片麻岩新成土中氮素淋溶迁移的模拟研究

采用室内土柱模拟的方法,研究片麻岩新成土中不同肥料、不同施氮量对氮素垂直运移的影响。结果表明,随着施氮量增加,硝态氮和铵态氮淋溶浓度增大,氮素淋失量增多。中等施氮量下施用有机无机混合肥可以减少氮素淋失。尿素、有机无机混合肥、氮磷复合肥中硝态氮淋失总量比值为671∶583∶629。尿素硝态氮淋失率平均为29.0%,氮磷复合肥硝态氮淋失率平均为27.8%,有机无机混合肥硝态氮淋失率平均为23.7%。随着土层深度的增加,60cm处和90cm处硝态氮淋失量差异不显著,两处硝态氮淋失量比值为1∶1.03,铵态氮的淋失量增加显著,两处铵态氮淋失量比值为1∶2.4。在片麻岩新成土壤地区,土壤培肥应本着少量多次原则。     

旱作地区长期小麦连作和苜蓿连作土壤剖面的矿质氮研究

对不同施肥条件下23年小麦连作地和苜蓿连作地土壤矿质氮分布和累积进行研究,探讨种植浅根系和深根系植物对硝态氮淋溶的影响。结果表明,不施肥(CK)和单施磷(P)肥,小麦和苜蓿连作地土壤硝态氮主要集中在0—60 cm土层,0—60 cm土层以下硝态氮含量变化稳定并小于2 mg/kg。氮肥、磷肥和有机肥配施(NPM)时,小麦连作地土壤硝态氮累积在20—100 cm和140—320 cm土层,年累积速率可达42.12 kg/(hm2.a);苜蓿连作土壤硝态氮主要集中在0—60 cm土层,仅在200—300 cm土层出现轻微累积,年累积速率仅为1.01 kg/(hm2.a)。在不施肥和单施磷肥下,种植小麦或苜蓿对土壤硝态氮残留量影响不显著,而氮、磷和有机肥配施时,小麦连作地土壤硝态氮残留量迅速增加,并与不施肥、单施磷肥处理有显著差异;苜蓿连作地土壤硝态氮残留量虽有少量增加,但与不施肥、单施磷肥处理无显著差异。不施肥、单施磷肥和氮、磷和有机肥配施,小麦连作、苜蓿连作地土壤剖面铵态氮含量主要在10—20 mg/kg之间波动,在土壤剖面无明显的累积现象,铵态氮残留量受施肥和作物种类的影响不显著。     

日光温室土壤剖面矿质态氮的含量、累积及其分布特性

测定了西安郊区和杨凌地区日光温室栽培番茄生长期间及收获后土壤剖面矿质态氮(铵态氮及硝态氮)的含量,分析了不同形态氮素在土壤剖面的累积及分布情况。结果表明,随着番茄的生长,土壤剖面硝态氮含量逐渐降低,降低的幅度因土壤层次不同而异;土壤剖面铵态氮以3月份含量最高,11月份与5月份相近。番茄收获后土壤剖面残留矿质氮以硝态氮为主,约占土壤剖面矿质氮的比例为80%～90%;残留的铵态氮在土壤剖面的分布相对较为一致。蔬菜生长期间及收获时日光温室土壤剖面硝态氮累积量均表现出在土壤表层相对累积现象,且温室土壤剖面硝态氮的残留量仍高于露地及高产农田。为减少硝态氮淋失带来的环境问题,除合理施用氮肥外,如何减少日光温室蔬菜作物收获后残留硝态氮的淋溶是值得进一步研究的问题。     

