Altered litter inputs modify carbon and nitrogen storage in soil organic matter in a lowland tropical forest

Biogeochemistry - Soil organic matter (SOM) in tropical forests is an important store of carbon (C) and nutrients. Although SOM storage could be affected by global changes via altered plant...     

Effects of alkali salts on carbon and nitrogen mineralization of organic matter in soil

Summary In an incubation experiment the mineralization of gulmohur leaves (Delonix regia L.) added to soil was studied at increased levels of exchangeable sodium percentage (ESP). CO₂ evolution, total mineralization of carbon and humic/fulvic acid carbon ratio increased with increased ESP and the process of nitrification was inhibited completely between 70–92 ESP. The mineralization and losses of nitrogen were equal to control up to 70 ESP but were very high at 92 ESP. The extractable carbon varied from 26% in case of control to 31% at 48.6 ESP.     

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.     

氮沉降对森林土壤有机质和凋落物分解的影响及其微生物学机制

氮沉降持续增加背景下土壤C∶N∶P化学计量比和pH环境等的改变及其可能的土壤微生物学机制已经成为陆地生态系统与全球变化研究的新生长点和科学研究前沿.以生态化学计量学和土壤微生物生态学为理论基础,综述了氮沉降对森林土壤有机质和凋落物分解的影响及其微生物学机制的基本理论、最新进展、研究热点与难点,旨在促进全球变化背景下陆地生态系统地下生态学的研究.氮沉降持续增加会导致森林生态系统磷循环加速,导致磷限制.氮沉降不但改变森林土壤有机质和凋落物的C∶N∶P化学计量比和降低土壤pH值,而且改变土壤微生物生物量碳氮磷、细菌、真菌和放线菌的组成以及影响碳氮磷分解的关键酶活性.氮沉降对森林土壤有机质和凋落物分解的影响表现为促进、抑制和无影响,其影响的差异可能来源于微生物效应的不同.叶片在凋落前有显著的氮磷养分回收,但是根无明显的养分回收,造成土壤有机质和凋落物的C∶N∶P化学计量比存在明显差异.基于DNA/RNA等分子生物学方法为土壤微生物生态学研究提供了强有力的手段,将促进氮沉降对森林土壤有机质和凋落物化学计量比改变的微生物学机制研究.     

不同化学性质叶凋落物添加对土壤有机碳矿化及激发效应的影响

凋落物输入可显著影响土壤有机碳(SOC)矿化速率,但添加不同化学性质叶凋落物对土壤有机碳矿化释放CO₂及激发效应的影响及其机理仍不清楚。本研究将亚热带6种树种¹³C标记的叶凋落物添加至天然次生林0～10 cm原位土柱中,比较不同树种叶凋落物添加对土壤总CO₂、外源凋落物和土壤来源CO₂释放速率和累积量以及激发效应的影响,并量化叶凋落物化学性质与土壤CO₂释放累积量、激发效应的相关关系。结果表明: 添加叶凋落物能够显著提高土壤总CO₂和土壤来源CO₂释放量,存在显著正激发效应,激发效应值为68%～128%。不同树种叶凋落物添加对土壤有机碳矿化和激发效应的影响存在显著差异。Pearson相关分析和逐步多元线性回归分析发现,凋落物来源CO₂释放累积量与叶凋落物C、P和纤维素含量呈显著负相关,而土壤来源CO₂释放量与叶凋落物C:N和木质素:N呈显著正相关。综上,不同化学性质的叶凋落物对土壤有机碳矿化和激发效应的影响存在异质性,在亚热带地区森林类型转变过程中营造具有高质量叶凋落物的人工林将有助于减少森林土壤碳损失。     

