甲硫氨基酸对亚热带森林土壤硝化作用和N2O排放的影响

为探讨甲硫氨基酸对亚热带红壤硝化作用和N₂O排放的影响,选择福建省建瓯市万木林保护区的山地红壤为研究对象,在土壤饱和持水量(WHC)60%和90%的条件下,开展室内培养试验.试验分为对照(CK)、添加甲硫氨基酸(M)、甲硫氨基酸和硫酸铵(MA)、甲硫氨基酸和亚硝酸钠(MN)、甲硫氨基酸和葡萄糖(MC)5个处理.结果表明: 与对照相比,M处理使土壤NH₄⁺-N平均含量显著提高0.8%～61.3%,而NO₃^--N含量显著降低13.2%～40.7%;60%WHC条件下,MC处理土壤NO₂^--N含量高于M处理,MA、MN处理NO₃^--N含量高于M处理,且MN处理高于MA处理,M处理于试验后期最低,表明甲硫氨基酸抑制了硝化作用的亚硝化过程.碳添加处理使甲硫氨基酸在一定程度上降低NH₄⁺-N含量,抑制了土壤自养硝化,并且甲硫氨基酸和碳源共同作用下NO₃^--N含量变化与土壤水分条件有关,在90%WHC条件下,碳加入后反硝化作用更明显;而NO₃^--N含量降低不足以表明是异养硝化受到抑制所致.甲硫氨基酸在一定程度上促进土壤N₂O的释放,90%WHC条件下较60%WHC条件下释放量更大,且葡萄糖添加的促进效果更明显.     

甲硫氨基酸对亚热带森林土壤硝化作用和N2O排放的影响

为探讨甲硫氨基酸对亚热带红壤硝化作用和N₂O排放的影响,选择福建省建瓯市万木林保护区的山地红壤为研究对象,在土壤饱和持水量(WHC)60%和90%的条件下,开展室内培养试验.试验分为对照(CK)、添加甲硫氨基酸(M)、甲硫氨基酸和硫酸铵(MA)、甲硫氨基酸和亚硝酸钠(MN)、甲硫氨基酸和葡萄糖(MC)5个处理.结果表明: 与对照相比,M处理使土壤NH₄⁺-N平均含量显著提高0.8%～61.3%,而NO₃^--N含量显著降低13.2%～40.7%;60%WHC条件下,MC处理土壤NO₂^--N含量高于M处理,MA、MN处理NO₃^--N含量高于M处理,且MN处理高于MA处理,M处理于试验后期最低,表明甲硫氨基酸抑制了硝化作用的亚硝化过程.碳添加处理使甲硫氨基酸在一定程度上降低NH₄⁺-N含量,抑制了土壤自养硝化,并且甲硫氨基酸和碳源共同作用下NO₃^--N含量变化与土壤水分条件有关,在90%WHC条件下,碳加入后反硝化作用更明显;而NO₃^--N含量降低不足以表明是异养硝化受到抑制所致.甲硫氨基酸在一定程度上促进土壤N₂O的释放,90%WHC条件下较60%WHC条件下释放量更大,且葡萄糖添加的促进效果更明显.     