有机肥替代化肥氮素对麦田土壤碳氮迁移特征的影响

利用小麦田间试验,设置控释尿素(CRU)、有机肥(OF)替代30%,50%,70%控释尿素氮量处理,并以普通尿素(Urea)为对照,研究等氮条件下有机肥替代不同比例化肥氮素对土壤碳氮迁移特征及小麦产量的影响。结果表明:有机肥处理小麦总生物量较Urea显著增加13.83%～17.57%,籽粒产量增加1.6%～10.5%,随有机肥替代化肥氮素比例增加,籽粒增产效应降低,70%OF与Urea无显著差异,但显著低于CRU处理。CRU、30%OF和50%OF处理氮素农学效率较Urea显著提高90.2%～124.4%,70%OF与Urea相比差异不显著。有机肥比例增加,土壤总碳含量呈上升趋势,且高于CRU和Urea;全氮含量大致呈下降趋势,整个生育期先增加后降低,30%OF自灌浆期至成熟期含量高于其他施氮处理。随土层深度增加,硝态氮和铵态氮含量减少,有机肥比例增加,各层土壤硝态氮减少,铵态氮增加(尤以返青期最为显著);整个生育期土壤无机氮呈下降趋势,但与Urea相比,有机肥处理的硝态氮主要集中在0—40 cm土层,且0—100 cm土壤铵态氮含量高于Urea和CRU(苗期除外)。因此,用30%～50%有机肥替代化肥氮素,配合控释尿素施用,可显著增加土壤总碳和铵态氮含量,减少60—100 cm土壤硝态氮淋溶,提高小麦氮素利用率和籽粒产量。     

小麦-玉米轮作体系下氮肥对长期不同施肥处理土壤氮含量及作物吸收的影响

以长期不同施肥处理土壤为对象,研究了不同施肥土壤中施用氮肥后土壤氮素含量、微生物固持及释放和作物吸收及利用特性。结果表明,施用氮肥显著增加长期不施肥土壤(NF)矿质氮含量,对长期施用化肥土壤(NPK)和有机无机配施土壤(MNPK)矿质态氮含量无显著影响;施用氮肥对NF中土壤微生物生物量氮(SMBN)含量无显著影响,使拔节期NPK和MNPK中SMBN含量分别增加了4.3倍和0.8倍。从小麦拔节期到开花期,NPK和MNPK中土壤微生物生物量氮含量分别显著降低51%和56%。小麦收获时NPK和MNPK土壤氮肥的利用率分别为36%和45%;而NF土壤所施入的氮素几乎未被小麦吸收利用,但在玉米季有34%被吸收。小麦收获时,NF土壤施入的氮肥有50%以上淋溶至土壤30 cm以下土层,施氮也显著提高了NPK土壤30～50 cm土层硝态氮含量,但施用氮肥对MNPK土壤0～100 cm剖面硝态氮含量无显著影响。说明长期有机无机配施增强了土壤氮素的缓冲能力,协调了土壤氮素固持与作物吸氮间的关系,为提高氮素利用率,减少氮素对环境影响的有效手段。     

氮肥用量及施用时间对土体中硝态氮移动的影响

土连续两年小麦—玉米轮作条件下 ,播前一次施氮量 130～ 5 2 0kghm-2 a-1时 ,氮肥用量对硝态氮在土体中的移动深度没有影响 ,但土壤剖面中残留的硝态氮量随施氮量增加显著增加。播前一次施用氮肥 ,差减法计算的肥料氮表观回收率 (作物携出量和土壤硝态氮的残留量 )为 6 2 %～ 82 7% ;就作物而言小麦的携出率高于玉米 ,在玉米生长季节有更多的硝态氮可能被淋移至土壤剖面的下层。小麦—玉米轮作一年 ,不同的施氮时间对肥料氮的表观回收率以及硝态氮在土壤剖面中的分布、累计没有明显影响。土区合适的氮肥用量是控制硝态氮向深层移动的主要措施     