杉木和米槠凋落叶DOM对土壤碳矿化的影响

DOM(Dissolved organic matter)是土壤微生物呼吸的重要底物,凋落物淋溶的DOM对土壤碳矿化具有重要影响。选择中亚热带地区具有代表性的杉木(Cunninghamia lanceolata)和米槠(Castanopsis carlesii)凋落叶作为研究对象,通过两个月的短期室内培养,把不同凋落叶浸提出的DOM添加到培养瓶中,定期测定土壤碳矿化速率,计算土壤碳累积矿化量,探讨两种等浓度等量DOM添加对土壤碳矿化的影响,并分析DOM化学性质在土壤碳矿化过程中的重要性。结果表明:米槠凋落叶浸提得到的DOC(Dissolved organic carbon)和DON(Dissolved organic nitrogen)浓度均显著高于杉木凋落叶的(P0.05),而杉木凋落叶浸提得到的DOM的UV吸收值(SUVA_(254))和HIX(Humification index)均显著低于米槠凋落叶的(P0.01)。添加等浓度等量杉木和米槠凋落叶DOM到土壤中均显著增加了土壤碳矿化速率,在第1天内分别比对照高198%和168%,3d后下降到61.8%和44.1%,14d后基本处于平稳状态,表明外源有机物添加对土壤碳矿化的前期影响较大。培养过程中,添加杉木和米槠凋落叶DOM的土壤碳矿化累积量均能采用双因素指数模型进行拟合(r~2=0.99),但添加两者凋落叶DOM后土壤碳矿化累积量没有显著差异。     

Long-term effects of elevated nitrogen on forest soil organic matter stability

Nitrogen addition may alter the decomposition rate for different organic-matter pools in contrasting ways. Using a paired-plot design, we sought to determine the effects of long-term elevated N on the stability of five organic-matter pools: organic horizons (Oe+a), whole mineral soil (WS), mineral soil fractions including the light fraction (LF), heavy fraction (HF), and a physically recombined fraction (RF). These substrates were incubated for 300 days, and respiration, mineralized N, and active microbial biomass were measured. Samples with elevated N gave 15% lower cumulative respiration for all five substrates. Over the 300-day incubation, the Oe+a gave twice the cumulative respiration (gCkg^–1 initial C) as the LF, which gave slightly higher respiration than the HF. Respiration was 35% higher for the WS than for the RF. Mineralized N was similar between N treatments and between the LF and HF. Net N mineralized by the LF over the course of the 300-day incubation decreased with higher C:N ratio, due presumably to N immobilization to meet metabolic demands. The pattern was opposite for HF, however, which could be explained by a release of N in excess of metabolic demands due to recalcitrance of the HF organic matter. Mineralized N increased with respiration for the HF but showed no pattern, or perhaps even decreased, for the LF. WS and RF showed decreasing active microbial biomass near the end of the incubation, which corresponded with decreasing respiration and increasing nitrate. Our results show that long-term elevated N stabilized organic matter in whole soil and soil fractions.     

Effects of roots and litter on mineralization processes in forest soil

Summary Leaf litter breakdown and fine root production, including exudation, are two major influences upon carbon and nitrogen mineralization rates in forest soil. Sieving and root removal experiments were used to examine their effects. Although carbon mineralization rates declined in smaller particle size fractions of forest litter, this trend largely disappeared when results were calculated on an ash-free basis. Nitrogen mineralization by contrast, was greatest in smaller fractions.Much of the variation in carbon mineralization rates appeared to be associated with fine roots. A rapid initial exponential decay phase noted in laboratory respiration studies was probably associated with disappearance of available carbon in the form of root exudates and/or the microorganisms dependent on them. Clear cutting caused a marked reduction in the size of available carbon pools, reflecting decreased root exudation and rhizosphere activity. A model of mineralization is proposed which represents the available and humified carbon pools.Deceased     

