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Environmental DNA (eDNA) in aquatic environments refers to genetic material found in the water column. Recent studies demonstrated the utility of eDNA for detecting fishes from various aquatic environments, including ponds1-3, rivers4-8, streams9, and seawater10-14. Most of these studies focused on detection of a single or a few invasive1,4-6,8,14 and rare or threatened species3,9, while some recent studies attempted simultaneous detection of multiple species in local fish communities7,9,12,13,15 and mesocosms11,12.
The latter approach is called "metabarcoding" and eDNA metabarcoding uses one or multiple sets of PCR primers to coamplify a gene region across taxonomically diverse samples. This is followed by library preparation with indexing and adapter addition, and the indexed libraries are analyzed by a high-throughput parallel sequencing platform. Recently Miya et al.12 developed universal PCR primers for metabarcoding eDNA from fishes (called "MiFish"). The MiFish primers target a hypervariable region of the mitochondrial 12S rRNA gene (163-185 bp), which contains sufficient information to identify fishes to taxonomic family, genus and species except for some closely related congeners. With the use of those primers in eDNA metabarcoding, Miya et al.12 detected more than 230 subtropical marine species from aquarium tanks with known species composition and coral reefs near the aquarium.
While optimizing the metabarcoding protocol to accommodate natural seawater with varying levels of eDNA concentration from fishes, we have noticed that the MiFish primers occasionally failed to amplify the target region for subsequent library preparation. One of the more likely reasons for this unsuccessful PCR amplification is lack of adequate amounts of the template DNA contained in small volumes of water filtered (i.e. 1-2 L). Although eDNA concentration from a specific taxonomic group is unknowable before the amplification, filtration of large water volumes (>1-2 L) would be a simple and effective means to collect more eDNA from the aquatic environments with scarce fish abundance and biomass, such as open-ocean and deep-sea ecosystems.
Relative to disk fiber filters conventionally used in a number of fish eDNA research16, filter cartridges have the advantage of accommodating larger water volumes before clogging17. Actually, a recent study showed large volume (>20 L) filtration of coastal seawater samples using filter cartridges18. In addition, they are individually packaged and sterile, and several steps of the experimental workflow can be performed in the filter housing, thus reducing the probability of contamination from the laboratory19. The latter feature is critical for eDNA metabarcoding, in which the risk of contamination remains among the greatest experimental challenges20,21. Despite these technical advantages of filter cartridges, it has not been used in eDNA studies of fishes with two exceptions8,15.
Here we provide a protocol for filtration of water samples with the filter cartridge and extraction of eDNA from its filter without having to cut open the housing. We also provide two alternative water filtration systems depending on the water volumes (≤4 L or >4 L). To compare the performance of the newly-developed protocol and a previously-used protocol using a glass-fiber filter in our research group12,14,22,23, we perform eDNA metabarcoding analysis of seawater from a huge aquarium tank (7,500 m3) with known species composition, and show the number of detected species derived from the two protocols as representative results. This protocol has been developed for metabarcoding eDNA from fishes, but is also applicable to eDNA from other organisms.