Effect of added nitrogen on plant litter decomposition depends on initial soil carbon and nitrogen stoichiometry

Increasing organic carbon inputs to agricultural soils through the use of pastures or crop residues has been suggested as a means of restoring soil organic carbon lost via anthropogenic activities, such as land use change. However, the decomposition and retention of different plant residues in soil, and how these processes are affected by soil properties and nitrogen fertiliser application, is not fully understood. We evaluated the rate and extent of decomposition of 13C-pulse labelled plant material in response to nitrogen addition in four pasture soils of varying physico-chemical characteristics. Microbial respiration of buffel grass (Cenchrus ciliaris L.), wheat (Triticum aestivum L.) and lucerne (Medicago sativa L.) residues was monitored over 365-days. A double exponential model fitted to the data suggested that microbial respiration occurred as an early rapid and a late slow stage. A weighted three-compartment mixing model estimated the decomposition of both soluble and insoluble plant 13C (mg C kg−1 soil). Total plant material decomposition followed the alkyl C: O-alkyl C ratio of plant material, as determined by solid-state 13C nuclear magnetic resonance spectroscopy. Urea-N addition increased the decomposition of insoluble plant 13C in some soils (≤0.1% total nitrogen) but not others (0.3% total nitrogen). Principal components regression analysis indicated that 26% of the variability of plant material decomposition was explained by soil physico-chemical characteristics (P = 0.001), which was primarily described by the C:N ratio. We conclude that plant species with increasing alkyl C: O-alkyl C ratio are better retained as soil organic matter, and that the C:N stoichiometry of soils determines whether N addition leads to increases in soil organic carbon stocks.

Bonding regimes of nitrogen in amorphous carbon

Nitrogen can have numerous effects on diamond-like carbon: it can dope, it can form the hypothetical superhard compound C3N4, or it can create fullerene-like bonding structures. We studied amorphous carbon nitrogen films deposited by a filtered cathodic vacuum arc as a function of nitrogen content, ion energy and deposition temperature. The incorporation of nitrogen from 10-2 to 10 at% was measured by secondary ion mass spectrometry and elastic recoil detection analysis and was found to vary slightly sublinearly with N2 partial pressure during deposition. In the doping regime from 0 to about 0.4% N, the conductivity changes while the sp3 content and optical gap remain constant. From 0.4 to approximately 10% N, existing sp2 sites condense into clusters and reduce the band gap. Nitrogen contents over 10% change the bonding from mainly sp3 to mainly sp2. Ion energies between 20 and 250 eV do not greatly modify this behaviour. Deposition at higher temperatures causes a sudden loss of sp3 bonding above about 150 °C. Raman spectroscopy and optical gap data show that existing sp2 sites begin to cluster below this temperature, and the clustering continues above this temperature. This transition is found to vary only weakly with nitrogen addition, for N contents below 10%.

Effects of nitrogen fertilization on soil respiration in temperate grassland in Inner Mongolia, China

Nitrogen addition to soil can play a vital role in influencing the losses of soil carbon by respiration in N-deficient terrestrial ecosystems. The aim of this study was to clarify the effects of different levels of nitrogen fertilization (HN, 200 kg N ha(-1) year(-1); MN, 100 kg N ha(-1) year(-1); LN, 50 kg N ha(-1) year(-1)) on soil respiration compared with non-fertilization (CK, 0 kg N ha(-1) year(-1)), from July 2007 to September 2008, in temperate grassland in Inner Mongolia, China. Results showed that N fertilization did not change the seasonal patterns of soil respiration, which were mainly controlled by soil heat-water conditions. However, N fertilization could change the relationships between soil respiration and soil temperature, and water regimes. Soil respiration dependence on soil moisture was increased by N fertilization, and the soil temperature sensitivity was similar in the treatments of HN, LN, and CK treatments (Q (10) varied within 1.70-1.74) but was slightly reduced in MN treatment (Q (10) = 1.63). N fertilization increased soil CO2 emission in the order MN > HN > LN compared with the CK treatment. The positive effects reached a significant level for HN and MN (P < 0.05) and reached a marginally significant level for LN (P = 0.059 < 0.1) based on the cumulative soil respiration during the 2007 growing season after fertilization (July-September 2007). Furthermore, the differences between the three fertilization treatments and CK reached the very significant level of 0.01 on the basis of the data during the first entire year after fertilization (July 2007-June 2008). The annual total soil respiration was 53, 57, and 24% higher than in the CK plots (465 g m(-2) year(-1)). However, the positive effects did not reach the significant level for any treatment in the 2008 growing season after the second year fertilization (July-September 2008, P > 0.05). The pairwise differences between the three N-level treatments were not significant in either year (P > 0.05).