食真菌线虫与真菌的相互作用及其对土壤氮素矿化的影响

采用悉生培养微缩体系,探讨了食真菌线虫(燕麦真滑刃线虫)与两种真菌(真菌Ⅰ：外皮毛霉和真菌Ⅱ：丛梗孢科的一种)间的相互作用及其对土壤氮素矿化的影响．结果表明,燕麦真滑刃线虫在取食两种真菌时表现为在真菌Ⅱ上的生长优于真菌Ⅰ,两个处理的线虫数达到显著差异．食真菌线虫对真菌的取食活动促进了真菌的增殖：接种真菌Ⅱ加线虫处理中真菌Ⅱ的数量是仅接种真菌Ⅱ处理的2．5～3．5倍,增幅在整个培养期基本稳定;而接种真菌Ⅰ加线虫处理中真菌Ⅰ的数量在培养前期(10d)是仅接种真菌Ⅰ处理的1．1～2．0倍。之后增幅达5．0～5．7倍．线虫和真菌的生长及增殖基本保持同步．食真菌线虫与真菌的相互作用显著提高了土壤铵态氮和矿质态氮含量,促进了土壤氮的矿化,其中线虫与真菌Ⅰ的相互作用对提高矿质态氮含量的贡献显著大于线虫与真菌Ⅱ的相互作用。     

蚂蚁筑巢对西双版纳热带森林土壤有机氮矿化的影响

蚂蚁作为生态系统工程师能够调节土壤微生物及理化环境,进而对热带森林土壤有机氮矿化速率及其时间动态产生显著影响。以西双版纳白背桐热带森林群落为研究对象,采用室内需氧培养法测定土壤有机氮矿化速率,比较蚁巢和非蚁巢土壤有机氮矿化速率的时间动态,揭示蚂蚁筑巢活动引起土壤无机氮库、微生物生物量碳及化学性质改变对有机氮矿化速率时间动态的影响。结果表明：（1）蚂蚁筑巢显著影响土壤有机氮矿化速率（P<0.01）,相较于非蚁巢,蚁巢土壤有机氮矿化速率提高了261%;（2）土壤有机氮矿化速率随月份推移呈明显的单峰型变化趋势,即6月最大（蚁巢1.22 mg kg^-1 d^-1、非蚁巢0.41 mg kg^-1 d^-1）,12月最小（蚁巢0.82 mg kg^-1 d^-1、非蚁巢0.18 mg kg^-1 d^-1）;（3）两因素方差分析表明,不同月份及不同处理对土壤有机氮矿化速率、NH₄-N及NO₃-N产生显著影响（P<0.05）,但对NO₃-N的交互作用不显著;（4）蚂蚁筑巢显著提高了无机氮库（NH₄-N与NO₃-N）、微生物生物量碳、有机质、水解氮、全氮及易氧化有机碳等土壤养分含量,而降低了土壤pH值;（5）回归分析表明,铵态氮和硝态氮对土壤有机氮矿化速率产生显著影响,分别解释87.89%、61.84%的有机氮矿化速率变化;（6）主成份分析表明NH₄-N、微生物生物量碳及有机质是影响有机氮矿化速率时间动态的主要因素,而全氮、NO₃-N、易氧化有机碳、水解氮及pH对土壤有机氮矿化速率的影响次之,且pH与土壤有机氮矿化速率呈显著负相关。总之,蚂蚁筑巢活动主要通过影响土壤NH₄-N、微生物生物量碳及有机质的状况,进而调控西双版纳热带森林土壤有机氮矿化速率的时间动态。研究结果将有助于进一步提高对土壤氮矿化生物调控机制的认识。     

南亚热带森林植被恢复演替序列的土壤有机碳氮矿化

采用室内培养的方法,分析了南亚热带鼎湖山森林植被恢复演替序列不同阶段代表性森林—马尾松林、针阔叶混交林和季风常绿阔叶林土壤(0~10cm)CO2、CH4排放/吸收和有机氮矿化的差异.结果表明:3种森林土壤培养52周的CO2-C累积排放量分别为(30.66±3.36)、(58.17±7.25)和(59.31±13.58)mg·kg-1,而其中的65.12%、64.41%和64.12%均在前9周被排放;马尾松林土壤的CO2-C累积排放量一直显著小于针阔叶混交林和季风常绿阔叶林;用相符的二库动力学模型模拟的活性库和惰性库的碳矿化速率均呈递减趋势;土壤培养52周吸收CH4的累积量、培养20周有机氮净矿化量和净硝化量均为马尾松林<针阔叶混交林<季风常绿阔叶林(P<0.05),净矿化的有效氮以硝态氮为主.说明森林植被类型的变化改变了土壤有机碳的分解速率,这是其影响土壤有机碳含量的一种内在方式.     

