土壤干燥过程对土壤易矿化有机态氮的影响

通过室内模拟培养的方法研究了土壤干燥过程对土壤氮素组分尤其是土壤易矿化有机态氮的影响。结果表明 ,随着干燥温度的升高 ,土壤铵态氮的数量有所增加 ,而对土壤硝态氮的数量影响差异不显著 ,但土壤易矿化有机态氮的数量则有增加的趋势。其中 105℃干燥处理后的土壤易矿化有机态氮的数量明显高于鲜土、风干和 4 0℃干燥处理的土样。进一步分析结果看出 ,105℃处理后的土壤易矿化有机态氮除了部分来自土壤微生物态氮的降解产物之外 ,还有一部分是靠高温将土壤本身大分子含氮化合物分解而产生的     

粘土矿物对蛋白质氮矿化的影响

本试验以粘粒(蒙脱)和蛋白质(明胶)为基本材料,较详细地研究了粘土矿物对蛋白质氮矿化的影响。指出:1.蛋白质与粘粒所处的状态不同,能导致蛋白质氮分解率的不同,其中复合物中的蛋白质氮分解率小于混合物,而后者又小于纯蛋白质氮;2.对于复合物或混合物来说,蛋白质在其中的比例越大其分解率就越大,而纯白质氮则相反,3.蛋白质-粘粒中的氮或纯蛋白质氮在土壤中的分解率小于在石英砂基质上的分解率,即土壤具有保护蛋白质氮免遭微生物分解的作用,不同土壤的这种保护作用不一样,主要是由于不同土壤粘土矿物的不同所致。     

酸雨对土壤有机碳氮潜在矿化的影响

Acid rain is a serious environmental problem worldwide. In this study, a pot experiment using forest soils planted with the seedlings of four woody species was performed with weekly treatments of pH 4.40, 4.00, 3.52, and 3.05 simulated acid rain （SAR） for 42 months compared to a control ofpH 5.00 lake water. The cumulative amounts of C and N mineralization in the five treated soils were determined after incubation at 25 ℃ for 65 d to examine the effects of SAR treatments. For all five treatments, cumulative CO2-C production ranged from 20.24 to 27.81 mg kg^-1 dry soil, net production of available N from 17.37 to 48.95 mg kg^-1 dry soil, and net production of NO3-N from 9.09 to 46.23 mg kg^-1 dry soil. SAR treatments generally enhanced the emission of CO2-C from the soils; however, SAR with pH 3.05 inhibited the emission. SAR treatments decreased the net production of available N and NO3-N. The cumulative CH4 and N2O productions from the soils increased with increasing amount of simulated acid rain. The cumulative CO2-C production and the net production of available N of the soil under Acmena acuminatissima were significantly higher （P 〈 0.05） than those under Schima superba and Cryptocarya concinna. The mineralization of soil organic C was related to the contents of soil organic C and N, but was not related to soil pH. However, the overall effect of acid rain on the storage of soil organic matter and the cycling of important nutrients depended on the amount of acid deposition and the types of forests.     

地膜覆盖对黄土高原旱作春玉米田土壤碳氮组分的影响

基于2年田间试验,研究了地膜覆盖对旱作春玉米田土壤有机碳、全氮及其组分的影响,试验包括地膜覆盖玉米田、无覆盖玉米田和裸地休闲3个处理,分层测定了0—40cm土层有机碳、全氮、颗粒有机碳氮、潜在矿化碳氮和微生物量碳氮含量。结果表明:在0—40cm土层,各处理间土壤有机碳和全氮含量均无显著差异。与不覆盖相比,地膜覆盖处理0—40cm土层颗粒有机碳氮及其所占比例分别降低了29.0%,33.3%,29.9%,35.7%;0—10cm土层潜在可矿化碳及其所占比例分别降低了17.8%和16.1%,潜在可矿化氮和微生物量碳及其所占比例无显著差异,但在0—10cm土层地膜覆盖微生物量氮含量及其所占比例分别较不覆盖处理提高了10.6%和10.5%(p0.05)。与裸地休闲相比,无覆盖处理0—40cm土层潜在可矿化碳氮分别提高了12.8%和14.7%,地膜覆盖处理则分别提高了7.8%和6.5%(p0.05),但种植玉米降低了微生物量碳氮含量及其所占比例。在0—40cm土层覆盖与否对潜在可矿化碳氮和微生物量碳氮影响不显著。总体来看,地膜覆盖能够在一定程度上提高表土微生物量氮组分及其所占比例,但显著降低了中活性碳氮组分含量及其比例,不利于长期的土壤碳氮固定。     