Effect of cattle urine addition on the surface emissions and subsurface concentrations of greenhouse gases in a UK peat grassland

Grazing systems represent a substantial percentage of the global anthropogenic flux of nitrous oxide (N2O) as a result of nitrogen addition to the soil. The pool of available carbon that is added to the soil from livestock excreta also provides substrate for the production of carbon dioxide (CO2) and methane (CH4) by soil microorganisms. A study into the production and emission of CO2, CH4 and N2O from cattle urine amended pasture was carried out on the Somerset Levels and Moors, UK over a three-month period. Urine-amended plots (50 g N m−2) were compared to control plots to which only water (12 mg N m−2) was applied. CO2 emission peaked at 5200 mg CO2 m−2 d−1 directly after application. CH4 flux decreased to −2000 μg CH4 m−2 d−1 two days after application; however, net CH4 flux was positive from urine treated plots and negative from control plots. N2O emission peaked at 88 mg N2O m−2 d−1 12 days after application. Subsurface CH4 and N2O concentrations were higher in the urine treated plots than the controls. There was no effect of treatment on subsurface CO2 concentrations. Subsurface N2O peaked at 500 ppm 12 days after and 1200 ppm 56 days after application. Subsurface NO3− concentration peaked at approximately 300 mg N kg dry soil−1 12 days after application. Results indicate that denitrification is the key driver for N2O release in peatlands and that this production is strongly related to rainfall events and water-table movement. N2O production at depth continued long after emissions were detected at the surface. Further understanding of the interaction between subsurface gas concentrations, surface emissions and soil hydrological conditions is required to successfully predict greenhouse gas production and emission.

High rate growth of nanocrystalline diamond films using high microwave power and pure nitrogen/methane/hydrogen plasma

In this work, we investigate the impact of minute amounts of pure nitrogen addition into conventional methane/hydrogen mixtures on the growth characteristics of nanocrystalline diamond (NCD) films by microwave plasma assisted chemical vapour deposition (MPCVD), under high power conditions. The NCD films were produced from a gas mixture of 4% CH4/H2 with two different concentrations of N2 additive and microwave power ranging from 3.0 kW to 4.0 kW, while keeping all the other operating parameters constant. The morphology, grain size, microstructure and texture of the resulting NCD films were characterized by using scanning electron microscope (SEM), micro-Raman spectroscopy and X-ray diffraction (XRD) techniques. N2 addition was found to be the main parameter responsible for the formation and for the key change in the growth characteristics of NCD films under the employed conditions. Growth rates ranging from 5.4 μm/h up to 9.6 μm/h were achieved for the NCD films, much higher than those usually reported in the literature. The enhancing factor of nitrogen addition on NCD growth rate was obtained by comparing with the growth rate of large-grained microcrystalline diamond films grown without nitrogen and discussed by comparing with that of single crystal diamond through theoretical work in the literature. This achievement on NCD growth rate makes the technology interesting for industrial applications where fast coating of large substrates is highly desirable.

