Microbial biomass and nitrogen cycling responses to fertilization and litter removal in young northern hardwood forests

The influence of site fertility on soil microbial biomass and activity is not well understood but is likely to be complex because of interactions with plant responses to nutrient availability. We examined the effects of long-term (8 yr) fertilization and litter removal on forest floor microbial biomass and N and C transformations to test the hypothesis that higher soil resource availability stimulates microbial activity. Microbial biomass and respiration decreased by 20–30 % in response to fertilization. Microbial C averaged 3.8 mg C/g soil in fertilized, 5.8 mg C/g in control, and 5.5 mg C/g in litter removal plots. Microbial respiration was 200 µg CO₂-C g^–1 d^–1 in fertilized plots, compared to 270 µg CO₂-C g^–1 d^–1 in controls. Gross N mineralization and N immobilization did not differ among treatments, despite higher litter nutrient concentrations in fertilized plots and the removal of substantial quantities of C and N in litter removal plots. Net N mineralization was significantly reduced by fertilization. Gross nitrification and NO₃ ^– immobilization both were increased by fertilization. Nitrate thus became a more important part of microbial N cycling in fertilized plots even though NH₄ ⁺ availability was not stimulated by fertilization.Soil microorganisms did not mineralize more C or N in response to fertilization and higher litter quality; instead, results suggest a difference in the physiological status of microbial biomass in fertilized plots that influenced N transformations. Respiration quotients (qCO₂, respiration per unit biomass) were higher in fertilized plots (56 µg CO₂-C mg C^–1 d^–1) than control (48 µg CO₂-C mg C^–1 d ^–1) or litter removal (45 µg CO₂-C mg C^–1 d^–1), corresponding to higher microbial growth efficiency, higher proportions of gross mineralization immobilized, and lower net N mineralization in fertilized plots. While microbial biomass is an important labile nutrient pool, patterns of microbial growth and turnover were distinct from this pool and were more important to microbial function in nitrogen cycling.     

半干旱草地土壤团聚体氮磷转化相关酶活性对氮添加的响应

日益加剧的大气氮沉降对土壤养分循环过程产生了深刻影响,土壤养分转化相关酶是其关键调控途径,而土壤不同粒级团聚体结构和环境差异导致其中酶活性介导的养分转换过程可能不同。但目前对半干旱区土壤团聚体水平养分转化相关酶活性对氮沉降的响应还不清楚。基于黄土高原自然草地持续3年的野外氮添加控制试验,分析不同氮添加水平下土壤不同粒级团聚体中的基础理化性质、氮（亮氨酸氨基肽酶LAP和β-1,4-N-乙酰氨基葡萄糖苷酶NAG）和磷转化相关的酶（磷酸单酯酶PME、磷酸二酯酶PDE和植酸酶phyA）活性及酶计量比,探索氮添加对团聚体酶活性的影响。结果表明：（1）氮添加导致了不同粒级团聚体中pH显著降低;高氮添加引起土壤团聚体有机碳、全氮、硝态氮、C ： P和N ： P升高;（2）随氮添加浓度增加,不同粒级团聚体中PME、PDE和phyA活性先降低后升高,而LAP、NAG和酶活性氮磷比均逐渐升高;团聚体酶活性总体表现为小团聚体（<0.25 mm）>中团聚体（0.25-2 mm）>大团聚体（>2 mm）;（3）在中和大团聚体中氮添加通过影响土壤N相关养分调控P转化相关酶活性。总之,氮添加通过改变团聚体养分及其计量比、pH等影响氮、磷转化相关酶活性。     

Contribution of winter processes to soil nitrogen flux in taiga forest ecosystems

