ESTABLISHMENT OF A SPECIMEN/TISSUE BANK AND ASSOCIATED DNA REFERENCE DATA FOR eDNA ANALYSIS

Luca Mirimin, Dulaney Miller, Sara Fernandez

Published: 2021-11-23 DOI: 10.17504/protocols.io.bzn2p5ge

Abstract

This protocol is intended to provide guidelines on the curation and establishment of a specimen/tissue bank and associated DNA sequence data to be used as reference material/data for subsequent environmental DNA (eDNA) analysis, with particular emphasis on marine non-indigenous and invasive species.

Before start

To minimize risk of cross-sample contamination, note that all re-usable materials (e.g. scalpels, scissors, tweezers) should be decontaminated to remove any traces of DNA. It is highly recommended to carry out these protocols in dedicated and PCR-free laboratories/rooms.

Ensure that each protocol and list of materials is checked before starting any of the procedures. Specifically, make sure that all key materials(e.g. kits) have not been modified or discontinued by the relevant supplier.

Steps

Introduction

1.

This document includes the following sections:

  • A graphical representation of the overall process

  • Collection of specimens and associated metadata

  • Specimen and tissue bank

  • Isolation of genomic DNA

  • Molecular barcoding

  • Acknowledgements

Graphical overview

2.
General workflow overview for the establishment and curation of a specimen and DNA reference database
General workflow overview for the establishment and curation of a specimen and DNA reference database

Collection of specimens and associated metadata

3.

Specimens can be collected following targeted surveys or opportunistically, using rapid methods (collection by hand, dredges, corers, traps, nets, etc.) or dedicated in situ approaches (e.g. SETL settlement plates; https://www.gimaris.com/Projects/SETL-project). When possible, whole specimens should be preserved for future downstream taxonomic identification.

As for metadata, the minimum information would include location (ideally with exact coordinates), date of collection, method of collection, photographs, and name/contact of person who collected the specimen. For an extensive list of recommended metadata, we recommend consulting guidelines provided in Rimet et al. (2021).

Citation
Rimet F, Aylagas E, Borja A, Bouchez A, Canino A, Chauvin C, Chonova T, Ciampor Jr F, Costa FO, Ferrari BJD, Gastineau R, Goulon C, Gugger M, Holzmann M, Jahn R, Kahlert M, Kusber W-H, Laplace-Treyture C, Leese F, Leliaert F, Mann DG, Marchand F, Méléder V, Pawlowski J, Rasconi S, Rivera S, Rougerie R, Schweizer M, Trobajo R, Vasselon V, Vivien R, Weigand A, Witkowski A, Zimmermann J, Ekrem T 2021 Metadata standards and practical guidelines for specimen and DNA curation when building barcode reference libraries for aquatic life Metabarcoding and Metagenomics https://doi.org/10.3897/mbmg.5.58056

Specimen and tissue bank

4.

For samples containing multiple organisms (e.g. dredge, SETL), specimens should be sorted and separated into single species groups. If the goal of the survey includes small- to micro-organisms, any small (>1mm) organism should be collected by rinsing with clear seawater (or artificial seawater) any substrate or specimen through a 1mm sieve, whereas the flow-through water should be inspected with a microscope for the presence of micro-organism.

Safety information
To avoid unintentional spreading of non-indigenous species and/or pathogens, make sure to treat any materials and liquids with appropriate disinfectants before disposal (e.g. Virkon aquatic).

A unique specimen identifier code should be allocated to each specimen collected. The format and style of such code will depend on the intended database/repository.

5.

Preservation conditions will depend on the organism and can vary substantially, however such conditions should be chosen with the purpose of (i) limit DNA degradation during storage and (ii) ensure that key taxonomic features are retained for subsequent identification. However, in the context of marine non-indigenous species, many taxa (including most invertebrates) can be preserved frozen (-20°C to -80°C), using 70-100% (for subsequent DNA analysis, but may lead to discoloration affecting taxonomic ID) and/or (for subsequent taxonomic identification, but not recommended or DNA isolation).

WARNING: caution should be exercised when handling ethanol and formalin. Please consult the relevant Safety Data Sheets for further information.

Safety information
H225 | Highly flammable liquid and vapour
H225 | Highly flammable liquid and vapour
H319 | Causes serious eye irritation
H319 | Causes serious eye irritation
H317 | May cause an allergic skin reactionH351 | Suspected of causing cancer
H317 | May cause an allergic skin reactionH351 | Suspected of causing cancer

Isolation of genomic DNA

6.

