Mechanisms of plant species impacts on ecosystem nitrogen cycling

Plant species are hypothesized to impact ecosystem nitrogen cycling in two distinctly different ways. First, differences in nitrogen use efficiency can lead to positive feedbacks on the rate of nitrogen cycling. Alternatively, plant species can also control the inputs and losses of nitrogen from ecosystems. Our current understanding of litter decomposition shows that most nitrogen present within litter is not released during decomposition but incorporated into soil organic matter. This nitrogen retention is caused by an increase in the relative nitrogen content in decomposing litter and a much lower carbon‐to‐nitrogen ratio of soil organic matter. The long time lag between plant litter formation and the actual release of nitrogen from the litter results in a bottleneck, which prevents feedbacks of plant quality differences on nitrogen cycling. Instead, rates of gross nitrogen mineralization, which are often an order of magnitude higher than net mineralization, indicate that nitrogen cycling within ecosystems is dominated by a microbial nitrogen loop. Nitrogen is released from the soil organic matter and incorporated into microbial biomass. Upon their death, the nitrogen is again incorporated into the soil organic matter. However, this microbial nitrogen loop is driven by plant‐supplied carbon and provides a strong negative feedback through nitrogen cycling on plant productivity. Evidence supporting this hypothesis is strong for temperate grassland ecosystems. For other terrestrial ecosystems, such as forests, tropical and boreal regions, the data are much more limited. Thus, current evidence does not support the view that differences in the efficiency of plant nitrogen use lead to positive feedbacks. In contrast, soil microbes are the dominant factor structuring ecosystem nitrogen cycling. Soil microbes derive nitrogen from the decomposition of soil organic matter, but this microbial activity is driven by recent plant carbon inputs. Changes in plant carbon inputs, resulting from plant species shifts, lead to a negative feedback through microbial nitrogen immobilization. In contrast, there is abundant evidence that plant species impact nitrogen inputs and losses, such as: atmospheric deposition, fire‐induced losses, nitrogen leaching, and nitrogen fixation, which is driven by carbon supply from plants to nitrogen fixers. Additionally, plants can influence the activity and composition of soil microbial communities, which has the potential to lead to differences in nitrification, denitrification and trace nitrogen gas losses. Plant species also impact herbivore behaviour and thereby have the potential to lead to animal‐facilitated movement of nitrogen between ecosystems. Thus, current evidence supports the view that plant species can have large impacts on ecosystem nitrogen cycling. However, species impacts are not caused by differences in plant quantity and quality, but by plant species impacts on nitrogen inputs and losses.     

A new strain, Streptomyces venezuelae GY1, producing a poly(vinyl alcohol)-degrading enzyme

Summary An actinomycete strain, which could produce an extracellular poly(vinyl alcohol) (PVA)-degrading enzyme, was isolated from a PVA-contaminated soil sample using PVA as the sole carbon source. The strain was identified as Streptomyces venezuelae according to the whole-nucleotide-sequence analysis of 16S rDNA, the morphological and the physiological characteristics. The strain produced 120 U/l extracellular PVA-degrading enzyme when PVA was used as the sole carbon source. When glucose was used as the sole carbon source, however, the extracellular enzyme activity was very low (12 U/l). This is the first report showing that an actinomycete strain can produce a PVA-degrading enzyme.     

1株土壤放线菌的分类鉴定及其抗菌活性的研究

对从土壤微生物中筛选到的放线菌菌株1356进行分类学和抗菌活性的研究。采用多相分类法,对菌株的形态特征、培养特征、生理生化特性及16 SrRNA基因序列进行了研究。结果表明:该菌株的形态特征、培养特征、生理生化特性为链霉菌属的特征;16S rDNA序列分析及系统进化树分析表明其序列与灰色产色链霉菌的同源性最高;该菌株的发酵产物对番茄叶霉、白色念珠菌、小麦根腐菌等17种真菌均有不同程度的抑制作用。放线菌1356菌株具有广谱抗真菌活性而对细菌无作用;初步确定其为链霉菌属灰色产色链霉菌的一个亚种。     

Root-Parasitic Nematodes Enhance Soil Microbial Activities and Nitrogen Mineralization

Obligate root-parasitic nematodes can affect soil microbes positively by enhancing C and nutrient leakage from roots but negatively by restricting total root growth. However, it is unclear how the resulting changes in C availability affect soil microbial activities and N cycling. In a microplot experiment, effects of root-parasitic reniform nematodes (Rotylenchulus reniformis) on soil microbial biomass and activities were examined in six different soils planted with cotton. Rotylenchulus reniformis was introduced at 900 nematodes kg^–1 soil in May 2000 prior to seeding cotton. In 2001, soil samples were collected in May before cotton was seeded and in November at the final harvest. Extractable C and N were consistently higher in the R. reniformis treatments than in the non-nematode controls across the six different soils. Nematode inoculation significantly reduced microbial biomass C, but increased microbial biomass N, leading to marked decreases in microbial biomass C:N ratios. Soil microbial respiration and net N mineralization rates were also consistently higher in the nematode treatments than in the controls. However, soil types did not have a significant impact on the effects of nematodes on these microbial parameters. These findings indicate that nematode infection of plant roots may enhance microbial activities and the turnover of soil microbial biomass, facilitating soil N cycling. The present study provides the first evidence about the direct role of root-feeding nematodes in enhancing soil N mineralization.     