We measured annual net nitrogen (N) mineralization, nitrification, and amino acid production in situ across a primary successional sequence in interior Alaska, USA. Net N mineralization per gram dry soil increased across the successional sequence, but with a sharp decline in the oldest stage (black spruce). Net N mineralization expressed per gram soil organic matter exhibited the opposite pattern, suggesting that soil organic matter quality decreases significantly across succession. Net N mineralization rates during the growing season from green-up (early May) through freeze-up (late September–early October) accounted for approximately 60% of the annual inorganic N flux, whereas the remaining N was released during the apparent dormant season. Nitrogen release during winter occurred primarily during October–January with only negligible N mineralization during early spring in stands of willow, alder, balsam poplar and white spruce. By contrast, black spruce stands exhibited substantial mineralization after snow melt during early spring. The high rates of N mineralization in late autumn through early winter coincide with high turnover of fine root biomass in these stands, suggesting that labile substrate production, rather than temperature, is a major controlling factor over N release in these ecosystems. We suggest that the convention of restricting measurements of soil processes to the growing season greatly underestimate annual flux rates of inorganic nitrogen in these high-latitude ecosystems.     

黄土高原不同土壤微生物量碳、氮与氮素矿化势的差异

以采自于黄土高原差异较大的25个农田石灰性耕层土壤为供试土样,对黄土高原主要类型土壤中微生物量碳(Bc)、微生物量氮(BN)和氮素矿化势(NO)的差异性进行了比较研究.结果表明,Bc、BN和NO在不同类型土壤间存在显著差异,由关中平原至陕北风沙区,BC、Bn和NO总体呈现下降趋势,其中以土垫旱耕人为土最高,简育干润均腐土最低,黄土正常新成土和干润砂质新成土居中:土垫旱耕人为土、简育干润均腐土、黄土正常新成土和干润砂质新成土等各土类平均BC分别为305.2μg·g-1,108.4μg·g-1,161.7μg·g-1和125.4μg·g-1,BN分别为43.8μg·g-1,20.3μg·g-1,26.0μg·g-1和30.6μg·g-1,NO分别为223μ·g-1,75μg·g-1,163μg·g-1和193μg·g-1.土壤氮素矿化速率(k)则以简育干润均腐土最大,干润砂质新成土最低,土垫旱耕人为土和黄土正常新成土居中:土垫旱耕人为土、简育干润均腐土、黄土正常新成土和干润砂质新成土的k分别为0.039w-1,0.044w-1,0.031w-1和0.019w-1.不同类型土壤BC、BN与NO的差异,主要与土壤形成过程、输入土壤的植物同化产物和土壤有机质的差异等有关,从较大尺度进一步证明了在黄土高原,土壤有机质是影响BC、BN的主要因子.研究结果对分析黄土高原土壤生产力形成过程具有一定参考价值.     

石灰性土壤微生物量碳、氮与土壤颗粒组成和氮矿化势的关系

以黄土高原土壤类型和土壤肥力差异较大的25个农田石灰性耕层土壤为供试土样,研究了土壤微生物量碳（BC）、微生物量氮（BN）与土壤氮素矿化势（NO）、全氮（TN）、有机碳（OC）及土壤颗粒组成的关系．结果表明：BC、BN与TN、OC呈极显著正相关（P〈0．01）,表明BC、BN与土壤肥力关系密切,可作为评价土壤质量的生物学指标．BC、BN与NO均呈高度正相关,相关系数分别为0．665和0．741（P〈0．01）．BC、BN、TN、OC、NO与土壤物理性粘粒（〈0．01mm）呈显著或极显著正相关,而与物理性砂粒（〉0．01mm）呈显著或极显著负相关,与物理性粘粒和砂粒比值呈显著或极显著正相关,表明土壤有机质主要通过与土壤物理性粘粒复合而形成有机无机复合体．     

New perspectives on forest soil carbon and nitrogen cycling processes: Roles of arbuscular mycorrhizal versus ectomycorrhizal tree species