氮素类型和剂量对寒温带针叶林土壤N2O排放的影响

大气氮沉降输入会增加森林生态系统氮素有效性,进而改变土壤N_2O产生与排放,然而有关不同氮素离子(氧化态NO_3~--N与还原态NH_4~+-N)沉降对土壤N_2O排放的影响知之甚少。以大兴安岭寒温带针叶林为研究对象,构建了3种类型(NH_4Cl、KNO_3、NH_4NO_3)和4个施氮水平(0、10、20、40 kg N hm~(-2)a~(-1))的增氮控制试验,利用流动化学分析仪和静态箱-气相色谱法4次/月测定凋落物层和矿质层土壤无机氮含量、土壤-大气界面N_2O净交换通量以及相关环境因子,分析施氮类型和剂量对土壤氮素有效性、土壤N_2O通量的影响探讨氮素富集条件下土壤N_2O通量的环境驱动机制。结果表明:施氮类型和剂量均显著影响土壤无机氮含量,土壤NH_4~+-N的积累效应显著高于NO_3~--N。施氮一致增加寒温带针叶林土壤N_2O排放,NH_4NO_3促进效应最为明显,增幅为442%-677%,高于全球平均水平(134%)。土壤N_2O通量与土壤温度、凋落物层NH_4~+-N含量正相关,且随着施氮水平增加而增加。结果表明大气氮沉降短期内不会导致寒温带针叶林土壤NO_3~--N大量流失,但会显著促进土壤N_2O的排放。此外,外源性NH_4~+和NO_3~-输入对土壤N_2O排放的促进作用具有协同效应,在未来森林生态系统氮循环和氮平衡研究中应该区分对待。     

水分状况与不同形态氮添加对亚热带森林土壤氮素净转化速率及N2O排放的影响

通过室内模拟试验,研究40%、70%和110%土壤饱和持水量(WHC)下,不同形态氮(硝态氮和铵态氮)添加对亚热带森林红壤氮素转化的影响.结果表明:70%WHC下土壤净矿化和氨化速率最高,40%WHC下最低;与对照相比,70%WHC下添加硝态氮使土壤净矿化和氨化速率分别降低56.1%和43.0%,110%WHC下分别降低68.2%和19.0%,但提高了氨化速率占矿化速率的比例,表明添加硝态氮抑制了硝化.110%WHC下,添加硝态氮后,土壤净硝化速率最低,但氧化亚氮(N2O)浓度最高,最大值出现在第3~7天,表明N2O产生自反硝化途径,硝态氮也在同时段降低;而40%WHC和70%WHC下,N2O浓度在培养初期最大,即使在铵态氮和硝态氮添加处理下,试验后期N2O浓度也没有显著变化,表明自氧硝化是试验前期N2O产生的主要途径.40%WHC下,土壤可溶性有机碳含量增加最多,且在铵态氮添加处理下增加最多,可见添加铵态氮促进土壤有机质矿化,增加可溶性有机碳,但是土壤水分含量增多不利于有机质矿化.在40%WHC和110%WHC下,铵态氮添加处理土壤可溶性有机氮(SON)变化速率分别显著高于对照73.6%和176.6%,而在硝态氮添加处理下,只有40%WHC下显著高于对照78.7%,表明高水分条件和添加铵态氮有利于SON的形成.     

凋落物中水溶性有机物和残渣对亚热带森林土壤氮素转化的影响

设置60%和90%WHC两种土壤水分条件,并添加凋落物过滤液、剩余残渣和丙氨酸,进行为期36 d的室内培养(25 ℃),研究了凋落物中水溶性有机物和残渣对土壤氮素转化的影响.结果表明: 在60%和90%WHC条件下,丙氨酸在土壤中迅速矿化,该处理的土壤铵态氮(NH₄⁺-N)含量分别比对照显著提高5.4%～44.7%和16.1%～41.3%,净氮矿化和氨化速率在培养前期也高于对照,而凋落物过滤液和残渣添加处理则降低了土壤NH₄⁺-N含量,且残渣的降幅大于过滤液.试验期间,土壤硝态氮(NO₃^--N)含量呈直线增长趋势,培养结束时60%WHC条件下NO₃^--N含量显著高于90%WHC.土壤水分含量增多不利于土壤有机质的矿化;90%WHC条件下可溶性有机碳(SOC)含量明显低于60%WHC,而土壤氧化亚氮(N₂O)排放量比60%WHC提高1.5～63.0倍,且在60%WHC条件下凋落物残渣添加处理显著促进了土壤N₂O的排放.凋落物在分解过程中的可溶性物质和剩余物对土壤氮的影响存在差异,且这种差异随分解而发生动态变化.     

