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Nitrogen balance in a paddy field planted with whole crop rice (Oryza sativa cv. Kusahonami) during two rice-growing seasons

机译:在两个水稻种植季节种植全谷类水稻(Oryza sativa cv。Kusahonami)的稻田中的氮平衡

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This paper focuses on N balance in a paddy field planted with whole crop rice (Oryza sativa cv. Kusahonami). The experiment was conducted with two treatments during two rice-growing seasons: one was fertilized with N (160 kg N ha−1; 16N plot) and the other unfertilized (0N plot); both plots were fertilized with P and K. The N input from precipitation was 15 and 12 kg N ha−1 in 2002 and 2003, respectively. The N input from irrigation water reached as much as 123 and 69 kg N ha−1 in 2002 and 2003, respectively. This was because irrigation water contained higher NO3 − concentrations ranging from 4 to 8 mg N l−1. The N uptake by rice plants was the major output: 118 and 240 kg N ha−1 in the 0N and 16N plots in 2002 and 103 and 238 kg N ha−1 in 2003, respectively. N losses by leaching were 4.8–5.3 and 6.5–7.3 kg N ha−1 in 2002 and in 2003, respectively. Laboratory experiments were carried out to estimate the amounts of N2 fixation and denitrification. Amount of N2 fixation was 43 and 0 kg N ha−1 in the 0N and 16N plots, respectively. Denitrification potential was quite high in both the plots, and 90% of the N input through irrigation water was lost through denitrification. Collectively, the total N inputs were relatively large due to irrigation water contaminated with NO3 −, but N outflow loading, expressed as leaching−(irrigation water + precipitation + fertilizer), showed large negative values, suggesting that the whole crop rice field might serve as a constructed wetland for decreasing N.
机译:本文着重于种植全谷类水稻的水稻田中的氮平衡(Oryza sativa cv。Kusahonami)。该实验在两个水稻生长季节中进行了两种处理:一种用氮肥(160 kg N ha-1 ; 16N地块)施肥,另一种不施肥(0N地块)。这两个地块均施以P和K。2002年和2003年降水的氮输入分别为15和12 kg N ha-1 。 2002年和2003年灌溉水的氮输入分别高达123和69 kg N ha-1 。这是因为灌溉水中的NO3 -浓度较高,为4至8 mg N l-1 。水稻对氮的吸收是主要的产量:2002年的0N和16N地块分别为118和240 kg N ha-1 ,2003年分别为103和238 kg N ha-1 。 2002年和2003年,淋溶氮损失分别为4.8–5.3和6.5–7.3 kg N ha-1 。进行了实验室实验,以估计N2 固定和反硝化的量。在0N和16N图中,N2的固色量分别为43和0 kg N ha-1 。在两个样地中,反硝化潜力都很高,并且通过反硝化损失了90%的灌溉水氮素损失。总的来说,由于灌溉水被NO3污染,总氮输入量相对较大,但以淋滤(灌溉水+降水+肥料)表示的氮外流负荷却显示出较大的负值,表明整个稻田可以作为减少N的人工湿地。

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