Nearly all tree species develop symbiotic relationships with either arbuscular mycorrhizal (AM) or ectomycorrhizal (EM) fungi to acquire nutrients from soils, and hence influence soil carbon (C) and nitrogen (N) cycles in terrestrial ecosystems. It is crucial to understand the differences in soil C and N cycles between AM and EM forests and the underlying mechanisms. In this review, we first compared the differences in the soil C and N cycles between AM and EM forests, and synthesized the underlying mechanisms from perspectives of the inputs, stabilization, and outputs of soil C and N in forest ecosystems. We also compared the responses of soil C and N cycles between AM and EM forests to global changes. In this field, one major research priority is comparing the structure and function (including the soil C and N cycles) between AM and EM forest ecosystems to provide theoretical basis and solid data for improving forest productivity and ecosystem services. The second research focus is deepening the understanding of the effects of interactions between aboveground litter and belowground mycorrhiza and free-living microbes on soil C and N cycles to reveal the potential underlying mechanisms in forests with different mycorrhizal symbioses. Third, the research methodology and new techniques need refining and applying to explicitly focus on scaling up the fine-scale measurements to better expound and predict the C and N cycles in forest ecosystems. Finally, more studies on the stability of soil organic matter among different mycorrhizal forests are needed to precisely assess responses of the structure and function of forest ecosystems to global changes.     

冻融对土壤氮素损失及有效性的影响

土壤冻融交替是寒冷生态系统土壤氮素循环的重要驱动力。已有研究表明冻融交替作用能够促进氮素周转,从而缓解因土壤有效氮素缺乏而引起的植物生长限制。即便如此,冻融环境下土壤有效氮素供应量远高于其利用量,过剩的氮素会通过气态(N2O-N)排放、淋溶和径流等途径损失。论述了季节冻融环境和模拟冻融条件下土壤氮素损失状况;同时分析了影响冻融土壤N2O生产的相关因素、产生途径及冻融期N2O大量排放的机制;针对冻融交替过程中土壤氮素有效性问题,探讨了氮矿化、可溶性有机氮(DON)和微生物量氮(MBN)与氮素损失的关系。评述了土壤冻融研究中存在的不足,认为模型研究、土壤微生物功能、氮素转化中间产物、土壤-植物界面过程是未来值得关注和深入探讨的研究方向。     

Microbial control of soil organic matter mineralization responses to labile carbon in subarctic climate change treatments

Half the global soil carbon (C) is held in high‐latitude systems. Climate change will expose these to warming and a shift towards plant communities with more labile C input. Labile C can also increase the rate of loss of native soil organic matter (SOM); a phenomenon termed ‘priming’. We investigated how warming (+1.1 °C over ambient using open top chambers) and litter addition (90 g m^?2 yr^?1) treatments in the subarctic influenced the susceptibility of SOM mineralization to priming, and its microbial underpinnings. Labile C appeared to inhibit the mineralization of C from SOM by up to 60% within hours. In contrast, the mineralization of N from SOM was stimulated by up to 300%. These responses occurred rapidly and were unrelated to microbial successional dynamics, suggesting catabolic responses. Considered separately, the labile C inhibited C mineralization is compatible with previously reported findings termed ‘preferential substrate utilization’ or ‘negative apparent priming’, while the stimulated N mineralization responses echo recent reports of ‘real priming’ of SOM mineralization. However, C and N mineralization responses derived from the same SOM source must be interpreted together: This suggested that the microbial SOM‐use decreased in magnitude and shifted to components richer in N. This finding highlights that only considering SOM in terms of C may be simplistic, and will not capture all changes in SOM decomposition. The selective mining for N increased in climate change treatments with higher fungal dominance. In conclusion, labile C appeared to trigger catabolic responses of the resident microbial community that shifted the SOM mining to N‐rich components; an effect that increased with higher fungal dominance. Extrapolating from these findings, the predicted shrub expansion in the subarctic could result in an altered microbial use of SOM, selectively mining it for N‐rich components, and leading to a reduced total SOM‐use.     

Carbon input to soil may decrease soil carbon content

It is commonly predicted that the intensity of primary production and soil carbon (C) content are positively linked. Paradoxically, many long‐term field observations show that although plant litter is incorporated to soil in large quantities, soil C content does not necessarily increase. These results suggest that a negative relationship between C input and soil C conservation exists. Here, we demonstrate in controlled conditions that the supply of fresh C may accelerate the decomposition of soil C and induce a negative C balance. We show that soil C losses increase when soil microbes are nutrient limited. Results highlight the need for a better understanding of microbial mechanisms involved in the complex relationship between C input and soil C sequestration. We conclude that energy available to soil microbes and microbial competition are important determinants of soil C decomposition.     

