Data from: Residual eDNA detection sensitivity assessed by quantitative real-time PCR in a river ecosystem

Several studies have demonstrated that environmental DNA (eDNA) can be used to detect the presence of aquatic species, days to weeks after the target species has been removed. However, most studies used eDNA analysis in lentic systems (ponds or lakes), or in controlled laboratory experiments. While...

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Main Authors: Balasingham, Katherine D., Walter, Ryan P., Heath, Daniel D.
Format: Dataset
Language:unknown
Published: 2016
Subjects:
Online Access:https://doi.org/10.5061/dryad.5rf92
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author Balasingham, Katherine D.
Walter, Ryan P.
Heath, Daniel D.
author_facet Balasingham, Katherine D.
Walter, Ryan P.
Heath, Daniel D.
author_sort Balasingham, Katherine D.
collection Unknown
description Several studies have demonstrated that environmental DNA (eDNA) can be used to detect the presence of aquatic species, days to weeks after the target species has been removed. However, most studies used eDNA analysis in lentic systems (ponds or lakes), or in controlled laboratory experiments. While eDNA degrades rapidly in all aquatic systems, it also undergoes dilution effects and physical destruction in flowing systems, complicating detection in rivers. However, some eDNA (i.e. residual eDNA) can be retained in aquatic systems, even those subject to high flow regimes. Our goal was to determine residual eDNA detection sensitivity using quantitative real-time polymerase chain reaction (qRT-PCR), in a flowing, uncontrolled river after the eDNA source was removed from the system; we repeated the experiment over two years. Residual eDNA had the strongest signal strength at the original source site and was detectable there up to 11.5 hours after eDNA source removal. Residual eDNA signal strength decreased as sampling distance downstream from the eDNA source site increased, and was no longer detectable at the source site 48 hours after the eDNA source water was exhausted in both experiments. This experiment shows that residual eDNA sampled in surface water can be mapped quantitatively using qRT-PCR, which allows a more accurate spatial identification of the target species location in lotic systems, and relative residual eDNA signal strength may allow the determination of the timing of the presence of target species. Appendix S1. Ct values for qRT-PCR efficiency for Salmo salar.Ct values for Figure 2. 10-fold Salmo salar dilution series with Salmo_Mito-951 (d-loop; Karlsson et al. 2012) primer set.Suppl Info - Appendix S1. Ct values for qRT-PCR efficiency.xlsxAppendix S2. Little River 2014 qRT-PCR Ct values.Ct values for Figure 3A. Little River 2014 river samples. Primer set Salmo_Mito-951 (Karlsson et al. 2012).Suppl Info - Appendix S2. Little River 2014 qRT-PCR Ct values.xlsxAppendix S3. Little River 2015 qRT-PCR Ct ...
