Data from: Influence of natural and novel organic carbon sources on denitrification in forest, degraded urban, and restored streams

Organic carbon is important in regulating ecosystem function, and its source and abundance may be altered by urbanization. We investigated shifts in organic carbon quantity and quality associated with urbanization and ecosystem restoration, and its potential effects on denitrification at the riparian–stream interface. Field measurements of streamwater chemistry, organic carbon characterization, and laboratory-based denitrification experiments were completed at two forested, two restored, and two unrestored urban streams at the Baltimore Long-Term Ecological Research site, Maryland, USA. Dissolved organic carbon (DOC) and nitrate loads increased with runoff according to a power-law function that varied across sites. Stable isotopes and molar C:N ratios suggested that stream particulate organic matter (POM) was a mixture of periphyton, leaves, and grass that varied across site types. Stable-isotope signatures and lipid biomarker analyses of sediments showed that terrestrial organic carbon sources in streams varied as a result of riparian vegetation. Laboratory experiments indicated that organic carbon amendments significantly increased rates of denitrification (35.1 ± 9.4 ng N·[g dry sediment]−1·h−1; mean ± SE) more than nitrate amendments (10.4 ± 4.0 ng N·[g dry sediment]−1·h−1) across streamflow conditions and sites. Denitrification experiments with naturally occurring carbon sources showed that denitrification was significantly higher with grass clippings from home lawns (1244 ± 331 ng N·g dry sediment−1·h−1), and overall unrestored urban sites showed significantly higher denitrification rates than restored and forest sites. We found that urbanization influences organic carbon sources and quality in streams, which can have substantial downstream impacts on ecosystem services such as denitrification.有机碳对于调控生态系统功能至关重要，其来源与丰度可能因城市化进程发生改变。本研究探究了与城市化及生态系统修复相关的有机碳数量与质量变化，及其在河岸-溪流界面对反硝化作用的潜在影响。研究在美国马里兰州巴尔的摩长期生态研究站点开展，选取了2条森林溪流、2条修复型城市溪流与2条未修复型城市溪流，完成了溪流水体化学、有机碳特征表征以及实验室反硝化实验的野外采样与测定。溶解性有机碳（Dissolved Organic Carbon, DOC）与硝酸盐负荷随径流呈幂函数增长，且该函数关系因采样位点而异。稳定同位素与摩尔碳氮比分析表明，溪流颗粒有机物质（Particulate Organic Matter, POM）由周丛生物、叶片与草本植物混合组成，其组成比例因位点类型不同存在差异。沉积物的稳定同位素特征与脂质生物标志物分析显示，溪流中的陆生有机碳来源因河岸植被的不同而存在差异。实验室实验结果表明，在所有径流条件与采样位点中，有机碳添加物对反硝化速率的提升效果（35.1 ± 9.4 ng N·[g干沉积物]⁻¹·h⁻¹，平均值±标准误）显著优于硝酸盐添加物（10.4 ± 4.0 ng N·[g干沉积物]⁻¹·h⁻¹）。以天然有机碳源开展的反硝化实验显示，使用家庭草坪剪下的草屑作为碳源时，反硝化速率显著更高（1244 ± 331 ng N·g干沉积物⁻¹·h⁻¹）；整体而言，未修复型城市溪流的反硝化速率显著高于修复型溪流与森林溪流。本研究发现，城市化会改变溪流中有机碳的来源与质量，进而对反硝化等生态系统服务产生显著的下游连锁影响。