Response of nitrogen cycling to simulated climate change: differential responses along a subalpine ecotone

In situ nitrogen (N) transformations and N availability were examined over a four‐year period in two soil microclimates (xeric and mesic) under a climate‐warming treatment in a subalpine meadow/sagebrush scrub ecotone. Experimental plots that spanned the two soil microclimates were exposed to an in situ infrared (IR) climate change manipulation at the Rocky Mountain Biological Laboratory, near Crested Butte, Colorado. Although the two microclimates did not differ significantly in their rates of N transformations in the absence of heating, they differed significantly in their response to increased IR. Under a simulated warming in the sagebrush‐dominated xeric microclimate, gross N mineralization rates doubled and immobilization rates increased by up to 60% over the first 2 years of the study but declined to predisturbance rates by the fourth year. This temporal pattern of gross mineralization rates correlated with a decline in SOM. Concurrently, rates of net mineralization rates in the heated plots were 60% higher than the controls after the first year. There were no differences in gross or net nitrification rates with heating in the xeric soils. In contrast to the xeric microclimate, there were no significant effects of heating on any N transformation rates in the mesic microclimate. The differing responses in N cycling rates of the two microclimate to the increased IR is most certainly the result of differences in initial soil moisture conditions and vegetation type and cover.     

暖温带森林土壤微生物量、群落结构和活性对植物地下碳源的响应

该研究以典型的亚热带—温带过渡区森林为对象,采用野外过程监测和控制试验相结合的方法,利用磷脂脂肪酸和土壤胞外酶活性分别表征土壤微生物群落结构和活性,并结合微环境因子,重点探究土壤微生物生物量、群落结构和活性对植物地下碳输入的响应特征。结果表明：在观测周期内,处理均能显著降低三组年龄段林分的土壤微生物量碳,其变化幅度在－8.72％~－5.72％之间,其中在80年的林分中降幅最大,而在160年的林分中降幅最小;微生物量氮的变化规律与相应的微生物量碳的变化规律相似,但与对照相比其差异性均未达到显著性水平;另外,经壕沟处理2~4个月后,所有林分的土壤微生物量碳和氮与对照相比出现增加的现象。处理均能对三组年龄段林分的土壤微生物群落结构产生不同程度的影响,其中40年林分的土壤微生物群落对处理的响应程度要高于另外两个年龄段的林分;与对照相比,壕沟处理样方的腐生真菌的相对丰富度均下降明显,其中在40年和80年林分中的下降幅度达到显著水平,而细菌、放线菌和丛枝菌根真菌均无明显变化;壕沟处理样方的水解酶(β-葡萄糖苷酶和N-乙酰-葡萄糖苷酶)活性均显著下降,而氧化酶(酚氧化酶和过氧化物酶)活性的变化相对较小,除80年的林分外,其余林分均不显著。此外,处理均不能显著影响土壤的含水量和温度。该研究结果为初步阐明全球气候变化背景下森林土壤微生物结构及其功能的变化特征以及更加精确预测未来森林土壤碳的变化趋势提供了科学依据。     

基于DSSAT模型的吉林省黑土作物-土壤氮循环和土壤有机碳平衡

应用DSSAT模型中的CERES-Maize作物模型和Century土壤模型,分析了作物管理参数、施肥量、土壤初始氮含量和作物桔杆还田对吉林省黑土地区玉米生长、氮循环以及有机碳氮生态平衡的影响.结果表明:在玉米目标产量为12000～15000kg.hm-2条件下,最佳施氮肥量为200～240kgN.hm-2.在该氮肥用量下,玉米地上氮吸收量为250～290kgN.hm-2,其中,120～140kgN.hm-2来自土壤,130～150kgN.hm-2来自肥料;提高氮肥用量(250～420kgN.hm-2)将导致土壤残留氮明显增加(63～183kgN.hm-2);延迟追肥时间同样导致土壤残留氮增加;当玉米秸杆还田量超过6000kg.hm-2时,模拟的土壤活性有机碳、氮可以维持当年的供需平衡.建议在吉林省中部地区黑土玉米带,化肥施氮量控制在200～240kgN.hm-2,适时追肥,秸杆还田量在6000kg.hm-2以上,以确保高产和维持土壤养分生态平衡.     