施用秸秆对土壤可溶性有机碳氮及矿质氮的影响

为了研究施用秸秆对土壤可溶性有机碳氮及矿质态氮含量的影响,设置CK（对照）,M₂,M₄,M₆共4个处理,处理中每100 g干土中加入秸秆量分别为0,2,4,6 g。在室温为25℃、土壤含水量为田间持水量的70%的条件下进行培养试验,分别在15,30,45,60,105,150 d时,采取各处理中的土壤样品,观测土壤可溶性有机碳氮及矿质氮的动态变化。结果表明:4个处理的土壤可溶性有机碳、氮具有相同的变化趋势,表现为随着培养时间的推移,先增加,再减小,然后经过一段时间的波动后趋于平稳。在培养的整个过程中,M₄与M₆处理的土壤可溶性有机碳、氮明显高于CK中的含量,表明了施用秸秆可以促进土壤可溶性有机碳氮的累积。在相同时间段内,各处理之间铵态氮含量无明显差异,与对照相比,加入秸秆后,土壤中硝态氮的含量明显下降。     

有机碳氮添加对酸性森林土壤氨氧化过程的影响

以亚热带酸性森林土壤为研究对象,开展了微宇宙室内培养实验,设置了有机碳和有机氮添加处理,分析了土壤硝化活性和氨氧化古菌(Ammonia-oxidizing archaea,AOA)、氨氧化细菌(Ammonia-oxidizing bacteria,AOB)的功能基因丰度,研究了外源有机碳和有机氮对酸性森林土壤氨氧化过程的影响规律。结果表明:外源有机氮添加显著刺激了酸性森林土壤硝化活性,乙炔抑制实验表明自养氨氧化对酸性森林土壤硝化过程的贡献率90%。有机碳添加对土壤硝化活性未有显著影响,同时添加有机碳和无机铵态氮也未显著提高土壤硝化活性,而外源有机氮添加提高了土壤矿化速率并导致土壤NH3浓度升高,可能是土壤硝化活性、AOA和AOB数量显著增加的主要原因。     

不同碳氮比有机肥对有机农业土壤微生物生物量的影响

有机肥能提高土壤微生物活性, 改善土壤品质。碳氮比是影响有机肥肥效的重要因素。本试验以无肥处理为对照(CK), 设置4个有机肥碳氮比处理(20︰1、15︰1、10︰1、5︰1), 在温室中进行茄子盆栽试验, 定期采集土壤样品, 用熏蒸提取法测定土壤微生物生物量碳(SMBC)、氮(SMBN), 研究等氮条件下不同碳氮比有机肥料对土壤生物活性的影响。试验结果表明, 不同碳氮比的有机肥均能提高土壤的SMBC和SMBN含量, 具体表现为SMBC: 20︰1>10︰1≈15︰1>5︰1>CK, SMBN: 15︰1>10︰1>20︰1>5︰1>CK。SMBC/SMBN的比率反映土壤氮素生物活性, 其值越低, 生物活性越大, 氮素损失越少, 本试验SMBC/SMBN表现为: 15︰1<10︰1<20︰1≈5︰1相似文献   

