Oenema Oene, Tamminga Seerp
Environmental Sciences, Wageningen University & Research Center, P.O.Box 47, NL-6700AA, Wageningen, The Netherlands.
Sci China C Life Sci. 2005 Sep;48 Suppl 2:871-87. doi: 10.1007/BF03187126.
Animal production systems convert plant protein into animal protein. Depending on animal species, ration and management, between 5% and 45 % of the nitrogen (N) in plant protein is converted to and deposited in animal protein. The other 55%-95% is excreted via urine and feces, and can be used as nutrient source for plant (= often animal feed) production. The estimated global amount of N voided by animals ranges between 80 and 130 Tg N per year, and is as large as or larger than the global annual N fertilizer consumption. Cattle (60%), sheep (12%) and pigs (6%) have the largest share in animal manure N production. The conversion of plant N into animal N is on average more efficient in poultry and pork production than in dairy production, which is higher than in beef and sheep production. However, differences within a type of animal production system can be as large as differences between types of animal production systems, due to large effects of the genetic potential of animals, animal feed and management. The management of animals and animal feed, together with the genetic potential of the animals, are key factors to a high efficiency of conversion of plant protein into animal protein. The efficiency of the conversion of N from animal manure, following application to land, into plant protein ranges between 0 and 60%, while the estimated global mean is about 15%. The other 40%-100% is lost to the wider environment via NH(3) volatilization, denitrification, leaching and run-off in pastures or during storage and/or following application of the animal manure to land. On a global scale, only 40%-50% of the amount of N voided is collected in barns, stables and paddocks, and only half of this amount is recycled to crop land. The N losses from animal manure collected in barns, stables and paddocks depend on the animal manure management system. Relative large losses occur in confined animal feeding operations, as these often lack the land base to utilize the N from animal manure effectively. Losses will be relatively low when all manure are collected rapidly in water-tight and covered basins, and when they are subsequently applied to the land in proper amounts and at the proper time, and using the proper method (low-emission techniques). There is opportunity for improving the N conversion in animal production systems by improving the genetic production potential of the herd, the composition of the animal feed, and the management of the animal manure. Coupling of crop and animal production systems, at least at a regional scale, is one way to high N use efficiency in the whole system. Clustering of confined animal production systems with other intensive agricultural production systems on the basis of concepts from industrial ecology with manure processing is another possible way to improve N use efficiency.
动物生产系统将植物蛋白转化为动物蛋白。根据动物种类、日粮和管理方式的不同,植物蛋白中5%至45%的氮(N)会转化并沉积在动物蛋白中。其余的55% - 95%则通过尿液和粪便排出,可作为植物(通常是动物饲料)生产的养分来源。据估计,全球动物排出的氮量每年在80至130太克之间,与全球每年的氮肥消费量相当或更大。牛(60%)、羊(12%)和猪(6%)在动物粪便氮产量中占比最大。与乳制品生产相比,家禽和猪肉生产中植物氮向动物氮的转化平均效率更高,而乳制品生产又高于牛肉和羊肉生产。然而,由于动物的遗传潜力、动物饲料和管理的巨大影响,一种动物生产系统内的差异可能与不同类型动物生产系统之间的差异一样大。动物和动物饲料的管理以及动物的遗传潜力是植物蛋白高效转化为动物蛋白的关键因素。动物粪便施用于土地后,其中氮转化为植物蛋白的效率在0%至60%之间,全球平均估计约为15%。其余的40% - 100%则通过氨(NH₃)挥发、反硝化作用、淋溶以及在牧场中或储存期间和/或动物粪便施用于土地后径流流失到更广泛的环境中。在全球范围内,只有40% - 50%排出的氮量在畜舍、马厩和围场中收集到,而其中只有一半被回收到农田。畜舍、马厩和围场中收集的动物粪便中的氮损失取决于动物粪便管理系统。在集约化动物饲养场中损失相对较大,因为这些场所往往缺乏有效利用动物粪便中氮的土地基础。当所有粪便迅速收集到不透水且有盖的水池中,并随后以适当的数量、在适当的时间和使用适当的方法(低排放技术)施用于土地时,损失将相对较低。通过提高畜群的遗传生产潜力、动物饲料的组成以及动物粪便的管理,有机会提高动物生产系统中的氮转化效率。将作物和动物生产系统耦合,至少在区域范围内,是提高整个系统氮利用效率的一种方法。基于工业生态学概念和粪便处理,将集约化动物生产系统与其他集约化农业生产系统聚集在一起是提高氮利用效率的另一种可能方法。