胶州湾滨海湿地凋落物分解对土壤有机碳矿化的影响

通过室内培养试验和三维荧光光谱技术(3D-EEMs),开展了胶州湾滨海湿地碱蓬、芦苇和互花米草的分解对土壤有机碳矿化的影响研究。结果表明,凋落物的添加提高了土壤有机碳矿化速率和累积矿化量,具体表现为碱蓬互花米草芦苇空白对照;乘幂曲线模型能较好地描述有机碳矿化速率和累积矿化量的变化趋势。光谱分析表明,分解过程中类蛋白荧光强度始终大于类腐殖酸荧光强度;利用荧光区域积分进行定量分析表明,不同处理下类蛋白质物质占比最高,类腐殖质物质次之;荧光参数表明,土壤有机碳的芳香化程度在培养期间先升高后降低。凋落物分解通过增加土壤中的营养物质,提高了土壤中微生物活性,从而改变了土壤有机碳的结构和化学组分,且凋落物的植被特征决定了其对土壤有机碳矿化影响程度的大小。     

鼎湖山亚热带常绿针阔叶混交林凋落物及矿质氮输入对土壤有机碳分解的影响

2010年7-12月,选取鼎湖山国家级自然保护区亚热带针阔叶混交林,采用全因子控制试验,研究不同类型的凋落物(针叶和阔叶凋落物)添加及氮处理(加氮模拟氮饱和、减氮模拟根吸收)对表层(0～10 cm)和下层(20～30 cm)土壤有机质分解(呼吸)的影响.结果表明： 2010年7-11月间,两种凋落物的添加使土壤-凋落物系统的呼吸速率显著增加,但这种影响在12月消失.减氮和加氮处理均显著增加了土壤-凋落物系统的呼吸.叶凋落物短期内完全分解,对土壤碳分解和积累的影响十分有限,可能不是该系统中土壤有机质的主要来源.通过减少土壤可利用氮模拟根系对氮的吸收能够明显促进土壤有机质的分解.     

Feedback from soil inorganic nitrogen on soil organic matter mineralisation and growth in a boreal forest ecosystem

Current nitrogen (N) deposition rates are considerably higher than during pre-industrial times and the growing interest in forest fertilisation requires better understanding of how the N and carbon (C) cycles interact. This study is based on experimental data showing how Scots pine (Pinus sylvestris L.) forests respond to single or consecutive pulse doses of N. The data were used to support the implementation of a dynamic feedback mechanism in the Q model, allowing for changes in soil N availability to regulate the rate of decomposer efficiency. Simulations of the long-term effects of slowly increasing N deposition with and without dynamic decomposer efficiency were then compared. Both versions of the model accurately predicted the response of tree growth to N fertilisation. Slowly increasing inputs of N over a century in the modified version acted on the inputs and outputs of soil C in opposing ways: (a) rate of litter input slowed down because more N was retained in the soil and thus not available for tree growth; (b) rate of C output, through soil heterotrophic respiration, was also gradually reduced due to increasing decomposer efficiency, although not enough to sufficiently balance the reduced litter input. Accurate prediction of the amount of added N retained in the ecosystem seems to be one of the key issues for estimating enhanced C sequestration.     

