Optimization and application of bacterial environmental DNA and RNA isolation for qualitative and quantitative studies

Author:

Browne Daniel J.1ORCID,Miller Catherine M.2,O'Hara Emily P.3,Courtney Robert3,Seymour Jamie3,Doolan Denise L.145,Orr Ryan67

Affiliation:

1. Centre for Molecular Therapeutics, Australian Institute of Tropical Health & Medicine James Cook University Cairns Queensland Australia

2. College of Medicine and Dentistry James Cook University Cairns Queensland Australia

3. Tropical Australian Stinger Research Unit, Australian Institute of Tropical Health & Medicine James Cook University Cairns Queensland Australia

4. Centre for Tropical Bioinformatics and Molecular Biology, Australian Institute of Tropical Health & Medicine James Cook University Cairns Queensland Australia

5. Institute for Molecular Bioscience The University of Queensland St Lucia Queensland Australia

6. College of Science and Engineering James Cook University Cairns Queensland Australia

7. Queensland Department of Agriculture and Fisheries Mareeba Queensland Australia

Abstract

AbstractMolecular detection of environmental DNA (eDNA) and RNA (eRNA) allows highly sensitive qualitative (i.e., presence or absence) and quantitative (i.e., abundance) monitoring of aquatic bacteria. However, bacterial molecular diagnostics are limited by low positive predictive values. Protocols for bacterial eDNA and eRNA molecular monitoring have primarily focused on optimizing specimen collection, and the optimal method to purify bacterial nucleic material from postcollection aquatic specimens to maximize the analytical sensitivity of molecular diagnostics remains poorly defined. Accordingly, strategies to isolate bacterial eDNA and eRNA from fresh and saltwater were investigated. We evaluated two filtration and four nucleic acid purification systems as representative of current generation bacterial eDNA and eRNA isolation strategies for capacity to isolate bacterial eDNA and eRNA from prelysed (i.e., free‐nucleic acids) and viable (i.e., colony forming units, CFU) bacterial cells. We also compared the sensitivities of reverse transcription quantitative PCR (RT‐qPCR) and metagenomic shotgun microbiome sequencing. The optimal protocol used 0.7 μm borosilicate glass filters (Whatman plc) followed by extraction with the RNeasy PowerWater kit (Qiagen). The protocol had a very high analytical sensitivity (10−3–100 ng and 102–101 CFU detected in 500 mL) across multiple species of bacteria, when tested with either RTqPCR or metagenomic sequencing. Importantly, this study highlighted several limitations which are restrictive to both qualitative and quantitative bacterial eDNA and eRNA studies. First, a 12‐h time course between sampling and extraction revealed significant species‐specific changes in cell number and free‐nucleic acid concentrations can occur postspecimen collection. Second, we found Gram‐positive bacteria yielded less nucleic material compared to Gram‐negative bacteria suggesting bacterial eDNA and eRNA studies could be biased by microorganism genome stability and extraction efficiency. This study highlights the need to define the species‐specific diagnostic sensitivity of a protocol when monitoring aquatic bacterial eDNA and eRNA with molecular diagnostics.

Publisher

Wiley

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