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                        <gco:CharacterString>Timor-Leste project portal on the NOAA Coral Reef Information Service website where NOAA's final report for Timor-Leste and the datasets generated by NOAA CREP as part of the project can be downloaded.</gco:CharacterString>
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            <gco:CharacterString>Pacific Islands Fisheries Science Center. 2017. Interdisciplinary baseline ecosystem assessment surveys to inform ecosystem-based management planning in Timor-Leste: Final Report. Pacific Islands Fisheries Science Center, PIFSC Special Publication, SP-17-002, 234 p. https://doi.org/10.7289/V5/SP-PIFSC-17-002.</gco:CharacterString>
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        <gco:CharacterString>The data described here includes cytochrome oxidase I (COI) DNA metabarcoding data collected from Autonomous Reef Monitoring Structures (ARMS). ARMS were deployed by the NOAA Pacific Islands Fisheries Science Center (PIFSC), Ecosystem Sciences Division (formerly the Coral Reef Ecosystem Division) in Timor Leste under USAID Timor Leste. Developed in collaboration with the Census of Marine Life (CoML) Census of Coral Reef Ecosystems (CReefs), ARMS were designed to mimic the structural complexity of a reef and attract/collect colonizing marine invertebrates. The key innovation of the ARMS method is that biodiversity is sampled over precisely the same surface area in the exact same manner.

These data were gathered at specific reef sites across Timor-Leste.  ARMS units were set-up, deployed and recovered as described in the ARMS record in the related items section below. After ARMS were disassembled, different size fractions of samples and plate scrapings were preserved in ethanol for metabarcoding.</gco:CharacterString>
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        <gco:CharacterString>The use of ARMS is a systematic, consistent, and comparable method for monitoring the marine cryptobiota community in coral reef ecosystems over time.

The Coral Reef Ecosystem Program (CREP) at NOAA Fisheries is conducting in-situ climate monitoring across the U.S. Pacific Islands Region. Climate monitoring provides a comprehensive view of climate change impacts on coral reef ecosystems and helps identify areas of resilience and vulnerability. The key indicators used to identify and monitor climate-driven trends include 1) thermal stress caused by changes in sea temperature, 2) ocean acidification resulting from changes in carbonate chemistry, and 3) ecological impacts by collecting data on coral growth rates and community structure to understand the impacts of thermal stress and ocean acidification on the ecosystem.

In 2011, NOAA and the United States Agency for International Development (USAID) Timor-Leste Mission formed a 5-year bi-lateral partnership agreement from 2012 to 2016, in support of the Government of Timor-Leste—particularly the Ministry of Agriculture and Fisheries (MAF)—by addressing significant information gaps in their nearshore marine ecosystems. Specifically, MAF asked NOAA to address the following questions:
1.Where are the nearshore marine resources?
2.What are the nearshore marine resources?
3.How are they changing over time and what threats are potentially causing these changes?
4.What approaches are needed to manage and conserve the nearshore marine resources?

With financial support from USAID and in-kind support from the NOAA Coral Reef Conservation Program (CRCP), the NOAA Coral Reef Ecosystem Program (CREP) conducted baseline ecosystem assessment surveys to inform ecosystem-based management planning in Timor-Leste. The primary activities conducted by NOAA to answer these questions included:
1.satellite mapping of nearshore habitats,
2.conducting coral reef ecosystem assessments,
3.establishing ecological baselines for climate change, and
4.building management capacity by developing a spatial data framework