土壤及凋落物源氮对中亚热带森林土壤SON的影响

土壤可溶性有机氮(SON)含量虽低,却是土壤氮库中最活跃的组分之一;主要来源于凋落物分解和土壤氮素转化。但是它们各自对土壤的影响还不清楚。通过添加杉木和~(15)N标记的阔叶凋落物于土壤表面,研究针阔叶凋落物分解对土壤SON的影响,及与土壤氮的关系。结果表明:由于没有降水的淋溶影响,培养期间,凋落物SON的显著降低,并没有直接增加土壤SON。与对照比较,杉木凋落物添加显著增加了土壤无机氮的含量,而较高C/N比的阔叶凋落物在其分解初期首先需要吸收更多的土壤氨态氮。添加~(15)N标记的阔叶凋落物提高了土壤SON在培养90—210天来自凋落物的比例,在第210天高达74.8%;来自凋落物的氨态氮比例在实验30天开始增加,到第210天高达39.8%;但是对硝态氮的影响不大。结果表明,土壤SON在培养初期因受凋落物的影响,主要来自土壤有机质的分解,而来自凋落物的SON更容易矿化;且土壤源的氮更容易发生硝化作用。可见,土壤中的SON是与凋落物分解动态、以及对土壤的影响有关。     

A comparison between the effect of fresh and dried organic materials added to soil on carbon and nitrogen mineralization

Summary Incubation experiments were carried out at 29°C in which fresh chopped, dried chopped, or dried and ground material of wheat plants,Polygonum nodosum, Senecio congestus (R. Br. DC.) and lucerne was mixed with a heavy calcareous loam. The C/N ratios of these materials were 45.9, 32.0, 19.3, and 12.6, respectively. At intervals of one or two weeks the content of mineral nitrogen in the treated and untreated soils was determined. In this way the immobilised or released nitrogen could be calculated. Parallel to this experiment the production of CO₂ in the soils treated in the same way was determined.The experiments have clearly shown that the mineralization of the carbon and nitrogen of incorporated organic materials is influenced not only by the N-content, the C/N ratio of the materials and the amount of the materials, but also depends on whether the plant materials are in fresh chopped, or dried chopped, or dried and ground condition.In most cases a retardation of the rate of nitrogen mineralization was found after drying the organic materials due to an increase of the C/N ratio of the water-soluble organic fraction by drying. The depressing effect of drying on the rate of nitrogen mineralization was increased by a mechanical breaking-up of the dried materials, presumably due to an increased surface of the non-soluble carbonaceous compounds.     

亚热带退化红壤区森林恢复类型土壤有机碳矿化对温度的响应

土壤有机质分解是陆地生态系统碳循环的重要环节,它不仅受植被类型的影响,对环境温度也十分敏感。以江西省泰和县石溪退化红壤区马尾松(Pinus massoniana)、木荷(Schima superb)和枫香(Liquidambar formosana)3种森林类型为研究对象,将其土壤分别置于4种不同温度(5、15、25℃和35℃)条件下培养,采用碱液吸收法进行为期35 d的土壤碳矿化研究。在同一温度条件下,不同林型土壤CO_2累计碳排放量大小顺序为:枫香马尾松木荷。在4种不同温度条件下枫香林地土壤CO_2累计排放量最大,其次是马尾松林、木荷林,且不同森林类型土壤CO_2累计排放量随温度升高而增加(P0.05)。在15℃、25℃和35℃条件下,不同林地土壤潜在碳排放量间无显著性差异。在15℃和25℃条件下,土壤碳排放量随土壤全碳含量呈现先增后减的变化趋势(P0.05),全碳的极值点分别约为1.83%和1.89%。不同植被类型和培养温度对土壤碳矿化量有显著影响,说明植被类型和温度能够对土壤呼吸产生重要影响,且不同温度对土壤呼吸作用更显著(P0.000),但两因素间并无显著交互效应。在25℃时,不同林型土壤碳排放量随土壤含水量先增后减,表明土壤含水量并不是影响土壤碳排放量的调控因子。采用单库模式方程C_m=C_o(1-exp~(-kt))对土壤潜在碳排放进行模拟,得出不同温度不同林型土壤最大碳排放量随温度升高而增加。不同林型不同温度条件下土壤Q_(10)值范围为1.797—1.971,变化幅度较小,且不同林型土壤Q_(10)值并未表现出显著性差异,这一结论为研究林型和温度对土壤碳矿化的影响提供参考。