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1.
Biological nitrogen fixation in mixed legume/grass pastures 总被引:16,自引:2,他引:16
Biological nitrogen fixation (BNF) in mixed legume/grass pastures is reviewed along with the importance of transfer of fixed nitrogen (N) to associated grasses. Estimates of BNF depend on the method of measurement and some of the advantages and limitations of the main methods are outlined. The amounts of N fixed from atmospheric N2 in legume/grass pastures throughout the world is summarised and range from 13 to 682 kg N ha-1 yr-1. the corresponding range for grazed pastures, which have been assessed for white clover pastures only, is 55 to 296 kg N ha-1 yr-1.Biological nitrogen fixation by legumes in mixed pastures is influenced by three primary factors; legume persistence and production, soil N status, and competition with the associated grass(es). These factors and the interactions between them are discussed. Legume persistence, production and BNF is also influenced by many factors and this review centres on the important effects of soil moisture status, soil acidity, nutrition, and pests and disease.Soil N status interacts directly with BNF in the short and long term. In the short-term, increases in soil inorganic N occurs during dry conditions and where N fertiliser is used, and these will reduce BNF. In the long-term, BNF leads to accumulation of soil N, grass dominance, and reduced BNF. However, cyclical patterns of legume and grass dominance can occur due, at least in part, to temporal changes in plant-available N levels in soil. Thus, there is a dynamic relationship between legumes and grasses whereby uptake of soil N by grass reduces the inhibitory effect of soil N on BNF and competition by grasses reduces legume production and BNF. Factors affecting the competition between legumes and grasses are considered including grass species, grazing animals, and grazing or cutting management.Some fixed N is transferred from legumes to associated grasses. The amount of N transferred below-ground, predominantly through decomposition of legume roots and nodules, has been estimated at 3 to 102 kg N ha-1 yr-1 or 2 to 26% of BNF. In grazed pasture, N is also transferred above-ground via return in animal excreta and this can be of a similar magnitude to below-ground transfer.Increased BNF in mixed legume/grass pastures is being obtained through selection or breeding of legumes for increased productivity and/or to minimise effects of nutrient limitations, low soil moisture, soil acidity, and pests and disease. Ultimately, this will reduce the need to modify the pasture environment and increase the role of legumes in low-input, sustainable agriculture. 相似文献
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Junji Ishizuka 《Plant and Soil》1992,141(1-2):197-209
In the world each year 17.2×107 tons of N are biologically fixed. Biological nitrogen fixation (BNF) contributes to plant production in arable lands and in natural ecosystems. Research to improve BNF is progressing through the breeding of efficient N-fixing organisms and host plants, selection of the best combinations of host plant and microsymbiont, and by the improvement of inoculation techniques and field management. Biotechnology is useful for the creation of promising N2-fixing organisms. However, to increase plant production through enhanced BNF the constraints in establishing effective N2-fixing systems in the field should be understood and eliminated. 相似文献
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Biological nitrogen fixation (BNF) has an assured place in agriculture, mainly as a source of nitrogen for legumes. Legumes are currently grown mostly as a source of vegetable oil and as food for humans and animals, but not as nitrogen source.Other crops with BNF capability may be eventually be developed eventually. Such crops will also need mineral fertilizers to maintain a good status of soil nutrients, but their possible effects to the environment is also a concern. Fertilizers, however, will remain a necessary and sustainable input to agriculture to feed the present and increasing human population. It is not a case of whether BNF is better or worse than mineral fertilizers because both plays an important role in agriculture. 相似文献