Investigation of bonded hydrogen defects in nanocrystalline diamond films grown with nitrogen/methane/hydrogen plasma at high power conditions

In this work, we investigate the influence of some growth parameters such as high microwave power ranging from 3.0 to 4.0 kW and N2 additive on the incorporation of bonded hydrogen defects in nanocrystalline diamond (NCD) films grown through a small amount of pure N2 addition into conventional 4% CH4/H2 plasma using a 5 kW microwave plasma CVD system. Incorporation form and content of hydrogen point defects in the NCD films produced with pure N2 addition was analyzed by employing Fourier-transform infrared (FTIR) spectroscopy for the first time. A large amount of hydrogen related defects was detected in all the produced NCD films with N2 additive ranging from 29 to 87 µm thick with grain size from 47 nm to 31 nm. Furthermore, a specific new H related sharp absorption peak appears in all the NCD films grown with pure N2/CH4/H2 plasma at high powers and becomes stronger at powers higher than 3.0 kW and is even stronger than the 2920 cm−1 peak, which is commonly found in CVD diamond films. Based on these experimental findings, the role of high power and pure nitrogen addition on the growth of NCD films including hydrogen defect formation is analyzed and discussed.

Behaviour of Gaseous Chlorine and Alkali Metals During Biomass Thermal Utilisation

The behaviour of gaseous chlorine and alkali metals of three sorts of biomass (Danish straw, Swedish wood, and sewage sludge) in combustion or gasification is investigated by the chemical equilibrium calculating tool. The ranges of temperature, air-to-fuel ratio, and pressure are varied widely in the calculations (T=400-1800 K, gimel=0-1.8, and P=0.1-2.0 MPa). Results show that the air excess coefficient only has less significant influence on the release of gaseous chlorine and potassium or sodium during combustion. However, in biomass gasification, the influence of the air excess coefficient is very significant. Increasing air excess coefficient enhances the release of HCl(g), KOH(g), or NaOH(g) as well as it reduces the formation of KCl(g), NaCl(g), K(g), or Na(g). In biomass combustion or straw and sludge gasification, increasing pressure enhances the release of HCl(g) and reduces the amount of KCI(g), NaCl(g), KCI(g), or NaOH(g) at high temperatures. However, during wood gasification, the pressure enhances the formation of KOH(g) and KCI(g) and reduces the release of K(g) and HCl(g) at high temperatures. During wood and sewage sludge pyrolysis, nitrogen addition enhances the formation of KCN(g) and NaCN(g) and reduces the release of K(g) and Na(g). Kaolin addition in straw combustion may enhance the formation of potassium aluminosilicate in ash and significantly reduces the release of KCl(g) and KOH(g) and increases the formation of HCl(g).

