively.

The physical data for all records includes the following: region, island, site, date (day, month, year), latitude (dd), longitude (dd), transect, segment, segment length, segment width, minimum depth (ft), and maximum depth.</gco:CharacterString>
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                    <gco:CharacterString>Ecosystem Sciences Division Standard Operating Procedures: Data Collection for Rapid Ecological Assessment Benthic Surveys, 2019 Update</gco:CharacterString>
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                        <gco:Date>2020-02-01</gco:Date>
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                                <gco:CharacterString>Winston W, Couch C, Huntington B, Vargas-Angel B. 2020. Ecosystem Sciences Division standard operating procedures: data collection for rapid ecological assessment benthic surveys, 2019 update. NOAA Tech. Memo. NMFS-PIFSC-96, 56 p.</gco:CharacterString>
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                    <gco:CharacterString>Swanson D, Bailey H, Schumacher B, Ferguson M, Vargas-Angel B. 2018. Ecosystem Sciences Division standard operating procedures: data collection for rapid ecological assessment benthic surveys. U.S. Dept. of Commerce, NOAA Technical Memorandum NOAA-TM-NMFS-PIFSC-71, 63 p. doi:10.25923/39jh-8993.</gco:CharacterString>
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