土壤水分和氮添加对3种质地紫色土氮矿化及土壤pH的影响

为正确认识土壤水分、质地和外源氮添加对紫色土氮矿化作用和土壤pH的影响,以西南地区典型的紫色土为研究对象,通过90d的室内恒温(25℃)好气培养,研究了3种质地(粘土、粉粘壤土和砂土)紫色土在不同含水量(55%,65%和75%田间持水量)和尿素氮添加水平(0mg/kg土和250mg/kg土.)条件下,土壤氮矿化作用和pH的变化。结果表明:前30d的累积矿化氮量可占培养期间(90d)的78.48%~91.55%,且各处理的土壤累积矿化氮量和净矿化速率均随着培养时间的延长而快速增加;第30~90d,土壤累积矿化氮量增长缓慢,净矿化速率迅速下降并趋于稳定。土壤累积矿化氮量和净矿化速率在各培养阶段均随土壤水分含量的增加而逐渐增大,其中75%WHC(75%田间持水量)和75%WHC+U(75%田间持水量+尿素)处理的矿化作用最强。土壤质地从一定程度上对土壤的矿化产生影响,但其影响并不显著。外源氮添加能促进土壤氮矿化,其净氮矿化量和净矿化速率在各培养阶段均极显著(p0.01)高于未加氮处理,分别为未施氮处理的1.68~4.56倍,0.60~6.47倍。外源氮添加使土壤pH显著下降,55%WHC+U、65%WHC+U和75%WHC+U处理分别下降了0.57,0.66,0.72个pH单位,土壤有酸化趋势。土壤pH值与土壤氮素净矿化速率呈极显著线性相关,净矿化速率对pH变化贡献巨大。总之,土壤含水量增加和外源氮添加均促进了土壤氮矿化,增加了土壤矿质氮含量,同时外源氮添加也加速了土壤pH下降,土壤有酸化趋势。     

美国有关放牧对土壤性质影响的研究

在连续放牧 10a的两种土壤上测定了放牧率对土壤有机碳和氮含量的影响。试验分 4种轮牧处理方式 :处理Ⅰ为轻度放牧 ,处理Ⅱ为中度放牧 ,处理Ⅲ为过度放牧 ,处理Ⅳ为不放牧。研究区土壤类型分别为Durant壤土和Teller粉沙壤土。在所有处理中 ,Durant土 0～ 6 0cm土层中有机碳含量平均为 95 7t hm2 ,Teller土平均为 5 6 7t hm2 。Durant土在放牧处理情况下 ,土壤有机碳含量随放牧率的增加而降低 ,不放牧处理土壤有机碳含量最高。在Teller土上 ,在所有放牧处理中土壤有机碳含量没有大的变化 ,不放牧处理相对较小。土壤全氮含量与有机碳的变化趋势相同。从土壤的特性可以确定放牧地的固碳潜力。     

固定态铵的含量及中国某些耕地土壤NH4+的固定能力

Fixed ammonium contents and NH4^ fixation capacities of some representative cultivated solis collected from 16 provinces of China were studied.Results showed that the contents of fixed ammonium in soils ranged from 35 to 573 mg N kg^-1,with an average of 198mg Nkg^-1.The content of fixed ammonium correlated very significantly with mica content for tropical and subtropical soils,whereas this was not the case for soils in the temperate zone.At the end of K-exhausting experiment the fixed ammonium content increased in most soils studied.However,it decreased in smom temperate soils.Generally,fixation of added NH4^ could not be found either before or after K-exhausting experiment for highly weathered soils,including tropical soils and soils derived from granite-gneiss or Quaternary red clays in the subtropic zone,while for most soils in the Yangtze River dalta the NH4^ fixation capacity was rather high and increased significantly in the K-exhausted soils.     