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The response of biological nitrogen fixation (BNF) to elevated CO(2) was examined in white clover (Trifolium repens)-dominated swards under both high and low phosphorus availability. Mixed swards of clover and buffalo grass (Stenotaphrum secundatum) were grown for 15 months in 0.2 m2 sand-filled mesocosms under two CO2 treatments (ambient and twice ambient) and three nutrient treatments [no N, and either low or high P (5 or 134 kg P ha(-1)); the third nutrient treatment was supplied with high P and N (240 kg N ha(-1))]. Under ambient CO2, high P increased BNF from 410 to 900 kg ha(-1). Elevated CO2 further increased BNF to 1180 kg ha(-1) with high P, but there was no effect of CO2 on BNF with low P. Allocation of N belowground increased by approx. 50% under elevated CO2 irrespective of supplied P. The results suggest that where soil P availability is low, elevated CO2 will not increase BNF, and pasture quality could decrease because of a reduction in aboveground N. 相似文献
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Peter M. Vitousek Duncan N. L. Menge Sasha C. Reed Cory C. Cleveland 《Philosophical transactions of the Royal Society of London. Series B, Biological sciences》2013,368(1621)
New techniques have identified a wide range of organisms with the capacity to carry out biological nitrogen fixation (BNF)—greatly expanding our appreciation of the diversity and ubiquity of N fixers—but our understanding of the rates and controls of BNF at ecosystem and global scales has not advanced at the same pace. Nevertheless, determining rates and controls of BNF is crucial to placing anthropogenic changes to the N cycle in context, and to understanding, predicting and managing many aspects of global environmental change. Here, we estimate terrestrial BNF for a pre-industrial world by combining information on N fluxes with 15N relative abundance data for terrestrial ecosystems. Our estimate is that pre-industrial N fixation was 58 (range of 40–100) Tg N fixed yr−1; adding conservative assumptions for geological N reduces our best estimate to 44 Tg N yr−1. This approach yields substantially lower estimates than most recent calculations; it suggests that the magnitude of human alternation of the N cycle is substantially larger than has been assumed. 相似文献
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Lowlands comprise 87% of the 145 M ha of world rice area. Lowland rice-based cropping systems are characterized by soil flooding during most of the rice growing season. Rainfall distribution, availability of irrigation water and prevailing temperatures determine when rice or other crops are grown. Nitrogen is the most required nutrient in lowland rice-based cropping systems. Reducing fertilizer N use in these cropping systems, while maintaining or enhancing crop output, is desirable from both environmental and economic perspectives. This may be possible by producing N on the land through legume biological nitrogen fixation (BNF), minimizing soil N losses, and by improved recycling of N through plant residues. At the end of a flooded rice crop, organic- and NH4-N dominate in the soil, with negligible amounts of NO3. Subsequent drying of the soil favors aerobic N transformations. Organic N mineralizes to NH4, which is rapidly nitrified into NO3. As a result, NO3 accumulates in soil during the aerobic phase. Recent evidence indicates that large amounts of accumulated soil NO3 may be lost from rice lowlands