不同施肥下冬小麦生长过程中土壤矿质氮变化及其与冬小麦叶片SPAD值的关系

通过调查分析,研究了土长期施肥条件下土壤中矿质氮含量变化及其与地上冬小麦叶片SPAD值。结果表明:(1)整个冬小麦生长期不同土层硝态氮和铵态氮的变化趋势不一致,硝态氮含量是先下降后上升的变化,而铵态氮含量呈一直上升的变化趋势。在没有施过氮肥的处理中,0—20cm,20—40cm土层中土壤硝态氮、铵态氮含量显著低于施用氮肥的处理;(2)冬小麦生长时期,各个处理叶片SPAD值各异,但都是先升高后下降的变化,无氮肥施用的叶片SPAD值低于施氮肥的处理;(3)冬小麦各个生长时期叶片SPAD值与土壤不同层次(0—20cm,20—40cm)硝态氮含量呈正相关关系,而与铵态氮含量相关性不显著,这表明小麦是对硝态氮较为敏感的作物。本试验结果可以为进一步合理调控氮肥施用、明确施氮对小麦产量和品质的影响提供一定的基础依据。     

岩溶流域不同土壤剖面溶解性碳氮分布和淋失特征

选取了重庆青木关岩溶流域不同土壤剖面,按10 cm间隔取样,测试各种土壤溶解碳氮含量,探讨不同土壤剖面溶解碳氮分布和淋失特征。结果表明,岩溶流域不同地质背景、植被类型和土地利用方式下的土壤剖面溶解碳氮均具有横向和垂向差异。砂岩区林地土壤DOC、DON和铵态氮含量高于灰岩区的土壤,而其硝态氮含量比灰岩区土壤低。灰岩区土壤DOC和DON含量为草地≈林地退耕还林地灌丛耕地(稻田除外),它们均随着深度增加而降低。岩溶区土壤DOC和DON与土壤pH值成反比,受富钙镁偏碱的岩溶生态环境制约,土壤溶解性有机碳氮会发生中和或螯合反应而被固定。岩溶区特殊的土壤剖面结构使得土壤DOC和DON在降雨条件下存在淋失的可能性。不同土壤剖面溶解无机氮形态以硝态氮为主,其次为铵态氮,亚硝态氮含量较低。林地铵态氮受植被类型影响较小,且低于耕地。不同土壤剖面硝态氮含量为耕地土灌丛土退耕还林土草地土林地土,其含量均随深度增加而升高,具有累积效应,表明土壤硝态氮发生了淋溶作用,其在降雨条件下极易淋失进入岩溶地下水中。     

片麻岩新成土中硝态氮垂直运移规律模拟研究

采用室内土柱模拟的方法,研究河北省太行山片麻岩新成土中不同肥料、不同施氮量对硝态氮垂直运移的影响。结果表明,尿素、有机无机混合肥、氮磷复合肥中硝态氮淋失总量比值为1∶0.87∶0.94。中等施氮量下,有机无机复混肥可以降低氮素淋失。尿素硝态氮淋失率平均为29%,氮磷复合肥平均为27.8%,有机无机混合肥平均为23.7%。60 cm和90 cm处硝态氮淋失量比值为1∶1.03,差异不显著。淋溶结束后,有机无机混合肥在不同土层各处理中硝态氮含量最高,尿素硝态氮含量最低。     

施氮量对植烟土壤不同土层无机氮质量含量的调控

为研究不同施氮量对土壤各层次和烤烟各生长期土壤中无机氮质量含量的影响,大田试验中设置5个氮肥施用量并分配在基肥、苗肥和追肥时期施用,烟苗移栽后第5周开始分7次钻取3个土层样,样品冷藏贮存并用流动注射分析仪测定硝态氮和铵态氮质量含量。结果表明：各施氮处理在移栽后第6周前0～20 cm土壤中硝态氮质量含量大于铵态氮,施用氮肥越多,土壤中无机氮质量含量提高幅度越大,施氮肥对0～20 cm土壤中无机氮质量含量的影响在烟株生育前期要远大于对20～40 cm土壤中无机氮质量含量的影响,同一时期不同深度比较,0～20 cm土层中硝态氮质量含量略大于20～40 cm和40～60 cm土层的硝态氮质量含量;烟株移栽7周后,0～20 cm土层中硝态氮被极大耗竭。各施氮量在各土层铵态氮质量含量变化幅度远大于硝态氮,铵态氮质量含量从第6周即开始上下波动,并在50 mg/kg附近上下变动,第8周土壤各层铵态氮质量含量有一个上升峰,而硝态氮质量含量在第7周停止快速下降后进入0～100 mg/kg范围的较平稳波动阶段。认为：不同施氮量对于生育前期和0～20 cm土层硝态氮质量含量影响深刻,但促进烤烟打顶前足量吸收并形成健壮烟株的合适施氮量还需结合烟草产量与品质而定;铵态氮调控是调节后期氮供应的关键。     