冬小麦生长期土壤固定态铵与微生物氮的动态研究

田间试验研究冬小麦生长期土壤固定态铵和微生物N动态变化结果表明 ,施入基肥后土壤固定态铵显著上升 ,春季后固定态铵显著下降 ,至扬花期降至最低点。作物生长后期随吸N量的降低 ,各施肥处理固定态铵含量约升至播前水平。冬小麦全生育期土壤微生物N呈明显季节变化 ,施基肥后短期内有所升高 ,且春季施肥后出现第 2次升高 ,至扬花期土壤微生物N降至最低点 ,至生长后期重新回升。     

NH4+对K+在土壤肥际微域中迁移和转化的影响

NH4^＋和K^＋共施在农田施肥中是很普遍的现象,研究它们共施后二者在土壤中的交互作用对指导施肥具有重要意义。采用室内土柱实验研究了共施条件下NH4^＋对K^＋在红壤和潮土肥际微域中的迁移和形态转化的影响,供试肥料为NH4Cl和KCl。试验结果表明,与单施K^＋相比,共施NH4^＋没有改变肥料钾在红壤和潮土中的迁移距离,但提高了肥际微域中的水溶性钾含量;在靠近施肥点附近,NH4^＋的施用减少了土壤交换性钾含量,这种作用在潮土中的表现不如在红壤中明显;与单施KCl相比,共施NH4Cl明显降低了施肥点附近土壤微域内的非交换性钾含量。研究结果表明,共施NH4Cl减少了土壤晶格对钾离子的固定,增加了钾的淋溶风险。     

水稻根系生长对不同氮形态响应的动态变化

土壤养分供应变异很大,植物根系生长对这种养分变异的响应非常敏感.为了探索水稻根系生长对N素供应响应的动态变化规律以及这种适应性变化与水稻N效率之间的关系,采用水培方法,以两个苗期不同N效率水稻品种桂单4号和南光为研究材料,比较了不同铵硝比、不同浓度NH4、不同浓度NO3-和不同浓度NH4NO3对水稻根系构型参数的影响.结果表明:NH4 和NH4NO3供应显著降低了总根长、总根表面积和总根体积,且有增加平均根直径的趋势;而NO3-供应在0～1 mmol/L浓度范围内,增加了总根长、总根表面积和总根体积,降低了平均根直径,但当NO3-供应超过1 mmo1/L后,NO3-却有降低总根长、总根表面积和总根体积的趋势,对平均根直径没有明显影响.苗期N高效基因型桂单4号总根长和总根表面积在各种N素营养条件下均显著高于N低效基因型南光.上述结果表明,NH4 和NH4NO3都抑制了水稻根系生长,而NO3-为低浓度诱导、高浓度抑制根系生长,根长和根表面积,对提高水稻N效率贡献较大.     

不同水稻品种对铵态氮和硝态氮吸收特性的研究

采用水培方法研究了不同形态氮素对武育粳 3号 (常规粳稻 )和扬稻 6号 (常规籼稻 )生长的影响及其水稻苗期对NH 4 N和NO-3 N的吸收动力学特征。结果表明 :不同形态氮素对水稻生长影响差异显著 ,铵硝混合营养下水稻的生长最优 ;扬稻 6号比武育粳 3号具有更强的氮素吸收能力 ;不论武育粳 3号或是扬稻 6号 ,单一氮源时NO-3 的Km 值均大于NH 4 ,说明水稻对NH 4 的亲和力大于NO-3 ,武育粳 3号对NH 4 的最大吸收速率小于NO-3 ,而扬稻 6号则极为接近 ;NH 4 的存在均显著降低两个水稻品种对NO-3的吸收速率 ,武育粳 3号和扬稻 6号的NO-3 的Vmax分别比单一硝营养减小 1/ 2和 2 / 3,NO-3 的存在不影响武育粳 3号对NH 4 的吸收速率 ,但使扬稻 6号对NH 4 的吸收速率减小     