增温和CO2浓度加倍对川西亚高山针叶林土壤可溶性氮的影响

采用全自动微气候控制的"人工模拟气候实验系统"研究了增温和CO2浓度加倍对川西亚高山针叶林土壤硝态氮(NO_3~--N)、铵态氮(NH_4~+-N)、游离氨基酸(FAA)、可溶性有机氮(DON)和可溶性总氮(TSN)的影响。结果表明:1在种植油松苗木组,增温处理显著降低了土壤NO_3~--N含量,不同处理0—15 cm土层NO_3~--N含量均显著小于15—30 cm层;而在未种树组,增温处理显著增加了土壤NO_3~--N含量,0—15 cm土层NO_3~--N含量显著高于15—30 cm层,这表明增温促进了油松苗对NO_3~--N的吸收。2在种植油松苗木组,增温(ET)、增CO_2(EC)及两者的共同作用(ETC)均显著增加了土壤NH_4~+-N、DON和TSN含量;在未种树组,ET显著增加了土壤NH_4~+-N、FAA、DON和TSN含量,EC和ETC对NH_4~+、FAA、DON和TSN含量具有微弱影响或没有显著影响。不同处理0—15cm层土壤NH_4~+-N、FAA、DON和TSN的含量显著大于15—30 cm层。3种植油松苗木组土壤NO_3~--N、NH_4~+-N、FAA、DON和TSN含量均显著低于未种树组,这是由植物对氮素的吸收消耗造成的。研究结果表明,EC、ETC主要通过植物根系作用促进了NH_4~+-N、DON和TSN含量增加,而ET处理通过影响土壤微生物和植物根系来促进NH_4~+-N、FAA、DON和TSN含量的增加。     

城乡交错带土壤氮素空间分布及其影响因素

城乡交错带土壤氮素是城乡生态系统中最重要的氮源与氮汇,但是城市化下的土壤氮素分布及其影响机制还不清楚,基于3S平台研究了土壤氮素在成都西郊城乡交错带的空间分布特征及城市化对土壤氮素的影响。结果表明,研究区内土壤全氮(STN)、硝态氮(NO_3~--N)和铵态氮(NH_4~+-N)含量均值分别为(1.46±0.06)g/kg、(50.04±3.59)mg/kg和(6.72±0.53)mg/kg。区内土壤氮素含量从近郊向远郊逐渐增高,STN和NO_3~--N含量为中部高于南北部,NH_4~+-N含量则由西北部和东南部向中部递增。方差分析表明,区内不同土地利用方式下STN、NO_3~--N和NH_4~+-N含量差异显著(P0.05)。回归分析显示STN含量与建筑密度(BD)、道路密度(RD)均呈现显著线性负相关(P0.05),NO_3~--N含量与道路密度呈极显著线性负相关(P=0.001),与建筑密度关系不明显(P=0.217)。土壤NH_4~+-N与建筑密度呈显著负线性相关(P=0.001),与道路密度呈显著指数相关关系(P=0.021)。研究结果显示城市发展使得城乡交错带土壤氮素含量降低,这种影响伴随着建筑面积的增加,道路长度的增加而加强。     