氮沉降对杉木人工林土壤有机碳矿化和土壤酶活性的影响

为探讨氮沉降对亚热带森林土壤有机碳矿化及土壤酶活性的影响规律,在杉木人工林中开展了野外模拟N沉降试验。试验设计为4种处理,分别为N0（对照）、N1（60 kg N?hm-2?a-1）、N2（120 kg N?hm-2?a-1）和N3（240 kg N?hm-2?a-1）,每处理重复3次。通过28 d的培养后发现,各土层有机碳日均矿化量随培养时间的延长呈下降趋势,而有机碳累计矿化量则逐步增加。不同氮沉降处理下各土层有机碳累计矿化量总体趋势表现为：随着氮沉降量的增加而降低,日均矿化量降低幅度以N1最大,其次是N0和N2,N3降幅最小。相同N沉降处理下,参与土壤碳循环的6种主要酶（蔗糖酶、纤维素酶、淀粉酶、β-葡糖苷酶、多酚氧化酶、过氧化物酶）活性、土壤有机碳日均矿化量和有机碳累计矿化量均随土层加深而降低。氮沉降对6种土壤酶活性的影响存在差异,对纤维素酶和多酚氧化酶具有促进作用,而对淀粉酶和过氧化物酶表现出一定的抑制作用;中-低氮沉降（N1、N2）对蔗糖酶无影响,而对β-葡糖苷酶具有促进作用,高氮沉降（N3）促进了蔗糖酶活性,但抑制了β-葡糖苷酶活性。表层土壤中,土壤有机碳累积矿化量与土壤纤维素酶、β-葡糖苷酶、过氧化物酶活性呈显著正相关。因此,氮沉降促进了表层土壤纤维素酶、多酚氧化酶和蔗糖酶的活性,但在一定程度上抑制了淀粉酶和过氧化物酶,对土壤有机碳矿化也表现出明显的抑制作用。     

Differential effects of sugar maple, red oak, and hemlock tannins on carbon and nitrogen cycling in temperate forest soils

Tannins are abundant secondary chemicals in leaf litter that are hypothesized to slow the rate of soil-N cycling by binding protein into recalcitrant polyphenol–protein complexes (PPCs). We studied the effects of tannins purified from sugar maple, red oak, and eastern hemlock leaf litter on microbial activity and N cycling in soils from northern hardwood–conifer forests of the northeastern US. To create ecologically relevant conditions, we applied tannins to soil at a concentration (up to 2 mg g⁻¹ soil) typical of mineral soil horizons. Sugar maple tannins increased microbial respiration significantly more than red oak or hemlock tannins. The addition of sugar maple tannins also decreased gross N mineralization by 130% and, depending upon the rate of application, decreased net rates of N mineralization by 50–290%. At low concentrations, the decrease in mineralization appeared to be driven by greater microbial-N immobilization, while at higher concentrations the decrease in mineralization was consistent with the formation of recalcitrant PPCs. Low concentrations of red oak and hemlock tannins stimulated microbial respiration only slightly, and did not significantly affect fluxes of inorganic N in the soil. When applied to soils containing elevated levels of protein, red oak and hemlock tannins decreased N mineralization without affecting rates of microbial respiration, suggesting that PPC formation decreased substrate availability for microbial immobilization. Our results indicate that tannins from all three species form recalcitrant PPCs, but that the degree of PPC formation and its attendant effect on soil-N cycling depends on tannin concentration and the pool size of available protein in the soil.     