外源蔗糖对高NH4+胁迫下拟南芥碳氮代谢的影响

以拟南芥野生型、amt1.1和amt1.3为实验材料，采取土培的方法，以正常培养液（4mmol/L NH4+）培养，在20mmol/L NH4+的胁迫下，通过在培养液中添加0%（T1）蔗糖、5%（T2）蔗糖，测定地上部分的鲜重，叶绿素，游离NH4+，可溶性糖，可溶性蛋白，谷氨酰胺合成酶（GS）、谷氨酸脱氢酶（GDH），矿质元素含量等指标，研究外源蔗糖对NH4+胁迫拟南芥碳氮代谢的影响。结果表明，T1处理下，拟南芥生长受到严重的抑制，鲜重，GS，GDH酶活性降低，游离NH4+含量，叶绿素含量，可溶性糖和可溶性蛋白含量增加，植株的N、P、K、Ca的含量增加，Mg、Fe的含量减少。其中col-0在T1处理下受到的抑制比amt1.1和amt1.3更为显著。与T1处理相比较，T2处理增加了拟南芥植株的鲜重，显著提高了可溶性糖和可溶性蛋白含量，提高了GS和GDH的活性；降低了叶绿素和游离NH4+的含量，提高了植株体内的N、P、K、Ca，Mg的含量，降低了植株Fe的含量，其中，外源蔗糖对col-0高NH4+毒害的缓解更为显著。     

定期淹水强碱性盐渍土中14C标记葡萄糖和NH4+的动态

Flooding an extremely alkaline（pH 10.6） saline soil of the former Lake Texcoco to reduce salinity will affect the soil carbon（C）and nitrogen（N） dynamics.A laboratory incubation experiment was done to investigate how decreasing soil salt content affected dynamics of C and N in an extremely alkaline saline soil.Sieved soil with electrical conductivity（EC） of 59.2 dS m^-1 was packed in columns,and then flooded with tap water,drained freely and conditioned aerobically at 50%water holding capacity for a month.This process of flooding-drainage-conditioning was repeated eight times.The original soil and the soil that had undergone one,two,four and eight flooding-drainage-conditioning cycles were amended with 1000 mg glucose-¹⁴C kg^-1 soil and 200 mg NH₄⁺-N kg^-1soil,and then incubated for 28 d.The CO₂ emissions,soil microbial biomass,and soil ammonium（NE₄⁺）,nitrite（NO₂^-） and nitrate（NO₃^-） were monitored in the aerobic incubation of 28 d.The soil EC decreased from 59.2 to 1.0 dS m_¹ after eight floodings,and soil pH decreased from 10.6 to 9.6.Of the added ¹⁴C-labelled glucose,only 8%was mineralized in the original soil,while 24%in the soil flooded eight times during the 28-d incubation.The priming effect was on average 278 mg C kg^-1 soil after the 28-d incubation.Soil microbial biomass C(mean 66 mg C kg^-1 soil) did not change with flooding times in the unamended soil,and increased 1.4 times in the glucose-NH₄⁺-amended soil.Ammonium immobilization and NO₂^- concentration in the aerobically incubated soil decreased with increasing flooding times,while NO₃^- concentration increased.It was found that flooding the Texcoco soil decreased the EC sharply,increased mineralization of glucose,stimulated nitrification,and reduced immobilization of inorganic N,but did not affect soil microbial biomass C.     

不同液土比和温度条件下塿土铵离子吸附

Effects of NH₄⁺ concentration, solution/soil ratio and temperature on NH₄⁺ adsorption were studied in a Eum-Orthic Anthrosol. The slopes of the soil NH₄⁺ adsorption isotherms and the fitted n, the coefficient for the adsorption intensity, and k, the coefficient related to adsorption capacity, of the Freundlich equation increased with increasing solution/soil ratio (SSR) and with decreasing temperature (T). For the range of experimental conditions, the value of ∂q/∂c, the rate of change of the amount of NH₄⁺ adsorbed in the soil solid phase (q) with respect to the equilibrium concentration of NH₄⁺ in soil solution (c), was 0.840, indicating that q increased with increasing c. From 2 to 45 ℃, ∂q/∂SSR, the rate of change of q with respect to SSR, decreased from 2.598 to 1.996, showing that q increased with increasing SSR, while its increasing rate decreased with temperature. From SSR 1:1 to 20:1, ∂q/∂T, the rate of change of q with respect to T, decreased from -0.095 to -0.361, indicating that q decreased with increasing temperature, and at the same time the negative effect of temperature became larger as SSR increased. Thus under the experimental conditions the order of importance in determining the amount of NH₄⁺ adsorbed in the soil solid phase was ∂q/∂SSR > ∂q/∂c > |∂q/∂T|, indicating that the greatest effect on the amount of NH₄⁺ adsorbed was with the solution/soil ratio; the equilibrium concentration of NH₄⁺ had a lesser effect; and temperature had the least effect.     

