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首页> 外文期刊>Biology and Fertility of Soils >Short-term nitrogen transformation rates in riparian wetland soil determined with nitrogen-15
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Short-term nitrogen transformation rates in riparian wetland soil determined with nitrogen-15

机译:氮15测定的河岸湿地土壤短期氮转化率

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N transformation rates in soil from a riparian wetland that receives runoff from adjacent pastoral land were investigated in a short-term (250 min), anaerobic laboratory incubation (20°C). A joint 15N tracing-isotope dilution technique was employed that used paired incubations of labelled (99 atom % 15N) NO3 –-unlabelled NH4 + and unlabelled NO3 –-labelled (99 atom % 15N) NH4 + at three N input levels (0.4, 4 and 24 μg N g–1 soil). At each N input level NO3 – and NH4 + were added in equal proportions (0.2, 2 and 12 μg N g–1 soil). Soil and gas samples were analysed after 10, 70 and 250 min, and the fate of 15N and N transformation rates were determined for each time period; 0–10 min (phase 1), 10–70 min (phase 2) and 70–250 min (phase 3). N transformation rates for all processes except gross NH4 + mineralisation were very high during phase 1. Processes favoured by aerobic conditions, NO3 – immobilisation (0–17% NO3 – removal, 0–8.2 μg N g–1 soil h–1), autotrophic nitrification (~2% NH4 + removal, 0.58–0.88 μg N g–1 soil h–1) and heterotrophic nitrification (11–35 μg N g–1 soil h–1) increased with increased N input while the anaerobic dissimilatory NO3 – reduction to NH4 + process (1–6% NO3 – removal, 0.48–0.62 μg N g–1 soil h–1) decreased, presumably due to the oxidising effect of higher NO3 – inputs. Denitrification (8–78% NO3 – removal, 3.8–9.6 μg N g–1 soil h–1) exhibited no clear trend related to N input levels. NH4 + immobilisation (39–72% NH4 + removal, 15–19 μg N g–1 soil h–1) was higher than NO3 – immobilisation. Gross NH4 + mineralisation (0.27–0.80 μg N g–1 soil h–1) was the only process not detected in phase 1 and one of few processes measurable in phases 2 or 3.
机译:在短期(250分钟),厌氧实验室培养(20°C)中,研究了从邻近牧区获得径流的河岸湿地中土壤的氮转化率。采用联合的15 N示踪同位素稀释技术,该方法使用标记的(99原子%15 N)NO3 -未标记的NH4 +的配对孵育。 和未标记的NO3 标记的(99原子%15 N)NH4 + 处于三个N输入水平(0.4、4和24)微克N g–1 土壤)。在每个氮输入水平上,NO3 和NH4 + 均等添加(0.2、2和12μgN g-1 土壤)。在10、70和250分钟后分析土壤和气体样品,并确定每个时间段内15 N和N的转化率。 0–10分钟(阶段1),10–70分钟(阶段2)和70–250分钟(阶段3)。在阶段1中,除总NH4 + 矿化作用外,所有过程的N转化率都非常高。在有氧条件下,固定NO3 (0–17%NO3 < / sub> – 去除,0–8.2μgN g–1 土壤h–1 ),自养硝化(〜2%NH4 + 去除,氮增加,0.58–0.88μgN g–1 土壤h-1 )和异养硝化作用(11–35μgN g–1 土壤h-1 )增加在厌氧异化NO3 还原为NH4 + 过程中输入(1–6%NO3 去除,0.48–0.62μgN g–1 土壤h–1 )减少,可能是由于较高的NO3 投入物的氧化作用所致。反硝化作用(去除8–78%NO3 ,3.8–9.6μgN g–1 土壤h–1 )没有明显的趋势与氮输入水平相关。 NH4 + 固定化(去除39–72%NH4 + ,土壤h–1 15–19μgN g–1 )高于NO3 固定化。总的NH4 + 矿化作用(0.27–0.80μgN g–1 土壤h-1 )是第一阶段未检测到的唯一过程,也是该阶段可测量的少数过程之一阶段2或3。

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