Abstract

Effective management of both endangered native and invasive alien crayfishes requires knowledge about distribution, monitoring of existing and early detection of newly established populations. Complementary to traditional survey methods, eDNA sampling has recently emerged as a highly sensitive non-invasive detection method to monitor crayfish populations. To advance the use of eDNA as detection tool for crayfish we used a twofold approach: 1) we designed a novel set of specific eDNA-assays for all native (Austropotamobius torrentium, Austropotamobius pallipes, Astacus astacus) and the most relevant invasive crayfish species (Pacifastacus leniusculus, Faxonius limosus, Faxonius immunis) in Central Europe. To ensure specificity each primer pair was tested in silico, in vitro, and in situ; 2) we assessed the influence of spatio-temporal variables (distance to upstream population, season, stream size) on eDNA detection in seven streams using two different detection methods (qualitative endpoint PCR and quantitative droplet digital PCR, ddPCR). The newly developed eDNA assays successfully detected all crayfish species across different lotic and lentic habitats. eDNA detection rate (endpoint PCR) and eDNA-concentration (ddPCR) were significantly influenced by distance and season. eDNA detection was successful up to 7 km downstream of the source population and across all seasons, although detectability was lowest in winter. eDNA detection rate further decreased with increasing stream size. Finally, eDNA-concentration correlated positively with estimated upstream population size. Overall, we provide near operational eDNA assays for six crayfish species, enabling year-round detection, which represents a clear benefit over conventional methods. Due to its high sensitivity, eDNA detection is also suitable for the targeted search of as-yet unrecorded or newly emerging populations. Using quantitative ddPCR might further allow for a rough estimation of population size, provided that the identified spatio-temporal factors are accounted for. We therefore recommend implementing eDNA-detection as a complementary survey tool, particularly for a large-scale screening of data-deficient catchments or a year-round monitoring.

Highlights

  • Freshwater crayfish (Crustacea, Decapoda, Astacidae) are among the most threatened animal taxa in Central European fresh waters (Souty-Grosset et al, 2006; Chucholl and Schrimpf, 2016)

  • To advance environmental DNA (eDNA) as detection tool for Central European crayfish we used a twofold approach: 1) we designed a novel set of specific endpoint eDNA-assays for all native (Austropotamobius torrentium, Austropotamobius pallipes, Astacus astacus) and the most relevant invasive crayfish species (Pacifastacus leniusculus, Faxonius limosus, Faxonius immunis) using a consistent multiple step approach, including an in silico, in vitro and in situ evaluation; 2) we assessed the influence of spatio-temporal variables on eDNA detection

  • Our approach is largely consistent to the recently proposed validation scale for targeted eDNA assays (Thalinger et al, 2020). According to this scale there are five levels ranging from “incomplete” to “operational.” Within this scale our assays can be classified from level 4 “substantial” to level 5 “operational.” Except for establishing a limit of detection (LOD), which is not possible when using endpoint PCR, our assays met all criteria propagated by the validation scale (Thalinger et al, 2020)

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Summary

Introduction

Freshwater crayfish (Crustacea, Decapoda, Astacidae) are among the most threatened animal taxa in Central European fresh waters (Souty-Grosset et al, 2006; Chucholl and Schrimpf, 2016). In addition to displacement by NICS and crayfish plague, ICS suffer from pollution and degradation of habitats, and the increasing frequency of summer droughts due to climate change (Chucholl and Schrimpf, 2016). Effective management of both ICS and NICS requires knowledge about distribution, early detection of newly emerging and monitoring of existing populations (Chucholl and Dehus, 2011; Kouba et al, 2014; Agersnap et al, 2017). Conventional methods are mostly successful during summer when animals are active, and are normally associated with a disturbance of the habitat (Peay, 2004; Olarte et al, 2019)

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