upon the flooding of aerobic soil for rice production. Plant uptake during the aerobic phase can conserve soil NO3 from potential loss. Legumes grown during the aerobic phase additionally capture atmospheric N through BNF. The length of the nonflooded season, water availability, soil properties, and prevailing temperatures determine when and where legumes are, or can be, grown. The amount of N derived by legumes through BNF depends on the interaction of microbial, plant, and environmental determinants. Suitable legumes for lowland rice soils are those that can deplete soil NO3 while deriving large amounts of N through BNF. Reducing soil N supply to the legume by suitable soil and crop management can increase BNF. Much of the N in legume biomass might be removed from the land in an economic crop produce. As biomass is removed, the likelihood of obtaining a positive soil N balance diminishes. Nonetheless, use of legumes rather than non-legumes is likely to contribute higher quantities of N to a subsequent rice crop. A whole-system approach to N management will be necessary to capture and effectively use soil and atmospheric sources of N in the lowland rice ecosystem.IRRI-NifTAL-IFDC joint contribution. 相似文献
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Fixation and transfer of nitrogen (N) from alfalfa (Medicago sativa L.) to different grass species including timothy (Phleum pratense L.) and bromegrass (Bromus inermis Leyss) were studied under field conditions, using the15N dilution technique.The percentage of alfalfa N derived from fixation (%NF) increased throughout the growing seasons and ranged from 62 to 83%. Nitrogen transfer (NT) from alfalfa to associated grasses was evident and contributed 26,46 and 38% of the total annual N yield of associated grasses or represented absolute amounts of 5, 20 and 19 kg N ha–1 during the first, second and third year, respectively. The gradual and consistent percentage of NT that occurred before first harvest indicated that this transfer is a result of a direct excretion of N compounds from alfalfa root systems. Decomposition of root and nodule debris seems to contribute to the NT from alfalfa to associated grasses in the later cuts. All grass species benefitted similarly from alfalfa, although earlier maturing species with greater competitive ability were slightly more responsive.Contribution No. 1159 from the Plant Research Centre 相似文献
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Timothy E. Crews 《Biogeochemistry》1993,21(3):141-166
Although nitrogen is considered to be the nutrient that most commonly limits production of natural and managed terrestrial ecosystems, I propose that phosphorus may regulate productivity in many continuously cultivated agroecosystems that do not receive applications of synthetic fertilizers. One way P may limit agroecosystem productivity is by controlling nitrogen fixation of legume crops, thus affecting nitrogen availability in the overall agroecosystem. I tested this hypothesis in two studies by examining the effect of phosphorus nutrition on nitrogen fixation of alfalfa in traditional Mexican agroecosystems. All farms used in the research relied on alfalfa as the primary nitrogen source for maize cultivation and other crops, and had minimal or no reliance on synthetic fertilizers.In one study, I used the natural abundance of15N to estimate nitrogen fixation in five alfalfa plots with soils representing a wide range of P fertility. I found a correlation of r = 0.85 between foliage P concentrations and nitrogen fixation in the alfalfa plots. Mean nitrogen fixation in alfalfa plots ranged between 232–555 kg ha–1 yr–1 as estimated by the15N-natural abundance method.In a second study, I sampled soils from alfalfa plots on traditional farms located in 5 different physiographic regions of Mexico. Half of each soil sample was augmented with phosphorus in a greenhouse experiment. I grew alfalfa on the fertilized and unfertilized soils from each site and then determined nitrogenase activity (acetylene reduction) of the Rhizobium on the plant roots. Nitrogenase activity increased in the alfalfa grown on all soils with added phosphorus, with two of the five differences being statistically significant at P < 0.01, 0 and one at P < 0.05. Foliage P concentrations and nitrogenase activity were 0 positively correlated (r = 0.81,P < 0.01).0 相似文献