不同氮素形态及其配比对盐胁迫下紫苏生理特性的影响

以60 mmol·L~(-1)NaCl处理紫苏幼苗为对象,研究不同氮素形态配比对盐胁迫下紫苏生长、叶绿素含量、可溶性蛋白质、抗氧化酶和氮素代谢相关酶活性的影响,为进一步研究盐胁迫环境下紫苏生产中氮肥的合理调控提供理论依据。结果表明:非盐胁迫下,当NH_4~+-N/NO_3~--N=25∶75时,紫苏地上部分的鲜重和干重、总叶绿素含量、硝酸还原酶(NR)和谷氨酰胺合成酶(GS)活性、可溶性蛋白含量和抗氧化酶活性都显著高于其他氮素处理;在盐胁迫下,紫苏生长受到抑制,叶绿素含量降低,可溶性蛋白和MDA含量增加,抗氧化酶活性升高,氮代谢相关酶NR和GS活性也升高; NaCl胁迫下,当NH_4~+-N/NO_3~--N=25∶75时,紫苏叶片的叶绿素含量、SOD活性、CAT活性和可溶性蛋白含量最高,MDA含量最低;当NH_4~+-N/NO_3~--N=50∶50时,POD活性最高;叶片中NR和GS活性都随着硝态氮比例的增加不断升高,并在NH_4~+-N/NO_3~--N=0∶100达到最大值,酰胺态氮处理组的NR和GS活性均低于全硝处理,但高于全铵处理组;不同氮素形态及配比对盐胁迫下紫苏叶绿素含量、氮素代谢和抗逆调节指标、产量影响显著;研究发现,在盐胁迫下,铵硝混合配施比单独施用全硝、全铵和酰胺态氮效果好,并且NH_4~+-N/NO_3~--N=25∶75处理更有利于维持抗氧化酶、氮代谢酶活性,缓解盐胁迫对紫苏幼苗生长的抑制,促进鲜重和干重的增加,从而维持较高的耐盐性。     

川西北高寒草地沙化过程中土壤氮素变化特征

草地沙化是我国最严重的环境问题之一,但关于草地沙化过程中氮素变化特征的研究报道多集中于干旱半干旱地区,而半湿润地区的相关报道还比较缺乏。通过野外调查,研究了川西北半湿润地区高寒沙质草地沙化过程中土壤氮素变化特征。结果表明,草地沙化对0—100cm土层土壤氮素具有显著影响,全氮、碱解氮、铵态氮(NH_4~+-N)、硝态氮(NO_3~--N)和微生物量氮(MBN)均呈现极显著下降的变化特征,极度沙化阶段较未沙化阶段分别减少了73.95%、77.72%、76.75%、79.77%和84.12%。其中,0—20cm土层变化最显著,全氮、碱解氮、NH_4~+-N、NO_3~--N和MBN含量分别减少了86.43%、83.52%、82.11%、88.82%和91.77%。随着土层深度增加,不同程度沙化草地土壤氮素含量及其变化量逐渐减少;草地沙化过程中,不同沙化阶段土壤氮素损失数量不尽相同,其中,以轻度沙化阶段氮素损失最严重,全氮、碱解氮、NH_4~+-N、NO-3-N和MBN含量分别降低了41.18%、35.17%、46.74%、43.46%和46.88%。草地沙化过程中,土壤全氮、碱解氮、NH_4~+-N、NO_3~--N和MBN含量与土壤粉粒、粘粒含量和植被群落盖度均呈极显著正相关特征,与土壤沙粒含量呈极显著负相关特征。研究区土壤氮素损失与风蚀选择性吹蚀土壤粉粒、粘粒及地表植物覆盖状况逐渐变差密切相关,因此该区域治沙的关键是采取措施降低风蚀对地表土壤吹蚀作用,提高沙化草地地表植被覆盖。同时,还应及时对沙化前期阶段及潜在沙化的草地进行生态治理,从而避免草地沙化继续恶化。     