内蒙古高原成熟和退化羊草草原群落物种功能特性与土壤微生物量C、N、P对氮素添加响应

氮素是大多数陆地生态系统初级生产力的主要限制因子。由于人类的工业和农业生产活动不断加剧，导致全球性氮沉降增加，使大多数生态系统氮素的可获得性增强。从而降低或消除了氮素对生态系统的限制作用，加速了生态系统生物地球化学过程，对物种多样性和生态系统结构与功能产生了显著的影响。但由于成土母质、气候条件、地形地貌、植被组成等的差异，不同生态系统类型对氮素增加的响应也不尽相同。欧洲和北美一些发达国家地区对于草地生态系统对于全球性氮沉降增加响应进行了较全面的研究，对于分布广泛的欧亚大陆草原研究相对不足。 本文研究选择对于欧亚大陆草原较具代表性的成熟羊草草原群落及该群落的退化类型为研究对象，从1999年开始，在这两类群落中选取地形相对平缓均一，植被组成一致的地段设置了施肥小区并进行持续氮素添加实验。本文研究了成熟和退化羊草草原群落物种功能特性与土壤微生物量C、N、P对氮素添加响应。 羊草群落中6种主要植物的地上生物量、种群密度、比叶面积、叶氮和叶绿素含量对于氮素添加响应以及各指标之间相关关系的分析表明：比叶面积、基于质量的叶片含氮量和叶绿素含量、叶绿素a和叶绿素b的比值等叶片水平上物种功能特性间的相互作用，共同影响和决定了种群密度和地上生物量对氮素添加的响应。羊草通过提高比叶面积、叶片叶绿素含量和含氮量、种群密度及个体生物量等多重调节功能对氮素添加做出响应。西伯利亚羽茅主要通过提高比叶面积、单位质量叶片的叶绿素含量和含氮量，以及株丛生物量，使其在群落占据优势。大针茅和冰草在提高比叶面积、叶片叶绿素含量和含氮量的调节能力相对较低，种群密度沿氮素添加梯度显著降低。黄囊苔草只能通过提高叶片叶绿素含量和含氮量对氮素添加做出响应，其叶绿素a与叶绿素b的比值沿氮素添加梯度逐渐降低，种群密度和地上生物量也显著降低。糙隐子草的叶绿素a与叶绿素b比值沿氮素添加梯度显著降低，但由于糙隐子草具有较高的SLA，且对叶绿素、叶片含氮量的调节能力较强，氮素添加处理没有对其种群密度和地上生物量产生显著的影响。上述结果支持Tilman的光资源竞争假说和Knops等的物种替代假说。 成熟和退化羊草群落土壤微生物量、土壤有机碳、全氮、全磷、速效氮、pH以及凋落物碳、氮、磷含量的测定结果表明：（1）成熟羊草群落表层土壤微生物量碳、氮、磷含量均随氮素添加量的增加而降低;退化羊草群落表层土壤微生物量碳、氮、磷含量沿氮素梯度表现出先增加而后降低的趋势;相关分析的结果显示各群落土壤微生物量碳、氮、磷均与土壤pH呈显著的正相关。（2）微生物量碳、氮、磷含量均随土层深度的增加而下将;而对照的微生物量碳、氮、磷含量则与土壤有机质含量呈显著正相关。（3）年度间降水量差异对土壤微生物量碳、氮、磷具有较大影响。综合上述研究结果，我们认为成熟羊草群落土壤微生物生长不受氮素限制，但退化群落不同;氮素添加导致的土壤酸化作用可能是两类群落表层土壤微生物量下降的主要因素，且这种影响主要集中在0-10cm的表层土壤;表层土壤微生物量碳、氮、磷对氮素添加的响应可能还受到其它因子（如生长季降水量）的影响;深层土壤微生物量较低主要是由于土壤有机质含量较低的缘故。