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Biological nitrogen fixation in trees in agro-ecosystems 总被引:1,自引:0,他引:1
The integration of trees, especially nitrogen fixing trees (NFTs), into agroforestry and silvo-pastoral systems can make a major contribution to sustainable agriculture by restoring and maintaining soil fertility, and in combating erosion and desertification as well as providing fuelwood. The particular advantage of NFTs is their biological nitrogen fixation (BNF), their ability to establish in nitrogen-deficient soils and the benefits of the nitrogen fixed (and extra organic matter) to succeeding or associated crops.The importance of NFTs leads to the question of how we can maximise or optimize their effects and how we can manage BNF and the transfer of nitrogen to associated or succeeding plantings. To be able to achieve these goals, suitable methods of measuring BNF in trees are necessary. The total nitrogen difference (TND) method is simple, but is better suited for low than high soil N conditions. The acetylene reduction assay (ARA), although sensitive and simple, has many technical limitations especially for NFTs, and the estimates of BNF have generally been very low, compared to other methods. For NFTs, the 15N techniques are still under development, but have already given some promising results (e.g., has been used to measure large genetic variability in BNF within different NFTs).Various factors affect BNF in trees. They include the age of trees, the microbial component, soil moisture, temperature, salinity, pH, soil N level and plant nutrient deficiencies. Some of the factors, e.g. temperature, affect the symbiosis more than plant growth, and differences in the effects of these factors on BNF in different NFT genotypes have been reported. These factors and research needs for improving BNF in trees are discussed. 相似文献
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湿润持续时间对生物土壤结皮固氮活性的影响 总被引:2,自引:0,他引:2
土壤可利用氮是干旱半干旱区生态系统中除水分之外的关键限制因子,研究湿润持续时间和温度变化对温性荒漠藻类结皮和藓类结皮固氮活性的影响,对于深入认识和准确评价全球变化大背景下生物土壤结皮对区域生态系统的氮贡献至关重要。通过野外调查采样,在一次较大降水事件发生后,利用开顶式生长室,采用乙炔还原法连续测定了沙坡头地区人工植被区和天然植被区两类典型生物土壤结皮固氮活性的变化,分析了湿润持续时间和模拟增温对其固氮活性的影响。研究结果表明:在经历31d持续干旱,降水发生后第4天两类结皮的固氮活性达到最大,此后随样品水分含量下降,至第10天其固氮活性将至最低;结皮固氮活性与水分含量之间呈显著的二次函数关系,其固氮活性随水分含量的增加呈先上升后下降的趋势,藻类结皮的固氮活性显著高于藓类结皮;短期模拟增温并不能显著提高其固氮活性,增温主要通过加速结皮水分散失来影响其固氮活性。上述结果反映了水分是控制生物土壤结皮固氮活性的关键因子,而实验前样品所经历的环境条件则决定了降水发生后其到达最大固氮速率的时间,野外长期观测结合控制严格的室内实验才能准确评价生物土壤结皮对区域生态系统的氮贡献。 相似文献
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古尔班通古特沙漠生物结皮固氮活性 总被引:3,自引:1,他引:3
利用乙炔还原法对新疆古尔班通古特沙漠不同类型的生物结皮(藻结皮、地衣结皮、苔藓结皮)的固氮活性(nmolC2H4m-2h-1)进行了定量研究。结果表明,不仅采样时段和结皮类型对生物结皮的固氮活性具有显著的影响(p<0.05),二者的交互效应同样对生物结皮的固氮活性具有极显著的影响(p<0.01)。各类型生物结皮固氮活性变化趋势表现为:3~5月间,藻结皮(2.26×103)>地衣结皮(6.54×102)>苔藓结皮(6.38×102)。6~10月份,各类型生物结皮的固氮能力显著提高(p<0.05),藻结皮的固氮活性最高(9.81×103),依次为地衣结皮9.06×103、苔藓结皮2.03×103。11月~翌年2月间,月均温都低于0℃,抑制了生物结皮的固氮活性,藻结皮、苔藓结皮的固氮活性降幅极显著(p<0.01),分别低达4.18×102、5.43×102,地衣结皮降低至2.78×103。生物结皮成为古尔班通古特沙漠除豆科植物外重要的氮源,为该沙漠1年生浅根系草本植物的种子萌发与植物体的生长提供丰富的有机质源,从而有利于这些植物种群的繁衍与更新,并与之共同促进对沙面的固定。 相似文献