Shewanella putrefaciens CN32对粘土附着态铵氮释放的影响

【目的】研究产胞外分泌物微生物Shewanella putrefaciens CN32对土壤中常见粘土矿物附着态NH_4~+的释放效果及影响机制。【方法】以吸附NH_4~+的蒙脱石、蛭石、伊蒙混层矿物和黑云母为对象,通过监测S. putrefaciens CN32作用下不同粘土释放的NH_4~+含量及过程,以及监测微生物量及释放的胞外聚合物(Extracellular Polymeric Substances,EPS)的含量变化,研究S. putrefaciens CN32作用下不同粘土矿物类型附着态NH_4~+释放的差异性。【结果】粘土矿物附着态NH_4~+含量从高到低依次为蒙脱石蛭石伊蒙混层矿物黑云母(黑云母NH_4~+吸附量极低,会在非生物作用下几乎完全释放),CN32作用下粘土附着态NH_4~+相对释放量依次为蒙脱石伊蒙混层矿物蛭石;然而,尽管CN32有效促进了粘土附着态NH_4~+释放,但释放的NH_4~+并未在溶液中大量累积,而是多被微生物同化吸收转化为生物有机氮(EPS为主)并吸附在粘土表面,且粘土对EPS的吸附能力表现为蒙脱石伊蒙混层矿物蛭石黑云母;由于粘土吸附NH_4~+及EPS都与矿物中的羟基(结构水或层间水)关系密切,推测EPS对矿物羟基的竞争吸附可能是CN32促进NH_4~+释放的重要原因之一。【结论】以上结果表明,产EPS微生物S. putrefaciens CN32能够促进各类粘土矿物的附着态NH_4~+释放,但释放的NH_4~+可以通过微生物作用转化为有机氮,从而在减少NH_4~+流失的同时增加土壤氮肥的生物可利用性,因此微生物在降低土壤氮肥流失、转化土壤氮肥污染过程中可能起到了重要作用,也揭示了深入系统地分析不同类型土壤(粘土类型不同)中粘土附着态NH_4~+在不同功能微生物作用下的迁移转化过程,是精准评估土壤氮肥施用效率及流失风险的前提之一。     

亚热带次级森林演替过程中模拟氮磷沉降对土壤微生物生物量及土壤养分的影响

氮（N）沉降深刻影响着森林生态系统的生物多样性、生产力和稳定性。亚热带地区森林土壤磷（P）的有效性较低,N沉降将更突显P的限制作用。N、P输入对亚热带次级森林土壤的影响是否依赖于森林演替阶段知之甚少。选取两种不同演替年龄阶段（年轻林：<40 a;老年林：>85 a）的亚热带常绿阔叶林,设置模拟N和/或P沉降（10 g m^-2 a^-1）4个处理（Ctrl、N、P、NP）,连续处理4.5年后采集表层、次表层和下底层（0-15、15-30、30-60 cm）土壤样品,综合分析了土壤微生物生物量碳（MBC）氮（MBN）和多种土壤养分含量。结果表明,MBC、MBN及土壤养分含量均随土壤深度增加而降低。N添加对两种演替阶段森林土壤中MBC和MBN均无显著影响。施P相关处理（P和NP）对年轻林表层土壤MBC和MBN无显著影响,但显著增加了老年林表层土壤MBC和MBN（P<0.05）,表明老年林可能比年轻林更易受P限制。N添加显著增加了两种演替森林表层土壤可溶性有机氮（DON）、氨态氮（NH₄⁺-N）和硝态氮（NO₃^--N）的含量（P<0.05）;P相关处理（P和NP）显著增加两种演替阶段表层和次表层土壤速效磷（AP）以及表层土壤全磷（TP）的含量（P<0.05）。土壤MBC和MBN与土壤中各养分指标（可溶性有机碳DOC、DON、NH₄⁺-N、NO₃^--N、AP、全碳TC、全氮TN和TP）呈显著正相关关系,土壤TC、TN和DOC是影响土壤微生物生物量的主要因子。研究可为评估和揭示未来全球环境变化背景下不同演替林龄亚热带森林的土肥潜力及土壤质量的演变提供一定的科学理论依据。     

Amending biochar affected enzyme activities and nitrogen turnover in Phaeozem and Luvisol