典型草原优势植物养分回收特性对养分和水分梯度变化的响应

养分回收是植物衰老时，养分从衰老组织向活的组织体转移的一种过程。该过程延长了养分在植物体内的滞留时间，提高了植物保持养分的能力，因此是植物适应养分贫瘠生境的策略之一。全球气候变化，包括降水格局改变和氮（N）沉降增加，改变了生态系统正常的生物地球化学循环，因此可能会对植物的养分回收特性产生影响。研究不同N、磷（P）、水梯度上，植物物种养分回收特性的响应格局，对于预测N沉降增加和降水格局改变对物种养分利用策略的潜在影响，具有一定的理论与实践意义。本研究以中国科学院植物研究所多伦恢复生态学实验站长期施N肥实验（0，1，2，4，8，16，32，64 g N m-2 yr-1等8个水平）为研究平台研究了克氏针茅（Stipa krylovii）群落中优势植物养分回收随N素添加梯度的变化，同时结合三个盆栽控制实验（施N肥实验：0，0.5，1，2，4，8，16，32，64，128 g N m-2等10个水平;施P肥实验：梯度同施N肥实验;控水实验：3600，4000，4500，5143，6000，7200，9000，12000，18000，36000 mL pot-1等10个水平），主要探讨了羊草（Leymus chinensis）养分回收效率（从衰老组织中回收转移的养分百分数，RE）和养分回收度（以枯叶中养分浓度衡量，RP）以及其它叶片养分特性(绿叶养分浓度和比叶面积SLA)对环境因子改变的响应格局。同时，我们还调查了枯叶C:N比和C:P比等参数，研究环境因子改变对凋落物分解的影响。 1）连续4年施N肥显著降低了五个物种叶片N素回收度（NRP），对P素回收度（PRP）的影响在各物种间差异较大，但低N提高了多数物种的PRP;物种间，冷蒿（Artemisia frigida）RP（枯叶N和P浓度分别为14.3±2.0 mg g-1和0.68±0.09 mg g-1）最低，砂韭（Allium bidentatum）（N：5.2±0.2 mg g-1，P：0.12±0.01 mg g-1）最高。沿施N梯度，N素回收效率（NRE）的变化趋势在物种间差异较小但在方法间（叶干重水平，叶面积水平和单株水平）差异较大，而P素回收效率（PRE）的变化在物种间和方法间差别都较大。叶干重水平和叶面积水平上，NRE在四个物种中表现出显著降低的趋势，PRE只在糙隐子草（Cleistogenes squarrosa）和星毛委陵菜（Potentilla acaulis）中显著降低，其它三个物种变化不显著。单株水平上，所有物种NRE（除了克氏针茅）和PRE均与施N量梯度无显著性关系。物种间，砂韭的RE最高（＞80.0%），冷蒿和星毛委陵菜最低（＜60.0%）。方法间，叶片水平上的RE均高于单株水平上。沿施N肥梯度，两个禾本科物种SLA无显著变化规律，而其它三个物种SLA表现出先增加后变化不大的趋势。物种间，最高和最低的SLA分别表现在冷蒿和克氏针茅。沿施N肥梯度，五个物种C:N比呈先显著降低后缓慢降低的趋势。物种间，最大和最小的C:N比分别出现在砂韭和冷蒿。 2）盆栽施N肥实验中，一定范围内，施N肥显著提高了羊草地上地下生物量、SLA和绿叶N浓度，显著降低了C:N比、NRP、NRE和PRE，但对绿叶P浓度、叶片PRP和C:P比无明显影响。平均枯叶N浓度和枯叶P浓度分别为16.2 mg g-1和1.01 mg g-1，平均NRE和PRE分别为46.1﹪和58.1﹪。10月时，地下生物量和养分积累均高于地上部分。 3）盆栽施P肥实验中，一定范围内，施P肥显著地提高了羊草地上地下生物量、SLA、绿叶N浓度和绿叶P浓度，显著降低了C:N比、C:P比、NRP、PRP和PRE，但对NRE无显著影响。平均枯叶N浓度和枯叶P浓度分别为9.9 mg g-1和7.43 mg g-1，平均NRE和PRE分别为58.2﹪，平均PRE为56.1﹪。10月时地下部分生物量和N库积累均高于地上部分，而P库在两个部分间差别不大。 4）盆栽控水实验中，一定范围内，供水量增加显著增加了羊草地上地下生物量、SLA、NRP、PRP、PRE、C:N比和C:P比，显著降低了绿叶N浓度，但对绿叶P浓度和NRE无显著性影响。平均枯叶N浓度和枯叶P浓度分别为10.4 mg g-1和0.32 mg g-1，平均NRE和PRE分别为54.4﹪和76.8﹪。10月时，地下部分生物量和养分积累均高于地上部分。 以上结果表明，N、P和水分因子的改变影响了植物生物量和养分分配、叶片养分特性、养分回收能力以及枯叶分解质量等，且不同梯度影响程度也不同。因此，未来全球变化包括N沉降增加和降水格局改变可能影响植物养分利用策略和凋落物分解特性，进而可能对植被-土壤系统养分循环产生影响。