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Land-use change effects on soil C and N transformations in soils of high N status: comparisons under indigenous forest, pasture and pine plantation

机译:土地利用变化对高氮土壤中碳氮转化的影响:土著森林,牧场和松树人工林的比较

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Globally, land-use change is occurring rapidly, and impacts on biogeochemical cycling may be influenced by previous land uses. We examined differences in soil C and N cycling during long-term laboratory incubations for the following land-use sequence: indigenous forest ( soil age = 1800 yr); 70-year- old pasture planted after forest clearance; 22-year-old pine ( Pinus radiata) planted into pasture. No N fertilizer had been applied but the pasture contained N-fixing legumes. The sites were adjacent and received 3 - 6 kg ha(-1) yr(-1) " volcanic" N in rain; NO3--N leaching losses to streamwater were 5 - 21 kg ha(-1) yr(-1), and followed the order forest < pasture = pine. Soil C concentration in 0 - 10 cm mineral soil followed the order: pasture > pine = forest, and total N: pasture > pine > forest. Nitrogen mineralization followed the order: pasture > pine > forest for mineral soil, and was weakly related to C mineralization. Based on radiocarbon data, the indigenous forest 0 - 10 cm soil contained more pre-bomb C than the other soils, partly as a result of microbial processing of recent C in the surface litter layer. Heterotrophic activity appeared to be somewhat N limited in the indigenous forest soil, and gross nitrification was delayed. In contrast, the pasture soil was rich in labile N arising from N fixation by clover, and net nitrification occurred readily. Gross N cycling rates in the pine mineral soil ( per unit N) were similar to those under pasture, reflecting the legacy of N inputs by the previous pasture. Change in land use from indigenous forest to pasture and pine resulted in increased gross nitrification, net nitrification and thence leaching of NO3--N.
机译:在全球范围内,土地利用变化正在迅速发生,并且对生物地球化学循环的影响可能会受到先前土地利用的影响。我们研究了长期实验室孵化过程中土壤C和N循环在以下土地利用序列方面的差异:土著森林(土壤年龄= 1800年);森林砍伐后种植了70年历史的牧场;在牧场上种植了22岁的松树(Pinus radiata)。没有施氮肥,但牧场中含有固氮豆类。这些站点是相邻的,并在雨中收到3-6 kg ha(-1)yr(-1)“火山” N; NO3--N向河水的淋失损失为5-21 kg ha(-1)yr(-1),其顺序为森林<牧场=松树。 0-10 cm矿质土壤中的土壤C浓度遵循以下顺序:牧场>松树=森林,总氮:牧场>松树>森林。氮矿化的顺序为:牧场>松树>森林为矿质土壤,与碳矿化关系不大。根据放射性碳的数据,局部森林0-10厘米土壤中的炸弹前碳含量高于其他土壤,部分原因是微生物在表层垃圾中进行了最新的碳处理。异养活动在本地森林土壤中似乎受到氮的限制,总硝化作用被延迟。相反,由于三叶草对氮的固定作用,牧草土壤富含不稳定的氮,并且容易发生净硝化作用。松树矿质土壤中的总氮循环速率(每单位氮)与牧场条件下的相似,这反映了先前牧场对氮输入的影响。从土著森林到牧场和松树的土地利用变化导致总硝化,净硝化增加,并因此使NO3--N淋失。

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