The biodiversity data described herein resulted from the third activity to establish ecological baselines for climate change.</gco:CharacterString>
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            <gco:CharacterString>DNA metabarcoding has inevitable PCR amplification and sequencing biases associated with using universal primers that amplify widely divergent taxa, and the variable rates of evolution within and among phyla that affect sequence clustering with a fixed divergence thresholds. Thus, some organisms may not be represented in the DNA metabarcoding data even though they were present on the plates. See https://onlinelibrary.wiley.com/doi/10.1002/edn3.163 for more details.</gco:CharacterString>
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            <gco:CharacterString>Analytical results could be different depending on the bioinformatics used to process the raw sequencing data, however, the overall picture will most likely remain the same.</gco:CharacterString>
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          <gmd:result gco:nilReason="missing" />
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            <gco:CharacterString>Bias</gco:CharacterString>
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            <gco:CharacterString>As stated in the Analytical Accuracy section, bias in the data may result in one's choice of tools to bioinformatically process sequencing data.</gco:CharacterString>
          </gmd:evaluationMethodDescription>
          <gmd:result gco:nilReason="missing" />
        </gmd:DQ_ThematicClassificationCorrectness>
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            <gco:CharacterString>All ARMS units that are recovered are disassembled, photographed, and sorted by size. Genetic analysis of ARMS samples may exist for a subset of fractions and locations. Missing fractions/locations could be a result of: 1) ARMS that were not recovered due to logistical constraints of the mission; 2) ARMS that were not found when divers returned to the site; and 3) ARMS fractions that were unsuccessfully extracted, amplified, or sequenced.</gco:CharacterString>
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            <gco:CharacterString>ARMS sample biodiversity over precisely the same surface area in the exact same manner. Thus, the use of ARMS is a systematic, consistent, and comparable method for monitoring the cryptobiota community overtime. Three units are deployed at each site to allow for replicate measurements. Divers typically record ARMS metadata into the master Microsoft Access database within a few days of the field operations and/or ARMS processing. QA/QC procedures are typically completed during the field mission.</gco:CharacterString>
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          <gmd:result gco:nilReason="missing" />
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      <gmd:lineage>
        <gmd:LI_Lineage>
          <gmd:statement>
            <gco:CharacterString>Autonomous Reef Monitoring Structures (ARMS) are assembled, deployed, recovered, and processed as described in the ARMS record in the related items section below. The sessile organisms, the 100 um and 500 um motile fractions, as well as plate scrapings, undergo DNA metabarcoding using the COI gene as the amplicon marker.</gco:CharacterString>
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                <gco:CharacterString>ARMS Deployment -
ARMS platforms are deployed as described in detail in the ARMS record of the related items section below.</gco:CharacterString>
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                    <gco:CharacterString>Timmers, Molly A</gco:CharacterString>
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                            <gco:CharacterString>molly.timmers@noaa.gov</gco:CharacterString>
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                <gco:CharacterString>ARMS Recovery and Processing -

ARMS units are recovered, initially processed, and documented as described in the ARMS record in the related items section below.

When all of the plate layers in the ARMS unit have been photographed and set aside (in seawater), the seawater from the disassembly tub, photo tray, and rinse bucket is sieved through adjoining 2 mm and 500 um sieve pans and an attachable 100 um mesh hand net. Material collected in the 500 um sieve and 100 um net are bulk preserved into two separate jars. Jars are filled with EtOH and labeled accordingly. The preserved 500 and 100 um sample fractions undergo a decantation process at a later date prior to DNA metabarcoding. All plates from an individual ARMS unit are scrapped en masse. Once all plates have been scraped, all the scrapings are transferred into a blender (Brevill; BBL600XL). The scrapings are blended for 45-60 seconds on maximum power until the sample is homogenized. The sample is then transferred from the blender to a 40 um net. The sample in the net is rinsed with filtered (&lt; 40 um) seawater until all discharge from net is clear (takes ~2 gal). Four ~10 ml samples are preserved in 50 ml falcon tubes with DMSO and 4 ~10 ml samples are preserved in 95% EtOH. These blended preserved samples undergo DNA metabarcoding. The remaining sample is stored in a sterile whirlpak at -20C. Between the processing of each ARMS unit the blender is rinsed in fresh water to remove any remaining homogenate. The blender is then placed in a 10% bleach solution for 15 minutes. Finally all parts thoroughly rinsed with DI water if available or fresh water.</gco:CharacterString>
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                    <gco:CharacterString>Timmers, Molly A</gco:CharacterString>
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                            <gco:CharacterString>(808)725-5449</gco:CharacterString>
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                            <gco:CharacterString>molly.timmers@noaa.gov</gco:CharacterString>
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                <gco:CharacterString>Decantation of the 100 and 500 um fractions:

NOTE: All equipment used in this step that is not already sterile need to be rinsed with fresh water, placed in 10% bleach solution for 20 minutes (new every day), transferred to Milliq water for 20 minutes (bleach bucket that the milliq water will go in first, and rinse) and then place under a UV light for 20 minutes.

