Curtis Amanda N, Larson Eric R
Program in Ecology, Evolution, and Conservation Biology, University of Illinois at Urbana-Champaign, Urbana, IL, United States of America.
Department of Natural Resources and Environmental Sciences, University of Illinois at Urbana-Champaign, Urbana, IL, United States of America.
PeerJ. 2020 Jun 11;8:e9333. doi: 10.7717/peerj.9333. eCollection 2020.
Environmental DNA (eDNA) is an emerging tool for monitoring invasive and imperiled species, particularly at low densities. However, the factors that control eDNA production, transport, and persistence in aquatic systems remain poorly understood. For example, the extent to which carcasses produce detectable eDNA is unknown. If positive detections are associated with dead organisms, this could confound monitoring for imperiled or invasive species. Here, we present results from one of the first studies to examine carcass eDNA in situ by deploying carcasses of the invasive red swamp crayfish () in a stream enclosure experiment for 28 days. We predicted that carcasses would initially produce eDNA that would decline over time as carcasses decayed. Unsurprisingly, crayfish carcasses lost biomass over time, but at the conclusion of our experiment much of the carapace and chelae remained. However, no eDNA of was detected in any of our samples at the crayfish density (15 carcasses at ∼615 g of biomass initially), stream flow (520-20,319 L/s), or temperature (∼14-25 °C) at our site. Subsequent analyses demonstrated that these results were not the consequence of PCR inhibition in our field samples, poor performance of the eDNA assay for intraspecific genetic diversity within , or due to the preservation and extraction procedure used Therefore, our results suggest that when crayfish are relatively rare, such as in cases of new invasive populations or endangered species, carcasses may not produce detectable eDNA. In such scenarios, positive detections from field studies may be more confidently attributed to the presence of live organisms. We recommend that future studies should explore how biomass, flow, and differences in system (lentic vs. lotic) influence the ability to detect eDNA from carcasses.
环境DNA(eDNA)是一种新兴的工具,用于监测入侵物种和濒危物种,特别是在低密度情况下。然而,控制eDNA在水生系统中的产生、运输和持久性的因素仍知之甚少。例如,尸体产生可检测到的eDNA的程度尚不清楚。如果阳性检测结果与死亡生物相关,这可能会混淆对濒危或入侵物种的监测。在此,我们展示了首批研究之一的结果,该研究通过在溪流围隔实验中部署入侵性红沼泽螯虾(Procambarus clarkii)的尸体28天,对尸体eDNA进行原位检测。我们预测,尸体最初会产生eDNA,随着尸体腐烂,eDNA会随时间下降。不出所料,螯虾尸体的生物量随时间减少,但在我们的实验结束时,大部分甲壳和螯仍保留着。然而,在我们的研究地点,以螯虾密度(最初约615克生物量的15具尸体)、水流(520 - 20319升/秒)或温度(约14 - 25°C),我们在任何样本中均未检测到克氏原螯虾的eDNA。后续分析表明,这些结果不是我们现场样本中PCR抑制、克氏原螯虾种内遗传多样性的eDNA检测方法性能不佳或所用保存和提取程序的结果。因此,我们的结果表明,当螯虾相对稀少时,例如在新入侵种群或濒危物种的情况下,尸体可能不会产生可检测到的eDNA。在这种情况下,实地研究中的阳性检测结果可能更可靠地归因于活体生物的存在。我们建议未来的研究应探索生物量、水流以及系统差异(静水与流水)如何影响从尸体中检测eDNA的能力。