Key Laboratory of Wetland Ecology and Environment, Northeast Institute of Geography and Agroecology, Chinese Academy of Sciences, Changchun 130102, China; The Three Gorges Institute of Ecological Environment, Chongqing Institute of Green and Intelligent Technology, Chinese Academy of Sciences, Chongqing 400714, China.
Key Laboratory of Wetland Ecology and Environment, Northeast Institute of Geography and Agroecology, Chinese Academy of Sciences, Changchun 130102, China.
Sci Total Environ. 2017 Dec 15;605-606:332-336. doi: 10.1016/j.scitotenv.2017.06.200. Epub 2017 Jun 29.
Phosphorus (P) enrichment is expected to strongly influence dissolved organic carbon (DOC) biodegradation. However, the relationship between P availability and DOC biodegradation is largely unknown in nitrogen (N)-limited ecosystems. Here, we investigated the changes in the ratio of DOC to dissolved total nitrogen (DTN), specific UV absorbance at 254nm (SUVA), and DOC biodegradation in surface water and soil pore water (0-15cm depth) following eight years of multi-level P addition (0, 1.2, 4.8, and 9.6gPmyear) in an N-limited freshwater marsh in Northeast China. We found that P addition caused an increase in DOC biodegradation in surface water and soil pore water, irrespective of the P addition levels. Compared with the control treatment, the P addition rates of 1.2, 4.8, and 9.6gPmyear increased DOC biodegradation by 20.7%, 15.2%, and 14.5% in surface waters, and 11.3%, 9.4%, and 12.0% in soil pore waters, respectively. The DOC biodegradation was separately negatively correlated with the DOC:DTN ratio and SUVA, indicating that the positive effect of P addition on DOC biodegradation was caused by the elevated N concentration and the reduced DOC aromaticity. Our findings suggest that P enrichment enhances the biodegradability of DOC through increased N availability and altered DOC chemical composition, which would accelerate DOC loss from the waters and alter ecosystem C balance in N-limited temperate wetlands.
磷(P)富集预计会强烈影响溶解有机碳(DOC)的生物降解。然而,在氮(N)限制的生态系统中,P 的可利用性与 DOC 生物降解之间的关系在很大程度上尚不清楚。在这里,我们研究了在 8 年的多水平磷添加(0、1.2、4.8 和 9.6gPmyear)后,中国东北一个氮限制淡水沼泽的地表水和土壤孔隙水(0-15cm 深度)中 DOC 与溶解总氮(DTN)的比值、254nm 处的特定紫外吸光度(SUVA)和 DOC 生物降解的变化。我们发现,无论 P 添加水平如何,P 添加都会导致地表水和土壤孔隙水中的 DOC 生物降解增加。与对照处理相比,P 添加率为 1.2、4.8 和 9.6gPmyear 时,地表水 DOC 生物降解分别增加了 20.7%、15.2%和 14.5%,土壤孔隙水 DOC 生物降解分别增加了 11.3%、9.4%和 12.0%。DOC 生物降解分别与 DOC:DTN 比和 SUVA 呈负相关,这表明 P 添加对 DOC 生物降解的积极影响是由 N 浓度升高和 DOC 芳香度降低引起的。我们的研究结果表明,磷富集通过增加 N 的可利用性和改变 DOC 的化学组成来增强 DOC 的生物降解性,这将加速水中 DOC 的损失,并改变 N 限制温带湿地生态系统的 C 平衡。