施氮量和土壤含水量对黑麦草还田红壤氮素矿化的影响

目标 氮素矿化是决定土壤供氮能力的重要生态过程,养分添加和水分在调节土壤的氮转化方面起着重要的作用。探讨施氮和土壤水分对黑麦草还田过程中土壤氮素矿化的影响有利于进一步优化红壤旱地作物生产的水肥管理。 【方法】 通过室内培养试验,研究了施氮量 (0、60、120 mg/kg) 和土壤含水量 (15%、30%、45%) 对红壤旱地黑麦草还田过程中土壤净硝化量、氨化量和氮矿化量的影响。 【结果】 土壤含水量15%时,施氮有利于提高黑麦草还田初期土壤净硝化量,施氮量120 mg/kg抑制了黑麦草还田后期土壤硝化作用。在30%土壤含水量时,施氮量120 mg/kg明显抑制了黑麦草还田后期土壤硝化作用。土壤含水量45%抑制了黑麦草还田初期不同施氮水平下土壤净硝化量,但增加了黑麦草还田91 d时土壤净硝化量,且施氮量60 mg/kg下的净硝化量显著高于120 mg/kg水平下的。土壤净氨化量在整个黑麦草还田过程中均为正值,且呈现多次升高-降低的往复动态变化。土壤净氨化量在三种土壤含水量下均表现为施氮条件下的显著高于不施氮处理。土壤含水量的增加有利于提高施氮量120 mg/kg下黑麦草还田初期土壤的氨化作用,但降低了黑麦草还田后期土壤净氨化量。相比不施氮,三个含水量条件下的施氮处理在黑麦草还田过程中的大部分阶段都显著增加了土壤净氮矿化量,土壤含水量30%条件下土壤净氮矿化量的变化最大。相比土壤含水量15%,30%含水量促进了黑麦草还田中期 (13～57 d) 土壤净氮矿化量的增加,45%含水量抑制了黑麦草还田后期 (73～91 d) 土壤净氮矿化量。 【结论】 红壤区旱地黑麦草还田时应合理施入化学氮肥 (60 mg/kg),在黑麦草还田初期保持较高的土壤含水量 (45%) 能够抑制土壤的氮矿化作用,还田中后期适当降低土壤含水量 (30%)有利于增加土壤氮素的矿化。      

土壤增氧方式对其氮素转化和水稻氮素利用及产量的影响

以3种不同生态型水稻品种中浙优1号(水稻)、IR45765-3B(深水稻)和中旱221(旱稻)为材料,比较研究了不同增氧方式(T1-增施过氧化钙、T2-微纳气泡水增氧灌溉、T3-表土湿润灌溉和CK-淹水对照)下稻田土壤氮素转化和水稻氮素吸收利用特性。结果表明:1)增氧处理明显改善土壤氧化还原状况,3种增氧方式下土壤氧化还原电位均高于CK。稻田增氧促进土壤氮素硝化,在分蘖期和齐穗期T1、T2和T3的土壤硝化强度和脲酶活性均显著高于CK,反硝化强度显著低于CK。2)不同增氧处理对水稻氮素吸收的影响不同,在拔节期、齐穗期和完熟期3品种的植株氮素积累量均表现为T1、T2显著高于CK,而T3显著低于CK;在完熟期,T1处理下中浙优1号、IR45765-3B和中旱221植株氮素积累量分别较CK增加了21.2%、13.2%和17.0%,而T2处理下3品种的植株氮素积累量分别较CK增加了14.3%、6.9%和9.1%。3)与CK相比,T1和T2显著提高水稻籽粒产量和收获指数,氮素籽粒生产效率与CK无显著差异,而T3显著增加水稻氮素干物质生产效率和氮素籽粒生产效率。可见,施用过氧化钙和微纳气泡水增氧灌溉能有效改善稻田土壤氧化还原状况,不仅显著提高水稻产量,而且显著增强稻田氮的硝化而减少氮素损失,从而提高水稻氮素积累量和氮素收获指数。     

