Surface N balances and reactive N loss to the environment from global intensive agricultural production systems for the period 1970-2030

Data for the historical years 1970 and 1995 and the FAO-Agriculture Towards 2030 projection are used to calculate N inputs (N fertilizer, animal manure, biological N fixation and atmospheric deposition) and the N export from the field in harvested crops and grass and grass consumption by grazing animals. In most industrialized countries we see a gradual increase of the overall N recovery of the intensive agricultural production systems over the whole 1970-2030 period. In contrast, low N input systems in many developing countries sustained low crop yields for many years but at the cost of soil fertility by depleting soil nutrient pools. In most developing countries the N recovery will increase in the coming decades by increasing efficiencies of N use in both crop and livestock production systems. The surface balance surplus of N is lost from the agricultural system via different pathways, including NH3 volatilization, denitrification, N2O and NO emissions, and nitrate leaching from the root zone. Global NH3-N emissions from fertilizer and animal manure application and stored manure increased from 18 to 34 Tg·yr-1 between 1970 and 1995, and will further increase to 44 Tg·yr-1 in 2030. Similar developments are seen for N2O-N (2.0 Tg·yr-1 in 1970, 2.7 Tg·yr-1 in 1995 and 3.5 Tg·yr-1 in 2030) and NO-N emissions (1.1 Tg·yr-1 in 1970, 1.5Tg·yr-1 in 1995 and 2.0 Tg·yr-1 in 2030).     

Surface N balances and reactive N loss to the environment from global intensive agricultural production systems for the period 1970–2030

Data for the historical years 1970 and 1995 and the FAO-Agriculture Towards 2030 projection are used to calculate N inputs (N fertilizer, animal manure, biological N fixation and atmospheric deposition) and the N export from the field in harvested crops and grass and grass consumption by grazing animals. In most industrialized countries we see a gradual increase of the overall N recovery of the intensive agricultural production systems over the whole 1970–2030 period. In contrast, low N input systems in many developing countries sustained low crop yields for many years but at the cost of soil fertility by depleting soil nutrient pools. In most developing countries the N recovery will increase in the coming decades by increasing efficiencies of N use in both crop and livestock production systems. The surface balance surplus of N is lost from the agricultural system via different pathways, including NH3 volatilization, denitrification, N₂O and NO emissions, and nitrate leaching from the root zone. Global NH₃-N emissions from fertilizer and animal manure application and stored manure increased from 18 to 34 Tg·yr^?1 between 1970 and 1995, and will further increase to 44 Tg·yr^?1 in 2030. Similar developments are seen for N₂O-N (2.0 Tg·yr^?1 in 1970, 2.7 Tg·yr^?1 in 1995 and 3.5 Tg·yr^?1 in 2030) and NO-N emissions (1.1 Tg·yr^?1 in 1970,1.5 Tg·yr^?1 in 1995 and 2.0 Tg·yr^?1 in 2030).     

集约化生产对农田土壤碳氮含量及δ13C和δ15N同位素丰度的影响

集约化生产下农田土壤碳、氮含量变化是衡量土壤肥力持久性的重要指标.对常规水稻-蚕豆轮作地、露地蔬菜地、3年塑料大棚地和10年以上塑料大棚地的土壤pH、电导率(EC)、土壤有机碳(SOC)和总氮(TN)含量及δ13C和δ15N同位素丰度进行测定,研究了集约化生产程度对土壤特性的影响.结果表明:与水稻-蚕豆轮作地相比,露地蔬菜地、3年塑料大棚地和10年以上塑料大棚地0 ～20 cm耕层土壤pH分别降低1.1、0.8和0.7,而土壤EC分别是水稻-蚕豆轮作地的4.2、4.9和5.2倍;土壤碳、氮含量随塑料大棚地生产年限的增加总体上呈先增大后减小的趋势.与水稻-蚕豆轮作地相比,10年以上塑料大棚地0～20、20～40、40 ～60、60 ～ 80、80 ～ 100 cm土层的土壤SOC含量分别下降了54％、46％、60％、63％和59％,土壤TN含量分别下降了53％、53％、71％、82％和85％.农田集约化生产程度显著影响土壤SOC、TN含量和δ13C、δ15N丰度,土壤δ13C丰度与SOC含量呈显著负相关.土壤δ13C丰度可作为评价农田土壤碳循环受人为干扰强度的指标.     

Reducing soil erosion and the loss of soil fertility for environmentally-sustainable agricultural cropping and livestock production systems

My proposals for reducing soil erosion are based on my experience of assessing erosion, largely in Britain, both of cultivated land and of upland grazings. I have assessed the extent and rates of erosion in the field mostly by using easily‐ and rapidly‐used photographic and measurement techniques, rather than by using experimental plots set up either in the field or laboratory which overstate erosion. Policies which have governed the economics of agricultural production have also been examined. Much of the increase in occurrence of runoff and soil erosion in Britain is due to changes in land use and in intensity of use since the Agriculture Act was passed in 1947, and especially since joining the Common Market in 1973, with its even greater emphasis on paying for increased production. The increasing numbers of animals grazing the land, especially sheep, led to the initiation and erosion of bare soil in the uplands and to trampling and puddling of soils in lowland pastures. There is evidence that runoff from the land, and sedimentation of water courses have also increased. In the cultivated lowlands, the expansion in area of land drilled to winter cereals, the increase in area of land sown to maize or used to rear outdoor pigs, changes in farming techniques, and larger machines working in larger fields can explain much of the increase in erosion. Reversing some of these changes, for example by lowering the intensity of grazing and inserting grass (set‐aside) into the arable rotation will reduce the extent of erosion. Other techniques to reduce erosion are well‐known but need national and international agricultural policies that improve farmers' incomes to bring them into use. In developed countries, erosion need not reduce soil fertility, as nutrients removed from the soil by animals or crops can be affordably replaced. This may not be so in other parts of the world. Education of farmers also has a vital role to play in persuading them to use the land more sustainably, for many of the impacts of erosion such as flooding and pollution of water supplies bear on society as a whole, not just farmers who are themselves little affected. The principles devised to reduce erosion in developed countries are likely to be successful in developing countries. However, it may take many years for better and more sustainable agricultural policies at national and international level to be devised and brought into being.     

Productivity and technical efficiency of suckler beef production systems: trends for the period 1990 to 2012

Over the past 23 years (1990 to 2012), French beef cattle farms have expanded in size and increased labour productivity by over 60%, chiefly, though not exclusively, through capital intensification (labour–capital substitution) and simplifying herd feeding practices (more concentrates used). The technical efficiency of beef sector production systems, as measured by the ratio of the volume value (in constant euros) of farm output excluding aids to volume of intermediate consumption, has fallen by nearly 20% while income per worker has held stable thanks to subsidies and the labour productivity gains made. This aggregate technical efficiency of beef cattle systems is positively correlated to feed self-sufficiency, which is in turn negatively correlated to farm and herd size. While volume of farm output per hectare of agricultural area has not changed, forage feed self-sufficiency decreased by 6 percentage points. The continual increase in farm size and labour productivity has come at a cost of lower production-system efficiency – a loss of technical efficiency that 20 years of genetic, technical, technological and knowledge-driven progress has barely managed to offset.