Elevated CO2 effects on carbon and nitrogen cycling in grass/clover turves of a Psammaquent soil

Effects of elevated CO₂ (525 and 700 L L^–1), and a control (350 L L^–1 CO₂), on biochemical properties of a Mollic Psammaquent soil in a well-established pasture of C3 and C4 grasses and clover were investigated with continuously moist turves in growth chambers over four consecutive seasonal temperature regimes from spring to winter inclusive. After a further spring period, half of the turves under 350 and 700 L L^–1 were subjected to summer drying and were then re-wetted before a further autumn period; the remaining turves were kept continuously moist throughout these additional three consecutive seasons. The continuously moist turves were then pulse-labelled with ¹⁴C-CO₂ to follow C pathways in the plant/soil system during 35 days.Growth rates of herbage during the first four seasons averaged 4.6 g m^–2 day^–1 under 700 L L^–1 CO₂ and were about 10% higher than under the other two treatments. Below-ground net productivity at the end of these seasons averaged 465, 800 and 824 g m^–2 in the control, 525 and 700 L L^–1 treatments, respectively.in continuously moist soil, elevated CO₂ had no overall effects on total, extractable or microbial C and N, or invertase activity, but resulted in increased CO₂-C production from soil, and from added herbage during the initial stages of decomposition over 21 days; rates of root decomposition were unaffected. CO₂ produced h^–1 mg^–1 microbial C was about 10% higher in the 700 L L^–1 CO₂ treatment than in the other two treatments. Elevated CO₂ had no clearly defined effects on N availability, or on the net N mineralization of added herbage.In the labelling experiment, relatively more ¹⁴C in the plant/soil system occurred below ground under elevated CO₂, with enhanced turnover of ¹⁴C also being suggested.Drying increased levels of extractable C and organic-N, but decreased mineral-N concentrations; it had no effect on microbial C, but resulted in lowered microbial N in the control only. In soil that had been previously summer-dried, CO₂ production was again higher, but net N mineralization was lower, under elevated CO₂ than in the control after autumn pasture growth.Over the trial period of 422 days, elevated CO₂ generally appears to have had a greater effect on soil C turnover than on soil C pools in this pasture ecosystem.     

荒漠土壤微生物量碳、氮变化对降水的响应

以腾格里沙漠东南缘的典型荒漠植被为研究对象,通过遮雨棚和滴灌系统设置5个降水梯度,即极端干旱处理、中度干旱处理、对照、增水处理I和增水处理II,研究了荒漠土壤微生物量碳(MBC)、氮(MBN)和微生物碳氮比(MBC/MBN)对季节、降水和土壤深度的响应规律,以期为极端降水事件影响干旱荒漠区土壤微生物量碳、氮及其循环规律的深入研究提供科学依据。结果表明:(1)MBC、MBN和MBC/MBN对降水处理的响应存在差异,三者的变化范围为:230.14—272.87 mg/kg,13.82—17.58 mg/kg,19.78—36.06。其中,降水处理对MBC、MBN的影响显著,对MBC/MBN的影响不显著,在极端干旱处理下,MBC、MBN均显著高于其他降水处理;(2)两年间的MBC、MBN和MBC/MBN差异显著,2017年较2016年MBC、MNB显著减少,MBC/MBN显著增加;(3)MBC、MBN和MBC/MBN变化均表现季节性差异,变化范围分别为:153.31—337.09 mg/kg,7.89—22.29 mg/kg,14.82—46.04,其中MBC、MBN为春季最高、秋季最低,M...     

