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Ammonia emissions from broiler manure during handling

机译:鸡粪处理过程中氨气的排放

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Broiler manure from poultry farms has become a commercial fertiliser mainly for farmers with ecological production. However, there is a lack of knowledge about nutrient losses from broiler manure during storage and after spreading within crop production. The aim was to determine what happens to the material during the course of handling, with special emphasis on ammonia losses, and to see how different measures affect the amount of ammonia losses. Broiler manure was stored for seven months from October until May. The manure was placed in two separate heaps, one uncovered and one covered with a 30 cm thick layer of straw. Ambient air temperature and temperatures in the heaps were recorded continuously. Ammonia emissions were measured five times during the storage period. A micrometeorological mass balance method, described by Schjomng et al. (1992) and applied by Karlsson (1994) was used. At the end of May, broiler manure from the uncovered heap and a commercial product based on broiler manure (Binadan) were spread on arable land at a rate of 110 kg total-N per ha. Ammonia emissions were measured from plots fertilised with broiler manure and Binadan, respectively, with and without harrowing four hours after spreading. A micrometeorological methodof measuring gaseous NH_3 was used, which is based on passive diffusion sampling close to the ground (Svensson, 1994). Temperature measurements in the heaps during storage revealed high biological activity. The highest temperatures were observed in thecovered heap. Despite this, the nitrogen lost in the form of ammonia was limited. The cumulative ammonia losses in per cent of total N were 7 percent from the uncovered heap and 10 percent from the covered heap. In total, 13.5 percent of the total nitrogen in the broiler manure was lost as ammonia after spreading without incorporation of the manure and 7.5 percent was lost from plots with incorporation four hours after spreading. After incorporation no ammonia emission occurred. No emissions occurred from plots fertilised with Binadan.
机译:家禽场的肉鸡粪便已成为一种主要用于具有生态生产能力的农民的商业肥料。但是,缺乏关于在存储过程中以及在作物生产中传播后从肉鸡粪中损失养分的知识。目的是确定在处理过程中材料发生了什么变化,并特别强调氨的损失,并了解不同的措施如何影响氨的损失量。从十月到五月,肉鸡粪便被保存了七个月。将粪肥放在两个单独的堆中,一个不覆盖,另一个用30厘米厚的稻草覆盖。连续记录环境温度和堆中温度。在储存期间对氨气排放进行了五次测量。一种微气象质量平衡方法,由Schjomng等人描述。 (1992),并由Karlsson(1994)应用。 5月底,未覆盖堆肥中的肉鸡粪便和一种以肉鸡粪便为基础的商业产品(Binadan)以每公顷总氮110千克的速率分布在耕地上。分别在有和没有撒播四个小时的情况下,从用肉鸡粪肥和Binadan施肥的地块测得的氨气排放量。使用了一种微气象学的方法来测量气态NH_3,该方法基于靠近地面的被动扩散采样(Svensson,1994)。在储存过程中堆中的温度测量显示出高生物活性。在覆盖的堆中观察到最高温度。尽管如此,以氨形式损失的氮却是有限的。在总氮量中,氨的累积损失为裸露堆中的7%和有盖堆中的10%。总共,在未掺入粪肥的情况下,传播后的肉鸡粪便中的总氮损失为氨的13.5%,在蔓延四个小时后从掺入的土地中损失了7.5%。掺入后没有氨排放发生。用比纳丹施肥的地块未发生排放。

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