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Methane emission from Indonesian rice fields with special references to the effects of yearly and seasonal variations, rice variety, soil type and water management

机译:印度尼西亚稻田的甲烷排放量,特别涉及年度和季节变化,稻米品种,土壤类型和水管理的影响

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Total amounts of CH emission from a Sumatra rice field were in the ranges 29·5–48·2 and 43·0–64·6 g CH m season for the plots with chemical fertilizer (CF-plot) and those with rice straw application (RS-plot), respectively. Nearly the same amounts of CH were emitted in the first and second half of the growth period, irrespective of rice straw application. The increase in the amounts of CH emission by rice straw application were from 1·3 to 1·6 times. There was no significant difference in the mean CH emission rates between rainy and dry seasons. Rain-fed conditions decreased the CH emission by 27–37% compared with continuously flooded conditions. Total amounts of CH emission from a rice field growing eight popular modern rice varieties in Indonesia were in the ranges 32·6–41·7 and 51·3–64·6 g CH m season for CF- and RS-plots, respectively. Total amounts of CH emission from four Sumatra rice fields with different soil types (a Typic Paleudult, a Typic Sulfaquent, a Typic Tropohumult and a Typic Tropopsament) were in the range 22·1 (a Typic Sulfaquent) to 53·4 (a Typic Tropohumult) g CH m season for CF-plots and from 26·7 (a Typic Sulfaquent) to 72·2 (a Typic Tropohumult) g CH m season for RS-plots. CH emission rates from Bali rice fields with soils of volcanic ash origin were very low; 3·5–7·7 and 5·3–14·3 g CH m season for CF- and RS-plots, respectively.Respective rice fields showed the specific productivity of grain production, and CH emission rates for 1 kg grain production were scattered widely from 8–11 and 11·24 g CH kg grain for rice fields of volcanic ash origin to 83 and 121 g CH kg grain for a Sumatra rice field for CF- and RS-plots, respectively. Water management was also an important factor in decreasing the CH emission rate. Copyright © 1998 John Wiley & Sons, Ltd.
机译:苏门答腊稻田CH排放总量在使用化学肥料(CF-地块)和稻草施用地块的CH·m季节为29·5–48·2和43·0–64·6 g CH m季节。 (RS-图)。不论施用稻草,在生育期的前半期和后半期排放的甲烷量几乎相同。稻草还田导致的CH排放量增加了1·3倍至1·6倍。在雨季和旱季之间,平均CH排放速率没有显着差异。与持续淹水的条件相比,雨养条件下的CH排放降低了27-37%。在印度尼西亚,种植八种流行的现代水稻品种的稻田的CH-排放总量分别在32·6–41·7和51·3–64·6 g CH m季节范围内。苏门答腊四个不同土壤类型的稻田(典型的古埃及,典型的硫磺,典型的热带风水和典型的Tro虫)的CH排放总量在22·1(典型的硫磺)至53·4(典型的硫磺)之间CF-plots用Tropphumult)g CH m季节,RS-plots用从26·7(Typic Sulfaquent)到72·2(Typic Tropohumult)g CH m季节。来自火山灰来源的巴厘岛稻田的甲烷排放量非常低; CF-图和RS-图的CH m季节分别为3·5-7·7和5·3-14·3 g。分别在稻田中显示出谷物生产的比生产率,1 kg谷物的CH排放速率为散布的火山灰产地的稻田分别为8-11和11·24 g CH kg谷物,而CF-和RS-plot的苏门答腊稻田分别为83和121 g CH kg谷物。水资源管理也是降低CH排放速率的重要因素。版权所有©1998 John Wiley&Sons,Ltd.

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