Elevated CO2 and temperature effects on soil carbon and nitrogen cycling in ryegrass/white clover turves of an Endoaquept soil

Effects of elevated CO₂ (700 L L^–1) and a control (350 L L^–1 CO₂) on the productivity of a 3-year-old ryegrass/white clover pasture, and on soil biochemical properties, were investigated with turves of a Typic Endoaquept soil in growth chambers. Temperature treatments corresponding to average winter, spring, and summer conditions in the field were applied consecutively to all of the turves. An additional treatment, at 700 L L^–1 CO₂ and a temperature 6°C higher throughout than in the other treatments, was included.Under the same temperature conditions, overall herbage yields in the 700 L L^–1 CO₂ treatment were ca. 7% greater than in the control at the end of the summer period. Root mass (to ca 25 cm depth) in the 700 L L^–1 CO₂ treatment was then about 50% greater than in the control, but in the 700 L L^–1 CO₂+6°C treatment it was 6% lower than in the control. Based on decomposition results, herbage from the 700 L L^–1+6°C treatment probably contained the highest proportion of readily decomposable components.Elevated CO₂ had no consistent effect on soil total C and N, microbial C and N, or extractable C concentrations in any of the treatments. Under the same temperature conditions, it did, however, enhance soil respiration (CO₂-C production) and invertase activity. The effects of elevated CO₂ on rates of net N mineralization were less distinct, and the apparent availability of N for the sward was not affected. Under elevated CO₂, soil in the higher-temperature treatment had a higher microbial C:N ratio; it also had a greater potential to degrade plant materials.Data interpretation was complicated by soil spatial variability and the moderately high background levels of organic matter and biochemical properties that are typical of New Zealand pasture soils. More rapid cycling of C under CO₂ enrichment is, nevertheless, indicated. Futher long-term experiments are required to determine the overall effect of elevated CO₂ on the soil C balance.     

Size and functional diversity of microbe populations control plant persistence and long-term soil carbon accumulation

Soil organic matter (SOM) models are based on the equation dC/dt = ?kC which states that the decomposition rate of a particular carbon (C) pool is proportional to the size of the pool and the decomposition constant k. However, this equation does not adequately describe the decomposition of recalcitrant SOM compounds. We present an alternative theory of SOM dynamics in which SOM decay rate is controlled by the size and the diversity of microbe populations and by the supply of energy‐rich litter compounds. We show that the SOM pool does not necessarily reach equilibrium and may increase continuously, which explains how SOM can accumulate over thousands of years. However, the simulated SOM accumulation involves the sequestration of available nutrients. How can plants persist? This question is explored with two models that couple the C cycle with a limiting nutrient. The first model considers a single type of microbe whereas the second includes two functional types in competition for energy and nutrient acquisition. The condition for plant persistence is the presence of these two competing microbial types.     

不同氮输入对湿地草甸沼泽土N_2O排放和有机碳矿化的影响

通过室内培养实验,研究了不同氮输入梯度下(N0:0mg·g-1,N1:0.1mg·g-1,N2:0.2mg·g-1,N3:0.5mg·g-1)湿地草甸沼泽土N2O排放和有机碳矿化特征,并分析了土壤微生物量碳、氮变化规律。整个培养期(23d)内,N0、N1、N2和N3处理N2O排放总量分别为91.12、133.02、147.75和303.45μg.kg-1,随氮输入量增大而增大,表明氮输入对N2O排放产生促进作用;氮输入处理的有机碳矿化速率在整个培养期除最后培养阶段外均低于对照,表明氮输入对有机碳矿化有一定的抑制作用;各氮输入处理土壤微生物量碳降低,与对照差异显著(P0.05),但各处理间差异未达到显著水平,土壤微生物量氮随氮输入量增大呈线性增加,各处理间差异显著(P0.05),表明氮输入影响土壤微生物结构和组成,具体影响机理须进一步探讨。     

Mineralization of carbon and nitrogen in acid forest soil treated with fast and slow-release nutrients