Understanding the soil nitrogen cycle

Abstract. A quantitative knowledge of nitrogen cycle processes is required to design strategies for decreasing leakage of N from agriculture to the wider environment. However, it is remarkably difficult to make reliable measurements of many of the key processes under realistic field conditions. In impermeable soils hydrologically separated plots provide an invaluable method of measuring leaching and runoff. Estimates of nitrate leaching using porous ceramic cups agree well with lysimeter measurements on sandy soil but are suspect on more structured soils. Estimates of N₂O flux from soil are subject to great spatial heterogeneity; developing long path-length measuring techniques may overcome this problem.
¹⁵N labelling is valuable for assessing fertilizer N loss, forms of N left in soil and the fate of N from crop residues. The combination of experimental and modelling approaches can provide insights that are otherwise unattainable, including a basis for more precise advice on N fertilization.
Mineralization of soil organic matter and crop or animal residues provides much of the nitrate leached during winter under the climatic conditions of north-west Europe, because mineralization is poorly synchronized with crop N uptake. Maintenance of crop cover during winter can greatly decrease leaching but the long-term effects on the N cycle of winter cover crops or incorporating cereal straw are not yet clear.     

Transformations of nitrogen fertilizers in soil

The effects of ¹⁵N-labelled urea, (NH₄)₂SO₄ and KNO₃ on immobilization, mineralization, nitrification and ammonium fixation were examined under aerobic conditions in an acid tropical soil (pH 4.0) and in a neutral temperate soil (pH 6.8). Urea, (NH₄)₂SO₄ and KNO₃ slightly increased net mineralization of soil organic nitrogen in both soils. There was also an apparent Added Nitrogen Interaction (ANI) i.e. added labelled NH₄-N stood proxy for unlabelled NH₄-N that would otherwise have been immobilized. So far as immobilization and nitrification were concerned, urea and (NH₄)₂SO₄ behaved very similarly in each soil. Immobilization of NO₃-N was negligible in both soils. Some of the added labelled NH₄-N was rapidly fixed, more by the temperate soil than by the tropical soil. This labelled fixed NH₄-N decreased during incubation, in contrast to labelled organic N, which did not decline.     

Quantifying soil nitrogen mineralization to improve fertilizer nitrogen management of sugarcane