Soil nitrogen (N) is a vital source of nutrients for maintaining soil fertility and crop production. However, the effect of biochar application rate on the mechanism of organic N transformation and the contribution of enzyme mineralization is still unclear. Therefore, we conducted two 5-year field experiments in contrasting soils (Phaeozem and Luvisol) with biochar application rate at 0 t hm⁻² (CK, 0), 22.5 t hm⁻² (D₁, 1%), 67.5 t hm⁻² (D₂, 3%), and 112.5 t hm⁻² (D₃, 5%) to investigate the potential effects of biochar application rate on soil organic nitrogen (N) turnover and its linkage to enzymatic mineralization in contrasting soil. The results showed that soil organic carbon (SOC) and microbial biomass nitrogen (MBN) contents, microbial biomass carbon to nitrogen ratio (MBC:MBN) and protease activity are significantly influenced by biochar application rate whereas not by soil type. Ammonium nitrogen (NH₄⁺-N) and nitrate nitrogen (NO₃⁻-N) contents, and dehydrogenase activity are significantly changed by soil type whereas not by biochar application rate. Based on the redundancy analysis, we found that organic N fractions are associated with MBN, SOC, and protease in Phaeozem, but related to protease activity in Luvisol. Our findings indicate that organic N turnover is not only related to the bioavailability of N but also requires carbon substrates in Phaeozem, whereas the transformation of organic N in Luvisol is dominated by enzymatic mineralization as the relatively low level of bioavailable N.     

Mineralization of amino acids and its signs in nitrogen cycling of forest soil

Amino acid mineralization and its fate in soil have effects on soil nitrogen cycling. Here we used ¹⁵N-labeled alanine and methionine to study differences in their mineralization from soil organic nitrogen under 60% WHC (water holding capacity) and 90% WHC soil conditions. We found that the maximum mineralization rates were at the 24th hours for alanine and at the 5th hours for methionine, and about two times greater rates at 60% WHC than at 90% WHC. The half-live was 24–72 h for alanine and > 72 h for methionine. Half-lives of amino acids occurred sooner under 90% WHC than under 60% WHC. The results suggested that some kind of amino acids do lead the nitrogen cycling in a specific ecosystem or as a sign to trigger soil nitrogen cycling when land utilization was altered or disturbed severely by humans.     

Soil moisture effects on gross nitrification differ between adjacent grassland and forested soils in central Alberta, Canada

Background and aims

Changes in soil moisture availability seasonally and as a result of climatic variability would influence soil nitrogen (N) cycling in different land use systems. This study aimed to understand mechanisms of soil moisture availability on gross N transformation rates.

Methods

A laboratory incubation experiment was conducted to evaluate the effects of soil moisture content (65 vs. 100% water holding capacity, WHC) on gross N transformation rates using the ¹⁵N tracing technique (calculated by the numerical model FLUAZ) in adjacent grassland and forest soils in central Alberta, Canada.

Results

Gross N mineralization and gross NH ₄ ⁺ immobilization rates were not influenced by soil moisture content for both soils. Gross nitrification rates were greater at 100 than at 65% WHC only in the forest soil. Denitrification rates during the 9 days of incubation were 2.47 and 4.91 mg N kg^-1 soil d^-1 in the grassland and forest soils, respectively, at 100% WHC, but were not different from zero at 65% WHC. In the forest soil, both the ratio of gross nitrification to gross NH ₄ ⁺ immobilization rates (N/IA) and cumulative N₂O emission were lower in the 65 than in the 100% WHC treatment, while in the grassland soil, the N/IA ratio was similar between the two soil moisture content treatments but cumulative N₂O emission was lower at 65% WHC.

Conclusions

The effect of soil moisture content on gross nitrification rates differ between forest and grassland soils and decreasing soil moisture content from 100 to 65% WHC reduced N₂O emissions in both soils.     

Biochar Effectively Reduces Ammonia Volatilization From Nitrogen-Applied Soils in Tea and Bamboo Plantations

Intensive practices in forest soils result in dramatic nitrogen (N) losses, particularly ammonia (NH₃) volatilization, to adjacent environmental areas. A soil column experiment was conducted to evaluate the effect of bamboo biochar on NH₃ volatilization from tea garden and bamboo forest soils. The results showed that biochar amendment effectively reduced NH₃ volatilization from tea garden and bamboo forest soil by 79.2% and 75.5%, respectively. The soil pH values increased by 0.53-0.61 units after biochar application. The NH₄⁺-N and total N of both soils were 13.8-29.7% and 34.0-41.9% higher under the biochar treatments than under the control treatment, respectively. In addition, the soil water contents of the two biochar-amended soils were significantly higher (P < 0.05), by 10.7-12.5%, than that of the soils without biochar amendment. Therefore, biochar mitigates NH₃ volatilization from the tested forest soils, which was due to the increases in soil NH₄⁺-N, total N and water contents after biochar amendment. Our main findings suggest that biochar addition is an effective management option for sustainable forest management.     

