Tsuji Satsuki, Ushio Masayuki, Sakurai Sho, Minamoto Toshifumi, Yamanaka Hiroki
Graduate School of Science and Technology, Ryukoku University, 1-5 Yokotani, Seta Oe-cho, Otsu, Japan.
Joint Research Center for Science and Technology, Ryukoku University, Otsu, Japan.
PLoS One. 2017 Apr 27;12(4):e0176608. doi: 10.1371/journal.pone.0176608. eCollection 2017.
Environmental DNA (eDNA) is DNA shed by organisms into surrounding environments such as soil and water. The new methods using eDNA as a marker for species detection are being rapidly developed. Here we explore basic knowledge regarding the dependence of the eDNA degradation rate on time and water temperature, and the relationship between eDNA degradation and bacterial abundance. This subject has not been well clarified, even though it is essential for improving the reliability of eDNA analysis. To determine the time- and water temperature-dependent degradation of eDNA, river water was sampled and eDNA concentrations were determined for ayu sweetfish (Plecoglossus altivelis altivelis) and common carp (Cyprinus carpio) at seven time points, over a 48-h period, and at three different water temperatures. The degradation of eDNA was modeled for each species using an existing exponential decay model with an extension to include water temperature effects. The degradation models were constructed for ayu sweetfish as Nt = 229,901.2 × exp [- (0.01062 × k - 0.07081) × t] and for common carp as Nt = 2,558.0 × exp [- (0.01075 × k - 0.07372) × t]. Nt is the DNA concentration at time t (elapsed time in hours) and k is the water temperature (°C). We also measured the concentration of eDNA derived from purified genomic DNA of the common carp, which was spiked into aquarium water without the target species, and we measured the bacterial abundance in the sample water after 12 and 24 h of incubation. Environmental DNA degradation was accelerated at higher water temperatures (generalized linear model, GLM; p < 0.001), but bacterial abundance did not have a significant effect on eDNA degradation (GLM, p = 0.097). These results suggest that the proper treatment of this temperature effect in data interpretations and adjustments would increase the reliability of eDNA analysis in future studies.
环境DNA(eDNA)是生物体释放到周围环境(如土壤和水)中的DNA。利用eDNA作为物种检测标记的新方法正在迅速发展。在此,我们探讨了关于eDNA降解速率对时间和水温的依赖性,以及eDNA降解与细菌丰度之间关系的基础知识。尽管这对于提高eDNA分析的可靠性至关重要,但该主题尚未得到充分阐明。为了确定eDNA随时间和水温的降解情况,采集了河水样本,并在48小时内的七个时间点以及三种不同水温下,测定了香鱼(Plecoglossus altivelis altivelis)和鲤鱼(Cyprinus carpio)的eDNA浓度。使用现有的指数衰减模型并扩展以纳入水温影响,为每个物种建立了eDNA降解模型。香鱼的降解模型为Nt = 229,901.2 × exp [- (0.01062 × k - 0.07081) × t],鲤鱼的降解模型为Nt = 2,558.0 × exp [- (0.01075 × k - 0.07372) × t]。Nt是时间t(以小时为单位的 elapsed time)时的DNA浓度,k是水温(°C)。我们还测量了添加到没有目标物种的水族箱水中的鲤鱼纯化基因组DNA衍生的eDNA浓度,并在孵育12小时和24小时后测量了样本水中的细菌丰度。在较高水温下,环境DNA降解加速(广义线性模型,GLM;p < 0.001),但细菌丰度对eDNA降解没有显著影响(GLM,p = 0.097)。这些结果表明,在数据解释和调整中对这种温度效应进行适当处理将提高未来研究中eDNA分析的可靠性。