DNA isolation protocols should be adapted to each organisms following the manufacturer's recommendations. However, in the context of marine non-indigenous species, two DNA isolation kits have been used with highly successful rates, including the (particularly successful on mollusks and arthropods) and the (for most other animal species, algae and microorganisms).

Subsequent to DNA isolation, template DNA should be quantified using a Qubit Fluorometer (Invitrogen), whereas quality of extracts should be assessed using a small-volume spectrophotometer (Thermo Scientific™).

Equipment

ValueLabel
Invitrogen™ Qubit™ 3 FluorometerNAME
Accurately measures DNA, RNA, and protein using the highly sensitive fluorescence-based Qubit quantitation assaysTYPE
Invitrogen™ Q33216BRAND
Q33216SKU

Equipment

ValueLabel
NanoDrop™ One UV-Vis SpectrophotometerNAME
spectrophotometerTYPE
Thermo ScientificBRAND
ND-ONE-WSKU
Sample Volume (Metric): Minimum 1µL; Spectral Bandwidth: ≤1.8 nm (FWHM at Hg 254 nm); System Requirements: Windows™ 8.1 and 10, 64 bit; Voltage: 12 V (DC); Wavelength Range: 190–850 nmSPECIFICATIONS

Molecular barcoding

7.

Note
The choice of genetic markers to be used in molecular barcoding depends on the target organism as well as on the intended taxonomic resolution of the barcode. Here we provide a range of molecular markers and protocols that were successfully used to barcode a wide range of marine non-indigenous species.

ABCDEFGHIJKL
Assay #Target TaxaTarget GeneAmplicon Length Range (bp)Forward Primer NameForward Primer Sequence (5'-3')Forward Primer Source ReferenceReverse Primer NameReverse Primer Sequence (5'-3')Reverse Primer Source Reference
1Marine metazoansCOI658LoboF1KBTCHACAAAYCAYAARGAYATHGGLobo et al. 2013LoboR1TAAACYTCWGGRTGWCCRAARAAYCALobo et al. 2013
2Marine metazoansCOI313mICOIintF‐XTGGWACWRGWTGRACWNTNTAYCCYCCLeray et al 2013jgHCO2198aTANACYTCNGGRTGNCCRAARAAYCALeray et al 2013
3Marine metazoansCOI710jgLCO1490TITCIACIAAYCAYAARGAYATTGGGeller et al 2013jgHCO2198bTAIACYTCIGGRTGICCRAARAAYCAGeller et al 2013
4Marine metazoans16S rRNA56716sar-LCGCCTGTTTATCAAAAACATPalumbi et al 200216sbr-HCCGGTCTGAACTCAGATCACGTPalumbi et al 2002
5(Freshwater) DiatomsRuBisCO312Diat_rbcL_708FAGGTGAARYWAAAGGTTCWTAYTTAAAVasselon et al 2017Diat_rbcL_R3CCTTCTAATTTACCWACWACTGVasselon et al 2017
8.

Note
The following PCR conditions are specific to the selected markers reported above and were optimized using Platinum II Taq Hot-Start DNA Polymerase (Invitrogen)or GoTaq® DNA Polymerase (Promega). While the reported reagents and conditions were successful on a range of taxonomic groups, further optimization may be required for specimens that fail to amplify.

Assay 1 (COI - Lobo et al 2013)

Citation
Lobo, J., Costa, P.M., Teixeira, M.A., Ferreira, M.S.G., Costa, M.H., Costa, F.O. 2013 Enhanced primers for amplification of DNA barcodes from a broad range of marine metazoans BMC Ecology https://doi.org/10.1186/1472-6785-13-34

ABC
Reagent name and starting concentrationAmount per reaction (µL)Final concentration (per reaction)
Moleculr grade waterto 10 μL-
5X Platinum™ II PCR Buffer21X
10 mM dNTP mix0.20.2 mM each
10 μM forward primer0.20.2 μM
10 μM reverse primer0.20.2 μM
Platinum™ II Taq Hot-Start DNA Polymerase0.080.04 U/μL
Template DNA1-2<200 ng/rxn
Total10

PCR reagents and concentrations for Assay 1

Thermal cycling conditions:

94ºC-1min

   94ºC-30secs

   45ºC-60secs             x5

   72ºC-60secs



   94ºC-30secs

   54ºC-90secs             x45

   72ºC-60secs

4ºC-+∞

Assay 2 (COI - Leray et al 2013)

Citation
Leray M, Yang JY, Meyer CP, Mills SC, Agudelo N, Ranwez V, Boehm JT, Machida RJ 2013 A new versatile primer set targeting a short fragment of the mitochondrial COI region for metabarcoding metazoan diversity: application for characterizing coral reef fish gut contents. Frontiers in zoology https://doi.org/10.1186/1742-9994-10-34

ABCD
Reagent name and starting concentrationAmount per reaction (µL)Final concentration (per reaction)
Moleculr grade waterto 20µL-
5X GoTaq PCR Buffer41X
10 mM dNTP mix0.40.2 mM each
10 μM forward primer10.5 µM
10 μM reverse primer10.5 μM
GoTaq DNA Polymerase0.150.04 U/μL
Template DNA2<200 ng/rxn
Total20

Thermal cycling conditions:

95ºC-1min

   95ºC-15secs

   46ºC-15secs             x40

   72ºC-10secs



   72ºC-3min

4ºC-+∞

Assay 3 (COI - Geller et al 2013)

Citation
Geller J, Meyer C, Parker M, Hawk H 2013 Redesign of PCR primers for mitochondrial cytochrome c oxidase subunit I for marine invertebrates and application in all-taxa biotic surveys. Molecular ecology resources https://doi.org/10.1111/1755-0998.12138

ABCD
Reagent name and starting concentrationAmount per reaction (µL)Final concentration (per reaction)
Moleculr grade waterto 20µL-
5X GoTaq PCR Buffer41X
10 mM dNTP mix0.40.2 mM each
10 μM forward primer10.5 µM
10 μM reverse primer10.5 μM
GoTaq DNA Polymerase0.150.04 U/μL
Template DNA2<200 ng/rxn
Total20

Thermal cycling conditions:

95ºC-5min

   95ºC-1min

   48ºC-1min             x40

   72ºC-1min



   72ºC-5min

4ºC-+∞

Assay 4 (16S rRNA - Palumbi et al 2002)

Citation
Palumbi S, Martin A, Romano S, McMillan W, Stice L, Grabowski G. The Simple Fool's Guide to PCR, Version 2.0

ABCD
Reagent name and starting concentrationAmount per reaction (µL)Final concentration (per reaction)
Moleculr grade waterto 20µL-
5X GoTaq PCR Buffer41X
10 mM dNTP mix0.40.2 mM each
10 μM forward primer10.5 µM
10 μM reverse primer10.5 μM
GoTaq DNA Polymerase0.150.04 U/μL
Template DNA2<200 ng/rxn
Total20

Thermal cycling conditions:

95ºC-5min

   94ºC-1min

   55ºC-1min             x40

   72ºC-2min



   72ºC-7min

4ºC-+∞

Assay 5 (RuBisCO - Vasselon et al 2017)

Citation
Vasselon, V., Rimet, F., Tapolczai, K., & Bouchez, A. 2017 Assessing ecological status with diatoms DNA metabarcoding: Scaling-up on a WFD monitoring network (Mayotte Island, France) Ecological Indicators https://doi.org/10.1016/j.ecolind.2017.06.024

ABCD
Reagent name and starting concentrationAmount per reaction (µL)Final concentration (per reaction)
Moleculr grade waterto 20µL-
5X GoTaq PCR Buffer41X
10 mM dNTP mix0.40.2 mM each
10 μM forward primer10.5 µM
10 μM reverse primer10.5 μM
GoTaq DNA Polymerase0.150.04 U/μL
Template DNA2<200 ng/rxn
Total20

Thermal cycling conditions:

94ºC-1min

   95ºC-30secs

   46ºC-30secs             x40

   72ºC-30secs



   72ºC-10min

4ºC-+∞

9.

Successful amplification and confirmation of expected size of PCR products should be carried out by agarose gel electrophoresis .

(Optional) A PCR clean-up step can be included at this stage, but in many cases it is not necessary.

DNA sequences should be obtained by Sanger sequencing using the Forward and/or reverse primers.

Sanger Sequencing

Raw DNA sequence data should be inspected using any suitable software (e.g. MEGA, Geneious) and curated to ensure high quality (error-free) of final data.

Linking DNA sequence data to public repositories such as GenBank GenBank and BOLD BOLD is strongly encouraged.

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