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In an agro-ecosystem, industrially produced nitrogenous fertilizers are the principal sources of nitrogen for plant growth; unfortunately these also serve as the leading sources of pollution. Hence, it becomes imperative to find pollution-free methods of providing nitrogen to crop plants. A diverse group of free-living, plant associative and symbiotic prokaryotes are able to perform biological nitrogen fixation (BNF). BNF is a two component process involving the nitrogen fixing diazotrophs and the host plant. Symbiotic nitrogen fixation is most efficient as it can fix nitrogen inside the nodule formed on the roots of the plant; delivering nitrogen directly to the host. However, most of the important crop plants are nonleguminous and are unable to form symbiotic associations. In this context, the plant associative and endophytic diazotrophs assume importance. BNF in nonlegumes can be encouraged either through the transfer of BNF traits from legumes or by elevating the nitrogen fixing capacity of the associative and endophytic diazotrophs. In this review we discuss mainly the microbiological strategies which may be used in nonleguminous crops for enhancement of BNF. 相似文献
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生物固氮在我国农业生产中的研究现状及发展对策 总被引:7,自引:0,他引:7
简述了生物固氦在我国农业生产中3个热点的研究现状:提高现有固氦生物的固氦能力、化学模拟固氦酶、固氦微生物的生物工程,同时提出了生物固氦在令后生态农业中的发展对策。 相似文献
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Earthworm communities in conventional wheat monocropping and low-input wheat-clover intercropping systems 总被引:1,自引:0,他引:1
O SCHMIDT J P CURRY R A HACKETT G PURVIS R O CLEMENTS 《The Annals of applied biology》2001,138(3):377-388
A comparative study was conducted on earthworm communities in a conventional winter wheat monocropping system and a low‐input intercropping system in which successive crops of winter wheat were direct‐drilled into a permanent white clover sward. Earthworm abundance, biomass and species composition under the two cropping systems in the second and third years of successive cropping were assessed each spring and autumn in farm‐scale field plots at four sites using formalin and electrical extraction methods. The wheat‐clover cropping system supported larger earthworm communities (overall mean abundance 548 individuals m?2, 137 g biomass m?2) than conventional wheat monocropping (194 individuals m‐2, 36 g biomass m‐2). Between one and five more earthworm species were recorded in the wheat‐clover system than in the wheat system at three out of the four study sites. Wheat–clover cropping especially favoured species belonging to the epigeic and epigeic/anecic ecological groups such as Lumbricus castaneus, L. festivus, L. rubellus, juvenile Lumbricus and Satchellius mammalis. Earthworm communities in the wheat‐clover cropping system were comparable in size and species composition to communities normally found in perennial grassland‐type habitats such as pastures and grass‐legume leys. 相似文献
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在荒漠生态系统氮沉降背景下,研究退化植被幼苗对水分和氮素变化的响应特征,对实现植被恢复和重建具有重要意义。在塔里木盆地南缘对骆驼刺(Alhagi sparsifolia)幼苗通过2年的水分(干旱、中水和湿润)和氮素(不施氮、低氮(51 mg/kg)、中氮(102 mg/kg)和高氮(306 mg/kg))添加试验,研究骆驼刺幼苗干物质累积、生物固氮和氮效率对水氮条件变化的响应。结果表明,骆驼刺幼苗不同器官的干物质累积和吸氮效率对水氮条件变化的响应因生长年份而异,但幼苗整株干物质累积和吸氮效率在2个生长年份的变化趋势却相似。在干旱条件下,骆驼刺幼苗的干物质量、吸氮效率和生物固氮量均在低氮处理下显著增加,之后随施氮量增加而降低。水氮交互可显著提高幼苗干物质累积、吸氮效率和生物固氮量,其中以中水中氮处理的效果最好。水氮添加有降低骆驼刺幼苗氮素利用效率(NUE)的趋势,但在干旱和中水条件下施氮可显著提高幼苗的生物固氮比例,然而生物固氮比例与NUE仅在第2个生长年份呈显著负相关。在2个生长年份,骆驼刺幼苗干物质量与吸氮效率和生物固氮量呈极显著正相关关系,但与NUE和生物固氮比例并无明显相关性。这表明骆驼刺幼苗主要是通过调节吸氮效率和生物固氮量来适应水氮条件变化,进而影响幼苗干物质累积。 相似文献
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氮肥运筹对晚播冬小麦氮素和干物质积累与转运的影响 总被引:12,自引:0,他引:12
氮素平衡对干物质积累与分配的影响是农业生态系统研究的重要内容,在保障产量前提下减少氮肥施用量可减少环境污染与温室气体排放。以晚播冬小麦为研究对象,设置4个施氮量水平:0 kg/hm2(N0)、168.75 kg/hm2(N1)、225 kg/hm2(N2)、281.25 kg/hm2(N3),每个施氮量水平下设置2个追氮时期处理:拔节期(S1)、拔节期+开花期(S2),研究了氮肥运筹对晚播冬小麦氮素和干物质积累与转运及氮肥利用率的影响。结果表明:拔节期追施氮肥(S1)条件下,在225 kg/hm2(N2)基础上增施25%氮肥(N3)对开花期氮素积累总量和营养器官氮素转运量无显著影响;拔节期+开花期追施氮肥(S2)条件下,随施氮量增加,开花期氮素积累总量和花后营养器官氮素转运量升高;S2较S1显著提高成熟期籽粒及营养器官氮素积累量、花后籽粒氮素积累量及其对籽粒氮素积累的贡献率。同一施氮量条件下,S2较S1提高了成熟期的干物质积累量、开花至成熟阶段干物质积累强度和花后籽粒干物质积累量。同一追氮时期条件下,籽粒产量N2与N3无显著差异,氮肥偏生产力随施氮量增加而降低;同一施氮量条件下,S2较S1提高了晚播冬小麦的籽粒产量和氮肥吸收利用率。拔节期+开花期追施氮肥,总施氮量225kg/hm2为有利于实现晚播冬小麦高产和高效的最优氮肥运筹模式。 相似文献