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Influence of nitrogen loading and plant nitrogen assimilation on nitrogen leaching and N2O emission in forage rice paddy fields fertilized with liquid cattle waste

机译:氮气加载和植物氮素同化对液体牛浪费施肥稻田稻田氮浸出和N2O排放的影响

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Livestock wastewater disposal onto rice paddy fields is a cost- and labor-effective way to treat wastewater and cultivate rice crops. We evaluated the influence of nitrogen loading rates on nitrogen assimilation by rice plants and on nitrogen losses (leaching and N2O emission) in forage rice fields receiving liquid cattle waste (LCW). Four forage rice fields were subjected to nitrogen loads of 107, 258, 522, and 786 kg N ha(-1) (N100, N250, N500, and N750, respectively) using basal fertilizer (chemical fertilizer) (50 kg N ha(-1)) and three LCW topdressings (each 57-284 kg N ha(-1)). Nitrogen assimilated by rice plants increased over time. However, after the third topdressing, the nitrogen content of the biomass did not increase in any treatment. Harvested aboveground biomass contained 93, 60, 33, and 31 % of applied nitrogen in N100, N250, N500, and N750, respectively. The NH4+ concentration in the pore water at a depth of 20 cm was less than 1 mg N L-1 in N100, N250, and N500 throughout the cultivation period, while the NH4+ concentration in N750 increased to 3 mg N L-1 after the third topdressing. Cumulative N2O emissions ranged from -0.042 to 2.39 kg N ha(-1); the highest value was observed in N750, followed by N500. In N750, N2O emitted during the final drainage accounted for 80 % of cumulative N2O emissions. This study suggested that 100-258 kg N ha(-1) is a recommended nitrogen loading rate for nitrogen recovery by rice plants without negative environmental impacts such as groundwater pollution and N2O emission.
机译:畜禽养殖废水处理到稻田是一个成本和劳动效益的方式来处理废水和培育水稻作物。我们通过水稻植物和氮的损失(沥滤和N2O发射)在接收液体废物牛(LCW)草料稻田评价的氮负荷率上的氮同化的影响。四对草料稻田进行的107氮负荷,258,522,786公斤氮公顷(-1)(N100,N250,N500,N750和,分别地)使用基肥(化肥)(50千克氮公顷( -1))和三个LCW topdressings(每57-284千克氮公顷(-1))。通过氮水稻植株吸收随时间增加。然而,第三次追肥后,生物质的氮含量并没有任何治疗增加。收获的地上生物量分别含有93,60,33,和在N100,N250,N500施加氮的31%,和N750。的NH 4 +浓度孔隙水中以20厘米的深度小于1毫克N- L-1在N100,N250,和N500整个培养期间,而在N750的NH4 +浓度后增加至3毫克N- L-1第三次追肥。累积氧化亚氮排放介于-0.042 2.39千克氮公顷(-1);在N750中观察到的最高值,其次是N500。在N750,N 2 O占累积氧化亚氮排放的80%的最终的排水期间发射。这项研究表明,100-258千克氮公顷(-1)是由稻植物氮回收没有负面的环境影响,如地下水污染和氧化亚氮排放一个推荐的氮负荷率。

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