Intensive use of synthetic nitrogen (N) fertilizers for sugarcane (Saccharum spp.) production presents environmental challenges for water and air quality as well as impacts profitability for producers. Central to these concerns is a widespread reliance on yield-based recommendations that invoke generic models of crop N response but lack any means to account for variations in soil N-supplying power, a critical determinant of fertilizer N need for cereal, fiber, and tuber crops. The work reported herein was designed to ascertain the impact of soil N mineralization on sugarcane response to N fertilization and was carried out in conjunction with eight N-response trials conducted between 2006 and 2010 at field sites in the largest sugarcane-cultivated area in Brazil. Soil samples were utilized in categorizing the sites as highly responsive, moderately responsive, or nonresponsive to fertilizer N, based on two chemical indices of soil N availability, the Illinois Soil Nitrogen Test (ISNT) and direct steam distillation (DSD), and assessments of (1) net mineralization during aerobic incubation for 12 weeks and (2) incubation-induced changes in soil N fractions obtained by acid (total hydrolyzable N, hydrolyzable NH₄ ⁺-N, amino sugar N, and amino acid N) or alkaline (ISNT-N) hydrolysis. Sugarcane varied widely in response to N fertilization, indicating that yield-based recommendations would often under- or overestimate N requirement and thus adversely impact sustainability of sugarcane-based ethanol production. In studies to evaluate feasibility of soil N testing to improve fertilizer N recommendations, mineral N production upon aerobic incubation was accompanied by significant decreases in hydrolyzable NH₄ ⁺-N and ISNT-N, indicating that both fractions were liberating mineralizable forms of soil N. Test values by the ISNT and DSD were highly correlated, and both showed promise for differentiating soil responsiveness to fertilizer N.     

The dynamics of soil-soluble nitrogen and soil-retained nitrogen in greenhouse soil

Field experiments were conducted to determine the effects of nitrogen (N) fertilization and manure addition on the soil-soluble nitrogen (SSN) (soil mineral N (SMN); soil-soluble organic N (SSON)) and soil-retained N (SRN) (soil fixed ammonium; soil microbial biomass N). The combined application of manure and inorganic N (different N fertilizer rates: M3N0, M3N1, M3N2, and M3N3; different manure rates: M0N2, M1N2, M2N2, and M3N2) was used in a greenhouse fertilization experiment. SSN and SRN increased with increasing N rate up to M3N2. SSON decreased with increasing manure rate and was the highest in the M1N2, whereas SMN and SRN were the highest in the M3N2, and increased with increasing manure rate on all sampling dates. Both SSN and SRN declined significantly with increasing soil depth in the different application rates of manure (p < .05). Moreover, the SSN and SRN significantly varied with plant growth and followed a different pattern during the growing season. SSN and FA peaked in the first ear fruit period, but SMBN was at its highest level in the second ear fruit period. There was a significant positive relationship (p < .05) between SSN and SRN throughout the plant growing season, and the annual apparent loss of N in the M3N3 was the highest. The combined application of inorganic N fertilizer and manure at an appropriate rate may be an effective strategy for maintaining the long-term health of greenhouses.     

旱地土壤氮素矿化参数与氮素形态的关系

应用间歇淋洗培养方法 ,以长期不同培肥定位试验土壤为研究对象 ,求得土壤氮素矿化参数 ,并探讨氮素矿化潜势 (N0)、碱解氮、微生物氮、可浸提易矿化氮、全氮之间的关系。结果表明 ,在 35℃和 20℃条件下培养 ,一级动力学模型能够很好的拟合试验数据 ,模拟方程和模拟参数均达到极显著水平。经过 15年的培肥和轮作 ,无论是单施氮肥区 ,还是氮肥与有机肥配合施用区 ,N0均有不同程度的增加 ,这标志着土壤活性有机氮库增加。k值变化范围在0.004628～0.013148d-1之间 ,说明可矿化氮以每天 0.46 %～1.31%的平均速率矿化释放。而且 ,在本试验条件下 ,淋洗液中均含有一定数量的可溶性有机态N ,因此进行氮素矿化研究时 ,同时测定NH4-N、NO3-N和Norg的含量是必要的。 35℃下 ,N0 占全氮的比例为 7.23%～17.36% ,变异系数30.4% ;易矿化有机态氮占全氮的比例为0.27%～0.48% ,变异系数 200% ;碱解氮占全氮的比例为 5.55%～6.54% ,变异系数仅 5.8% ;微生物氮占全氮的比例在 2.16%～5.18%之间 ,变异系数28.8%。从几种指标测得的平均值看 ,N0碱解氮 微生物氮 易矿化氮 ,而变异系数是N0微生物氮 易矿化氮 碱解氮。虽然N0的绝对值远高于田间实际矿化量 ,