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湿地土壤中溶解有机质在实验增温下的浓度动态及生物降解性。

Concentration dynamics and biodegradability of dissolved organic matter in wetland soils subjected to experimental warming.

机构信息

College of Natural Resource and Environmental Sciences, China Academy of West Region Development, ZheJiang University, Yuhangtang Avenue 688, HangZhou, ZheJiang Province, 310058, China.

water@leeds, School of Geography, University of Leeds, Leeds LS2 9JT, UK.

出版信息

Sci Total Environ. 2014 Feb 1;470-471:907-16. doi: 10.1016/j.scitotenv.2013.10.049. Epub 2013 Nov 12.

DOI:10.1016/j.scitotenv.2013.10.049
PMID:24239698
Abstract

Dissolved organic matter (DOM) is the most bioavailable soil organic pool. Understanding how DOM responds to elevated temperature is important for forecasting soil carbon (C) dynamics under climate warming. Here a 4.5-year field microcosm experiment was carried out to examine temporal DOM concentration dynamics in soil pore-water from six different subtropical wetlands. Results are compared between control (ambient temperature) and warmed (+5°C) treatments. UV-visible and fluorescence spectroscopy was performed to reveal DOM structural complexity at the end of the warming incubation. Elevated temperature resulted in initially (1 to 2.5 years) high pore-water DOM concentrations in warmed samples. These effects gradually diminished over longer time periods. Of the spectral indices, specific UV absorbance at 280 nm and humification index were significantly higher, while the signal intensity ratio of the fulvic-like to humic-like fluorescence peak was lower in warmed samples, compared to the control. Fluorescence regional integration analysis further suggested that warming enhanced the contribution of humic-like substances to DOM composition for all tested wetlands. These spectral fingerprints implied a declined fraction of readily available substrates in DOM allocated to microbial utilization in response to 4.5 years of warming. As a negative feedback, decreased DOM biodegradability may have the potential to counteract initial DOM increases and alleviate C loss in water-saturated wetland soils.

摘要

溶解有机物质(DOM)是最具生物可利用性的土壤有机库。了解 DOM 对高温的响应对于预测气候变暖下土壤碳(C)动态非常重要。本研究进行了为期 4.5 年的野外微宇宙实验,以研究来自六个不同亚热带湿地土壤孔隙水中 DOM 浓度的时间动态。在实验结束时,对对照(环境温度)和升温(+5°C)处理的结果进行了比较。采用紫外可见和荧光光谱法揭示了升温孵育结束时 DOM 结构复杂性。高温导致升温样品中最初(1 至 2.5 年)高孔隙水 DOM 浓度。这些影响在较长时间内逐渐减弱。与对照相比,在升温样品中,特定紫外吸收值 280nm 和腐殖化指数显著更高,而富里酸样到腐殖酸样荧光峰的信号强度比值较低。荧光区域积分分析进一步表明,升温增强了所有测试湿地 DOM 组成中腐殖质样物质的贡献。这些光谱指纹表明,在 4.5 年的升温过程中,分配给微生物利用的 DOM 中易于利用的底物比例下降。作为负反馈,DOM 生物降解性的降低可能有潜力抵消初始 DOM 的增加,并减轻水饱和湿地土壤中 C 的损失。

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