Cycling Dynamics of NH4 + and Amino Acid Nitrogen in Soils of a Deciduous Boreal Forest Ecosystem

Conventional studies of nitrogen (N) cycling in forest ecosystems have focused on inorganic N uptake as the primary source of N for plant metabolism. More recently, however, alternative sources of N for plant nutrition, such as free amino acids, have gained attention, particularly in nutrient-limited systems. Using a multiple stable isotope (¹³C and ¹⁵N) design, that allowed us to simultaneously assess root uptake of ammonium (NH₄ ⁺) and glycine, we compared the cycling dynamics of NH₄ ⁺ and amino acid N within the soils of several interior Alaskan floodplain balsam poplar stands. Our design included multiple sampling periods extending from 45 min to 14 days, which permitted us to study interpool transfers of our carbon (C) and N isotopes over time. Microbial biomass N was the largest sink of both ¹⁵N-ammonium and glycine. Percent recovery of ¹⁵N for this pool was an order of magnitude larger than fine-root ¹⁵N uptake for most sampling periods. Although recovery of ¹⁵N in fine-root biomass was small, amino acid N and NH₄ ⁺ were assimilated at approximately the same rate irrespective of sampling period, and total recovery was still increasing 2 weeks after application. Recovery of ¹⁵N in bulk soil samples did not vary significantly over time for either treatment. However, bulk soil ¹³C declined steadily during the experiment, measuring less than 30% recovery of added label after 14 days. We suspect that the majority of ¹³C lost from our soils was respired. Soil microorganisms strongly outcompeted plants in the short term for both NH₄ ⁺ and amino acid N. However, amino acid N appears to cycle through soil N pools at approximately the same rate as inorganic N forms. The similarity in uptake patterns for inorganic and organic N suggests that these stands are meeting part of their N requirements directly from amino acids.     

黄河三角洲盐碱地不同造林模式下的土壤碳氮分布特征

为了探讨不同造林模式对土壤碳氮影响的生态效应,以黄河三角洲盐碱地白蜡+棉花(FC)、香花槐+棉花(RC)、竹柳+棉花(SC)、白蜡林(F)、竹柳林(S)等5种造林模式为研究对象,分析比较各造林模式土壤的碳氮形态及分布特征,为重度退化刺槐林的经营改造和造林模式选择提供理论依据。结果显示:(1)不同造林模式下土壤的可溶性总碳和可溶性有机碳含量均高于裸地,农林间作高于纯林,其中SC模式含量最高,其次为FC和RC模式,而F和S纯林模式较低;5种造林模式不同土层可溶性有机碳含量均表现为0—20 cm高于20—40 cm。(2)农林间作模式0—40 cm土层的可溶性全氮和可溶性有机氮平均含量均高于纯林模式,其中SC模式的含量最高。FC、SC和S纯林模式0—20 cm土层可溶性有机氮含量显著高于20—40 cm土层,分别为其1.4、1.5和2.7倍;而RC模式20—40 cm土层可溶性有机氮含量显著高于0—20 cm土层。(3)5种造林模式中,除F纯林土壤硝态氮低于裸地外,其他造林模式下的土壤各种氮养分含量均显著高于裸地。土壤可溶性有机碳与全氮和铵态氮的相关性达到极显著水平(P0.01)。研究表明农林间作模式可显著提高重度退化刺槐林皆伐后土壤中有效态碳、氮含量,其中SC模式改良效果较好,而纯林模式较差。     

Challenging the paradigm of nitrogen cycling: no evidence of in situ resource partitioning by coexisting plant species in grasslands of contrasting fertility