The effects of slow (apatite, biotite) and fast-release nutrients (P, K, Mg) on C and N mineralization in acid forest soil were studied. These nutrients were applied alone or together with urea or urea and limestone. The production of CO₂ in the soil samples taken one and three growing seasons after the application was lower in the soils treated with the fast-release nutrients than in the untreated soils. Similar reduction of microbial activity was not seen after the apatite and apatite+biotite treatments. In the first growing season, urea and urea+limestone enhanced CO₂ production, but after three growing seasons, the opposite was true. Apatite and apatite+biotite added together with urea did not compensate for the decreasing effect of urea on the CO₂ production. The addition of fast-release salts increased somewhat the concentration of NH _inf4 ^sup+ in the soil and more NH₄ ⁺ accumulated during laboratory incubation in the soil samples taken one growing season after the application. The urea addition immediately increased the concentrations of NH₄ ⁺ and of NO₃ ⁻ in the soil, but, three growing seasons after application, urea had only a slight increasing effect on mineral N content of the soil. Slow-release nutrients seem to have a more favourable effect than fast-release salts on nutrient turnover in acid forest soil.     

冻融交替对土壤氮素循环关键过程的影响与机制研究进展

冻融交替是由于季节或昼夜热量的变化,在表土及以下一定深度形成的反复冻结和解冻的过程,是普遍存在于中、高纬度及高海拔地区的一种自然现象。在全球变暖的背景下,部分地区的土壤环境将经受更广泛和频繁的冻融交替作用,这将对土壤氮素循环关键过程产生深远的影响。冻融交替主要通过改变土壤的理化性质使土壤微生物量、微生物群落的组成和结构发生改变,进而影响氮素在土壤中的迁移与转化,是陆地生态系统氮循环的重要影响因素。目前,关于冻融交替对土壤氮素循环关键过程影响的研究结果还不尽一致,其影响机制尚不明晰,研究方法也还有待进一步创新。重点论述了冻融交替对土壤氮素循环各个关键过程的影响效应,归纳总结了冻融交替对土壤氮素循环的影响机制,简要指出了目前研究过程中存在的一些不足,并对未来研究中值得重点关注和深入研究的科学问题进行了探讨与展望。     

土壤水分和氮添加对华北平原高产农田有机碳矿化的影响

通过105 d的恒温(25℃)控湿室内培养方法,探讨了华北平原高产粮田土壤有机碳矿化特征以及水分和有机、无机氮输入对其影响。试验设4个肥料添加水平和4个水分梯度,分别为对照(S0)、仅添加无机氮(尿素)(S1)、无机氮和有机氮(鸡粪)配施(S2)以及仅添加有机氮(S3)和25%(田间持水量;M0)、50%(M1)、75%(M2)和100%(M3)共16个处理,每处理3次重复。结果表明,各处理有机碳矿化速率均在培养后1 d达第1高峰,之后直线下降,培养7 d时下降幅度达57.2%—75.0%,培养20—30 d时出现第2高峰。有机碳累积矿化量有208.8—1161 mg/kg,主要集中在前30 d,可占整个培养期的59.1%—69.9%,105 d的净矿化率为0.07%—2.01%。根据双指数方程模拟结果,研究了土壤潜在矿化碳库(C1+C2),其中活性碳库(C1)和惰性碳库(C2)分别为53.0—135.1 mg/kg和156.9—1069 mg/kg,潜在矿化率为1.75%—9.66%。土壤含水量显著影响有机碳矿化,且与潜在矿化碳库呈二次函数关系(P0.05)。田间持水量25%—100%范围内,随着土壤含水量的升高,有机碳矿化速率呈增加趋势,但增幅降低,其中M2(田间持水量75%)的有机碳净矿化率最高。有机碳矿化量与土壤微生物碳和矿质氮含量呈线性正相关(P0.05),保持氮水平(200 kg N/hm2)相同,有机氮(鸡粪)和无机氮(尿素)均显著促进土壤有机碳矿化,但两者间差异不显著(P0.05),且有机氮和无机氮对有机碳矿化的影响均与土壤含水量有显著交互作用(P0.05)。