铁铝氢氧化物对两种土壤和高岭石表面K+和NH4+解吸的影响

Potassium (K) and nitrogen (N) are essential nutrients for plants. Adsorption and desorption in soils affect K+ and NH + 4 availabilities to plants and can be affected by the interaction between the electrical double layers on oppositely charged particles because the interaction can decrease the surface charge density of the particles by neutralization of positive and negative charges. We studied the effect of iron (Fe)/aluminum (Al) hydroxides on desorption of K+ and NH + 4 from soils and kaolinite and proposed desorption mechanisms based on the overlapping of diffuse layers between negatively charged soils and mineral particles and the positively charged Fe/Al hydroxide particles. Our results indicated that the overlapping of diffuse layers of electrical double layers between positively charged Fe/Al hydroxides, as amorphous Al(OH) 3 or Fe(OH) 3 , and negatively charged surfaces from an Ultisol, an Alfisol, and a kaolinite standard caused the effective negative surface charge density on the soils and kaolinite to become less negative. Thus the adsorption affinity of these negatively charged surfaces for K+ and NH + 4 declined as a result of the incorporation of the Fe/Al hydroxides. Consequently, the release of exchangeable K+ and NH +4 from the surfaces of the soils and kaolinite increased with the amount of the Fe/Al hydroxides added. The greater the positive charge on the surfaces of Fe/Al hydroxides, the stronger was the interactive effect between the hydroxides and soils or kaolinite, and thus the more release of K+ and NH + 4 . A decrease in pH led to increased positive surface charge on the Fe/Al hydroxides and enhanced interactive effects between the hydroxides and soils/kaolinite. As a result, more K+ and NH + 4 were desorbed from the soils and kaolinite. This study suggests that the interaction between oppositely charged particles of variable charge soils can enhance the mobility of K+ and NH + 4 in the soils and thus increase their leaching loss.     

黄绵土与淋溶土含水量与施肥方法对铵固定和肥料氮回收率的影响

Ammonium fixation and the effects of soil moisture and application methods on fertilizer N recovery were investigatedin two soils of Shaanxi Province, China, a Luvisol and an Entisol, through two experiments performed in the laboratoryand in a glass shelter, respectively, by using ammonium bicarbonate (NH4HCO3). The laboratory closed incubationbox experiment was conducted using the Luvisol to study NH fixation rate at soil moisture levels of 10.1%, 22.7% and 35.3% water filled pore space (WFPS). The fixed NH -N increased dramatically to 51% and 66%, 67% and 74%,and 82% and 85% 1, 2 and 36 h after fertilizer incorporation at moisture levels of 10.1% and 22.7% WFPS and 35.3% WFPS, respectively. The rapid NH fixation rates at all moisture levels could help prevent NH losses from ammonia volatilization. In the glass shelter pot experiment, N fertilizer was applied by either banding (in a concentrated strip)or incorporating (thoroughly mixing) with the Entisol and the Luvisol. An average of 74.2% of the added N fertilizerwas recovered 26 days after application to the Luvisol, while only 61.4% could be recovered from the Entisol, due tohigher NH fixation capacity of the Luvisol. The amount of fixed NH decreased with increasing WFPS. The amountof fixed NH in the incorporated fertilizer treatment was, oll average, 10% higher than that in the banded treatment.Higher NH fixation rates could prevent N loss and thus increase N recovery. The results from the Luvisol showed lowernitrogen recovery as soil moisture level increased, which could be explained by the fact that most of the fixed NH wasstill not released when the soil moisture level was low. When the fertilizer was incorporated into the soil, the recovery ofN increased, compared with the banded treatment, by an average of 26.2% in the Luvisol and 11.2% in the Entisol, whichimplied that when farmers applied fertilizer, it would be best to mix it well with the soil.