Forest and Rangeland Ecosystem Science Center, U.S. Geological Survey, Boise, ID, 83706, USA.
Mol Ecol Resour. 2014 Jan;14(1):109-16. doi: 10.1111/1755-0998.12159. Epub 2013 Sep 6.
Environmental DNA (eDNA) methods for detecting and estimating abundance of aquatic species are emerging rapidly, but little is known about how processes such as secretion rate, environmental degradation, and time since colonization or extirpation from a given site affect eDNA measurements. Using stream-dwelling salamanders and quantitative PCR (qPCR) analysis, we conducted three experiments to assess eDNA: (i) production rate; (ii) persistence time under different temperature and light conditions; and (iii) detectability and concentration through time following experimental introduction and removal of salamanders into previously unoccupied streams. We found that 44-50 g individuals held in aquaria produced 77 ng eDNA/h for 2 h, after which production either slowed considerably or began to equilibrate with degradation. eDNA in both full-sun and shaded treatments degraded exponentially to <1% of the original concentration after 3 days. eDNA was no longer detectable in full-sun samples after 8 days, whereas eDNA was detected in 20% of shaded samples after 11 days and 100% of refrigerated control samples after 18 days. When translocated into unoccupied streams, salamanders were detectable after 6 h, but only when densities were relatively high (0.2481 individuals/m(2) ) and when samples were collected within 5 m of the animals. Concentrations of eDNA detected were very low and increased steadily from 6-24 h after introduction, reaching 0.0022 ng/L. Within 1 h of removing salamanders from the stream, eDNA was no longer detectable. These results suggest that eDNA detectability and concentration depend on production rates of individuals, environmental conditions, density of animals, and their residence time.
环境 DNA(eDNA)方法在检测和估计水生物种的丰度方面迅速发展,但对于分泌物速率、环境降解以及从特定地点定植或灭绝以来的时间等过程如何影响 eDNA 测量的问题知之甚少。我们使用溪流栖居的蝾螈和定量 PCR(qPCR)分析进行了三项实验来评估 eDNA:(i)产生率;(ii)在不同温度和光照条件下的持续时间;以及(iii)在实验引入和将蝾螈移除到以前未占据的溪流后随时间的可检测性和浓度。我们发现,在水族馆中饲养的 44-50 g 个体每小时产生 77 ng eDNA,持续 2 小时,之后产生的速度要么大大减慢,要么开始与降解平衡。在 3 天内,全阳光和遮荫处理中的 eDNA 以指数方式降解至原始浓度的<1%。在 8 天后,全阳光样本中不再检测到 eDNA,而在 11 天后 20%的遮荫样本和 18 天后的冷藏对照样本中仍能检测到 eDNA。当被转移到未占据的溪流中时,蝾螈在 6 小时后即可被检测到,但只有在密度相对较高(0.2481 个/平方米)并且在距动物 5 m 内采集样本时才能检测到。检测到的 eDNA 浓度非常低,并且在引入后 6-24 小时内稳步增加,达到 0.0022ng/L。在将蝾螈从溪流中移除 1 小时内,eDNA 就不再可检测到。这些结果表明,eDNA 的可检测性和浓度取决于个体的产生率、环境条件、动物的密度及其居留时间。