format Dataset
genre Salmo salar
genre_facet Salmo salar
geographic Little River
geographic_facet Little River
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spelling fttriple:oai:gotriple.eu:50|dedup_wf_001::790bb70dcb762610e841c537b1325362 2025-01-17T00:34:13+00:00 Data from: Residual eDNA detection sensitivity assessed by quantitative real-time PCR in a river ecosystem Balasingham, Katherine D. Walter, Ryan P. Heath, Daniel D. 2016-01-01 https://doi.org/10.5061/dryad.5rf92 undefined unknown http://dx.doi.org/10.5061/dryad.5rf92 https://dx.doi.org/10.5061/dryad.5rf92 lic_creative-commons oai:services.nod.dans.knaw.nl:Products/dans:oai:easy.dans.knaw.nl:easy-dataset:94105 10.5061/dryad.5rf92 oai:easy.dans.knaw.nl:easy-dataset:94105 10|eurocrisdris::fe4903425d9040f680d8610d9079ea14 10|openaire____::9e3be59865b2c1c335d32dae2fe7b254 re3data_____::r3d100000044 10|re3data_____::84e123776089ce3c7a33db98d9cd15a8 10|re3data_____::94816e6421eeb072e7742ce6a9decc5f 10|openaire____::081b82f96300b6a6e3d282bad31cb6e2 10|opendoar____::8b6dd7db9af49e67306feb59a8bdc52c Life sciences medicine and health care Environmental DNA River qRT-PCR Residual DNA persistence envir geo Dataset https://vocabularies.coar-repositories.org/resource_types/c_ddb1/ 2016 fttriple https://doi.org/10.5061/dryad.5rf92 2023-01-22T17:22:51Z Several studies have demonstrated that environmental DNA (eDNA) can be used to detect the presence of aquatic species, days to weeks after the target species has been removed. However, most studies used eDNA analysis in lentic systems (ponds or lakes), or in controlled laboratory experiments. While eDNA degrades rapidly in all aquatic systems, it also undergoes dilution effects and physical destruction in flowing systems, complicating detection in rivers. However, some eDNA (i.e. residual eDNA) can be retained in aquatic systems, even those subject to high flow regimes. Our goal was to determine residual eDNA detection sensitivity using quantitative real-time polymerase chain reaction (qRT-PCR), in a flowing, uncontrolled river after the eDNA source was removed from the system; we repeated the experiment over two years. Residual eDNA had the strongest signal strength at the original source site and was detectable there up to 11.5 hours after eDNA source removal. Residual eDNA signal strength decreased as sampling distance downstream from the eDNA source site increased, and was no longer detectable at the source site 48 hours after the eDNA source water was exhausted in both experiments. This experiment shows that residual eDNA sampled in surface water can be mapped quantitatively using qRT-PCR, which allows a more accurate spatial identification of the target species location in lotic systems, and relative residual eDNA signal strength may allow the determination of the timing of the presence of target species. Appendix S1. Ct values for qRT-PCR efficiency for Salmo salar.Ct values for Figure 2. 10-fold Salmo salar dilution series with Salmo_Mito-951 (d-loop; Karlsson et al. 2012) primer set.Suppl Info - Appendix S1. Ct values for qRT-PCR efficiency.xlsxAppendix S2. Little River 2014 qRT-PCR Ct values.Ct values for Figure 3A. Little River 2014 river samples. Primer set Salmo_Mito-951 (Karlsson et al. 2012).Suppl Info - Appendix S2. Little River 2014 qRT-PCR Ct values.xlsxAppendix S3. Little River 2015 qRT-PCR Ct ... Dataset Salmo salar Unknown Little River ENVELOPE(-135.687,-135.687,60.894,60.894)
spellingShingle Life sciences
medicine and health care
Environmental DNA
River
qRT-PCR
Residual
DNA persistence
envir
geo
Balasingham, Katherine D.
Walter, Ryan P.
Heath, Daniel D.
Data from: Residual eDNA detection sensitivity assessed by quantitative real-time PCR in a river ecosystem
title Data from: Residual eDNA detection sensitivity assessed by quantitative real-time PCR in a river ecosystem
title_full Data from: Residual eDNA detection sensitivity assessed by quantitative real-time PCR in a river ecosystem
title_fullStr Data from: Residual eDNA detection sensitivity assessed by quantitative real-time PCR in a river ecosystem
title_full_unstemmed Data from: Residual eDNA detection sensitivity assessed by quantitative real-time PCR in a river ecosystem
title_short Data from: Residual eDNA detection sensitivity assessed by quantitative real-time PCR in a river ecosystem
title_sort data from: residual edna detection sensitivity assessed by quantitative real-time pcr in a river ecosystem
topic Life sciences
medicine and health care
Environmental DNA
River
qRT-PCR
Residual
DNA persistence
envir
geo
topic_facet Life sciences
medicine and health care
Environmental DNA
River
qRT-PCR
Residual
DNA persistence
envir
geo
url https://doi.org/10.5061/dryad.5rf92