Wear gloves. Take sample out the freezer and let sit to defrost before decantation. Empty container(s) into a 1 L conical flask (that has been bleached, rinsed and UV sterilized). Fill the conical flask with ~300 ml of Milli-Q water. Seal neck of flask with parafilm and shake vigorously for 30 seconds. Make sure to hold the parafilm tightly in place with one hand and place the other hand on the base of the flask.

When finished, immediately carefully pour the liquid through the correct sieve (45 μm for 100- 500 μm fraction; 106 μm for 500 μm – 2 mm fraction) trying not to pour the more dense sediment into the sieve. Fill flask with another 300 ml of Milli-Q and repeat process. Do this 7 times. The aim is to remove all the less dense biological material from the flask through decantation, while keeping the more dense sediment in the flask.

Collect the material in the sieve and weigh it using a sterile spatula and falcon tube. Put exactly half of the material in a 50 ml falcon tube, fill the tube with ethanol and freeze as a back-up. Place the other half in a sterile mortar and use a pestle to crush the sample for 1 minute. Collect the sample in a 50 ml falcon tube, using a little ethanol to re-suspend it and fill the tube with 95 % ethanol. This sample is now ready for DNA extraction. Store samples at -20C until extraction.

Finally, collect the sediment left in the conical flask, using a little Milliq water and pour into the same sieve used in the previous step. Collect the material, weigh it and place in a 50ml falcon tube. Fill with ethanol and freeze at -20C.</gco:CharacterString>
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                    <gco:CharacterString>Timmers, Molly A</gco:CharacterString>
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                          <gmd:voice>
                            <gco:CharacterString>(808)725-5449</gco:CharacterString>
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              <gmd:description>
                <gco:CharacterString>For DNA extraction, amplification, and sequencing methods see- Timmers M, Vicente J, Webb M, Jury C, Toonen RJ (2020) Sponging up diversity: evaluating metabarcoding performance for a taxonomically challenging phylum within a complex cryptobenthic community. Environmental DNA. https://doi.org/10.1002/edn3.163</gco:CharacterString>
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                    <gco:CharacterString>Timmers, Molly A</gco:CharacterString>
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                            <gco:CharacterString>(808)725-5449</gco:CharacterString>
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                            <gco:CharacterString>molly.timmers@noaa.gov</gco:CharacterString>
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          <gmd:processStep>
            <gmd:LI_ProcessStep>
              <gmd:description>
                <gco:CharacterString>To obtain the sequencing data, go to XXXXXXX which takes you to the National Center for Biotechnology Information (NCBI) which hosts Genbank, a genetic sequence database collection of all publicly available DNA sequences. To download a sequence file, click on the SRA link associated with each entry. Click on the data access tab in the new link and select the highlighted name to download the sequence file.</gco:CharacterString>
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                  <gmd:individualName>
                    <gco:CharacterString>Timmers, Molly A</gco:CharacterString>
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                            <gco:CharacterString>(808)725-5449</gco:CharacterString>
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                            <gco:CharacterString>molly.timmers@noaa.gov</gco:CharacterString>
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          <gmd:processStep>
            <gmd:LI_ProcessStep>
              <gmd:description>
                <gco:CharacterString>Once sequences are downloaded, you may choose to conduct the bioinformatics in a numbers of ways based on your preference.</gco:CharacterString>
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              <gmd:processor>
                <gmd:CI_ResponsibleParty>
                  <gmd:individualName>
                    <gco:CharacterString>Timmers, Molly A</gco:CharacterString>
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