Dataset: COI mtDNA sequences for trematodes from fish collections across the Northern Line Islands and French Polynesia archipelagos collected between 2009 and 2023

ValidatedFinal no updates expectedDOI: 10.26008/1912/bco-dmo.953401.1Version 1 (2025-03-03)Dataset Type:Other Field Results

Principal Investigator: Alison Haupt (California State University Monterey Bay)

Principal Investigator: Stuart Sandin (University of California-San Diego Scripps)

Principal Investigator: Chelsea L. Wood (University of Washington)

Scientist: Randi Barton (California State University Monterey Bay)

BCO-DMO Data Manager: Audrey Mickle (Woods Hole Oceanographic Institution)


Project: Collaborative Research: Decomposing the effects of diversity on the abundance of marine parasites (Diversity-disease)


Abstract

The loss of biological diversity is considered one of the principal environmental challenges of the 21st century, and there are hints that this massive reorganization of food webs could affect how parasites are transmitted among hosts. Parasites are often hidden and can be easy to overlook, but they are ecologically important and ubiquitous - so it is important to understand whether we should expect more or fewer of them as biodiversity disappears. Does biodiversity loss increase the abundance o...

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Field collections and sample processing

Coral reef fish host species Acanthurus nigricans, Stegastes aureus, and Stegastes fasciolatus were caught at islands from Northern Line Islands (NLI) and French Polynesia (FP) during expeditions in 2010, 2019, 2020, and 2021. Sampling was conducted across three archipelagos of the central equatorial Pacific, encompassing 19 islands (Jarvis, Kingman, Kiritimati, Palmyra, Tabuaeran, and Teraina in the Northern Line Islands; Flint, Malden, Millennium, Starbuck, and Vostok in the Southern Line Islands; Huahine, Moorea, Raiatea, Rangiroa, Tahiti, Takapoto, Tetiaroa, and Tikehau in French Polynesia). 

Acanthurus nigricans are a type of surgeonfish belonging to the Family AcanthuridaeStegastes aureus and Stegastes fasciolatus are damselfish of Family Pomacentridae. Reef fish were collected from the forereef of each island from depths between 8m and 18m using three-pronged spears and hand nets. Fish were euthanized humanely according to UC San Diego IACUC protocol #S09392 and frozen for parasitological assessment. 

Parasites were identified and counted by the Wood Lab at the University of Washington using standard dissection methods [see appendix E in (Wood et al. 2014)]. Parasites were identified to the lowest possible taxonomic level [see appendix F in (Wood et al. 2014)] and stored in 70% ethanol. All of the adult trematodes used in this study were sampled from host species A. nigricans, while the NLI larval samples came from S. aureus, and the FP larval samples came from S. fasciolatus.

Following morphological assessment conducted by the Wood Lab, it was determined that all of the adult trematodes sampled from the NLI were of the Family Microscaphidiidae (NLI adults), and all of the adult trematodes sampled from FP were of the Family Paramphistomatidae (FP adults). Parasite vouchers were sent to the Haupt Lab at California State University, Monterey Bay for further genetic analysis in 2022 (Barton, 2024).

DNA Extraction, PCR, and Sequencing

In most cases, DNA was extracted from all collected parasites. However, when more than 30 parasites were obtained from a single island, sequencing was generally limited to the first 30 individuals encountered in the vials. In some cases, additional samples were included before this threshold was recognized.

As detailed in Barton (2024): Each voucher was emptied into a petri dish containing 70% ethanol, one at a time. The petri dish was then examined under a dissecting microscope at the lowest magnification. A disposable glass pipette was used to move the parasite to a microcentrifuge tube containing autoclaved DI water in order to rinse the parasite of residual fish tissue. Individuals were not soaked for any longer than two hours as this could lead to degradation of the specimen. After 30 minutes to an hour, the parasite was then transferred into another microcentrifuge tube containing tissue lysis buffer and proteinase K and incubated at 56℃ for at least one hour. Larger individuals were incubated for 2 or more hours. Extractions were then conducted using either the QIAGEN QIAamp DNA Micro Kit (Cat. #51304) or the QIAGEN DNeasy Blood & Tissue Kit (Cat. #69504). The DNeasy kit was used for those parasite individuals that were larger and had more tissue present. DNA yield was estimated after extraction using a Nanodrop spectrophotometer. Due to the small amount of tissue present, DNA yields were often very small. Therefore, there were no restrictions on which samples moved forward to polymerase chain reaction (PCR). 

A 743 bp segment of the mtDNA cytochrome oxidase 1 gene (CO1) was amplified using three primers designed by Brant and Loker (2009) for trematodes. PCR was performed in two consecutive 50 µL reactions. The first reaction was conducted using the DNA extraction and the forward and reverse primers. The PCR product of the first run was then used in the second reaction with the forward and internal primers. Both reactions were run on thermocyclers with the following reaction conditions: Initial denaturation at 94°C for 2 min, followed by 35 cycles of 94°C for 30 s, 55°C for 40 s, 72°C for 1 min, with a final step of 72°C for 10 min. Final PCR products were run on a 1.5% agarose gel using SYBR™ Safe DNA Gel Stain (Cat. #S33102) and the GeneRuler 1 kb DNA Ladder (Cat. #SM0314). The gels were run at 120 V for 30-45 minutes. However, we discovered that even if a band could not be seen, the sample was often still able to be sequenced. Therefore, we decided to send all amplified DNA samples off for sequencing. Amplified DNA was purified using the QIAGEN QIAquick PCR Purification Kit (Cat. #28104). Samples were sent for Sanger sequencing (MCLAB, San Francisco, CA) and were sequenced in the forward and internal directions.


Related Datasets

References

Dataset: Parasite abundance in coral reef fishes
Relationship Description: Dataset is created based on samples collected in this related dataset. See methods for more information on sample provenance.
Wood, C. L., Sandin, S., Haupt, A. (2025) Parasite abundance data collected from coral reef fishes across 19 islands in the central equatorial Pacific from 2009 to 2021. Biological and Chemical Oceanography Data Management Office (BCO-DMO). (Version 1) Version Date 2025-01-22 doi:10.26008/1912/bco-dmo.945218.1

Related Publications

Results

Barton, Randi Leigh, "Population genetic analysis informs dispersal capacity in representative marine trematodes from Family Microscaphidiidae and Family Paramphistomatidae" (2024). Capstone Projects and Master's Theses. 1846. https://digitalcommons.csumb.edu/caps_thes_all/1846
Results

Wood, C. L., Zgliczynski, B. J., Haupt, A. J., Guerra, A. S., Micheli, F., & Sandin, S. A. (2018). Human impacts decouple a fundamental ecological relationship—The positive association between host diversity and parasite diversity. Global Change Biology, 24(8), 3666–3679. Portico. https://doi.org/10.1111/gcb.14159
Methods

Brant, S. V., & Loker, E. S. (2009). Molecular Systematics of the Avian Schistosome Genus Trichobilharzia (Trematoda: Schistosomatidae) in North America. Journal of Parasitology, 95(4), 941–963. https://doi.org/10.1645/GE-1870.1
Methods

Wood, C. L., Sandin, S. A., Zgliczynski, B., Guerra, A. S., & Micheli, F. (2014). Fishing drives declines in fish parasite diversity and has variable effects on parasite abundance. Ecology, 95(7), 1929–1946. Portico. https://doi.org/10.1890/13-1270.1