In monoculture, certain plant species are able to preferentially utilize different nitrogen (N) forms, both inorganic and organic, including amino acids and peptides, thus forming fundamental niches based on the chemical form of N. Results from field studies, however, are inconsistent: Some showing that coexisting plant species predominantly utilize inorganic N, while others reveal distinct interspecies preferences for different N forms. As a result, the extent to which hypothetical niches are realized in nature remains unclear. Here, we used in situ stable isotope tracer techniques to test the idea, in temperate grassland, that niche partitioning of N based on chemical form is related to plant productivity and the relative availability of organic and inorganic N. We also tested in situ whether grassland plants vary in their ability to compete for, and utilize peptides, which have recently been shown to act as an N source for plants in strongly N-limited ecosystems. We hypothesized that plants would preferentially use NO₃⁻-N and NH₄⁺-N over dissolved organic N in high-productivity grassland where inorganic N availability is high. On the other hand, in low-productivity grasslands, where the availability of dissolved inorganic N is low, and soil availability of dissolved organic N is greater, we predicted that plants would preferentially use N from amino acids and peptides, prior to microbial mineralization. Turves from two well-characterized grasslands of contrasting productivity and soil N availability were injected, in situ, with mixtures of ¹⁵N-labeled inorganic N (NO₃⁻ and NH₄⁺) and ¹³C¹⁵N labeled amino acid (l-alanine) and peptide (l-tri-alanine). In order to measure rapid assimilation of these N forms by soil microbes and plants, the uptake of these substrates was traced within 2.5 hours into the shoots of the most abundant plant species, as well as roots and the soil microbial biomass. We found that, contrary to our hypothesis, the majority of plant species across both grasslands took up most N in the form of NH₄⁺, suggesting that inorganic N is their predominant N source. However, we did find that organic N was a source of N which could be utilized by plant species at both sites, and in the low-productivity grassland, plants were able to capture some tri-alanine-N directly. Although our findings did not support the hypothesis that differences in the availability of inorganic and organic N facilitate resource partitioning in grassland, they do support the emerging view that peptides represent a significant, but until now neglected, component of the terrestrial N cycle.     

Consequences of liming and gypsum top-dressing on nitrogen and carbon dynamics in acid forest soils with different humus forms

The aim of this study was to understand the effects of lime and gypsum on nitrogen and carbon turnover of the soil. A pot experiment was conducted in parallel with a field experiment which was set up in 1989 in a declining forest of the French Ardennes. A dystric cambisol, associated with a moder and mull humus separately, was used to study changes in the soil chemistry as a result of added lime and gypsum top-dressing.The lime was applied to the surface of an acid mull humus of an oak (Quercus petraea) stand and of a moder humus of a spruce (Picea abies) stand. A quantity of 2.8 t ha^-1 equivalent CaO was supplied as CaCO₃, CaCO₃+MgO and CaSO₄.2H₂O. The experiment was installed in an open-air nursery for 20 months, during which the organic carbon and nitrogen in the solution were analysed monthly. They were analysed in the solid phase after 20 months. At the end of this period the changes in the soil and leachate depended mainly on the type of the material added.The leachate was enriched with nitrogen from the third month of the experiment under lime treatments and in the control. The same pattern was found under the two humus types but the magnitude was higher in soil with a mull humus. The nitrogen was mostly leached as NO₃ ^--N in the carbonate treatments and in the control, whereas it was predominantly NH₄ ⁺-N under gypsum. The NO₃ ^--N was 50% higher than NH₄ ⁺-N in the control and CaCO₃, CaCO₃+MgO treatments. In the CaSO₄ treatment this phenomenon was reversed. The leaching of organic carbon was greater under gypsum than under the other treatments whatever the humus.In the solid phase of the soil (organic layers) the organic carbon and nitrogen concentration decreased significantly after liming, especially in the mull humus. Consequently it induced a decrease in C:N ratio of about 18% with respect to the control.