Leaf litter diversity alters microbial activity,microbial abundances,and nutrient cycling in a subtropical forest ecosystem

Human activities affect both tree species composition and diversity in forested ecosystems. This in turn alters the species diversity of plant litter and litter quality, which may have cascading effects on soil microbial communities and their functions for decomposition and nutrient cycling. We tested microbial responses to litter species diversity in a leaf litter decomposition experiment including monocultures, 2-, and 4-species mixtures in the subtropical climate zone of southeastern China. Soil microbial community composition was assessed by lipid analysis, and microbial functions were measured using extracellular enzyme activity and gross rates of nitrogen mineralization. We observed a positive relationship between litter species diversity and abundances of mycorrhizal fungi and actinomycetes. Alternatively, enzyme activities involved in carbon and phosphorus acquisition, and enzyme indices of relative carbon limitation, were higher only in the 4-species mixtures. This suggests that the minimum basal substrate level for enzyme production was reached, or that limitation was higher, at the highest diversity level only. Responses to litter diversity also changed over time, where phosphatase responses to litter diversity were strongest early in decomposition and the indices of carbon limitation relative to other nutrients showed stronger responses later in decomposition. Enzyme activities were related to lipid biomarker data and the mass of litter remaining at the third time point, but relationships between enzyme activity and the mass of litter remaining were not consistent across other time points. We conclude that litter species richness will likely only reduce microbial functions at key intervals of diversity loss while microbial growth is more sensitive to incremental diversity loss, with no clear relationships between them or to ecosystem functions. The observed litter diversity effects on soil microbial biomass and enzyme activity indicate interactions of aboveground and belowground communities, and together with environmental conditions they are important for maintaining ecosystem functions.     

武夷山低海拔和高海拔森林土壤有机碳的矿化特征

研究不同海拔土壤有机碳矿化对深入认识不同海拔森林土壤有机碳动态变化具有重要意义.本文以武夷山低海拔和高海拔森林土壤为研究对象,通过室内模拟其在各自年平均气温(17、9℃)条件下的矿化培养试验,探讨土壤有机碳矿化特征的差异.结果表明:培养126 d后,尽管高海拔森林土壤的有机碳含量显著高于低海拔森林土壤,但低海拔和高海拔森林土壤在各自环境温度背景下的有机碳累积矿化量并无显著差异.一级动力学方程均能较好地模拟高低海拔森林土壤有机碳矿化特征,高海拔和低海拔森林土壤有机碳潜在矿化量(CP)和矿化速率常数均无显著差异,但低海拔土壤C_P/SOC值和矿化率显著高于高海拔土壤,表明在环境温度背景下,低海拔土壤固碳能力低于高海拔土壤.随着培养时间增加,高海拔土壤微生物生物量碳和微生物熵显著高于低海拔土壤,表明高海拔土壤微生物的碳同化量高于低海拔土壤微生物,有利于有机碳的积累.高海拔森林土壤中的β-葡萄糖甘酶和纤维素水解酶高于低海拔森林土壤,说明高海拔土壤微生物可能更多地分解活性碳.未来气候变暖可能暗示着会降低高海拔土壤有机碳固碳能力和微生物碳利用效率,从而导致土壤有机碳储量下降.     

Streptomyces lydicus A_(01) affects soil microbial diversity,improving growth and resilience in tomato

The actinomycete Streptomyces lydicus A_(01) promotes tomato seedling growth; however, the underlying mechanism is unclear. In this study, we investigated whether changes in soil microbial diversity, following Streptomyces lydicus A_(01) treatment, were responsible for the increased tomato seedling growth. Eukaryotic 18 S ribosomal DNA(rDNA) sequencing showed that S. lydicus A_(01)-treated and untreated soil shared 193 operational taxonomic units(OTUs), whereas bacterial 16 S rDNA sequencing identified 1,219 shared OTUs between the treated and untreated soil. Of the 42 dominant eukaryotic OTUs, eight were significantly increased and six were significantly decreased after A_(01) treatment. Of the 25 dominant bacterial OTUs, 12 were significantly increased and eight were significantly decreased after A_(01) treatment.Most of the eukaryotes and bacteria that increased in abundance exhibited growth promoting characteristics,which were mainly predicted to be associated with mineralization of nitrogen and phosphorus, phosphate solubilization, nutrient accumulation, and secretion of auxin, whereas some were related to plant protection,such as the degradation of toxic and hazardous substances. Soil composition tests showed that S. lydicus A_(01) treatment enhanced the utilization of nitrogen, phosphorus, and potassium in tomato seedlings. Thus, microbial fertilizers based on S. lydicus A_(01) may improve plant growth, without the detriment effects of chemical fertilizers.     

广西典型喀斯特地区深层土壤有机碳矿化及其影响因素

以广西典型峰丛洼地草地和原生林深层土壤(70～100cm)为对象,利用微生物交叉接种培养试验,研究不同土地利用类型、土壤微生物群落和通气条件对深层土壤有机碳矿化的影响。在124d的培养期内,微生物接种改变了0～28d原生林和0～81d草地深层土壤有机碳矿化速率,而通气条件变化对这一过程没有明显影响。3因素方差分析结果显示,深层土壤有机碳累积矿化率受土地利用类型、微生物群落和通气条件的影响显著(P<0.01),且存在3因素间交互效应。研究结果对于深入认识喀斯特深层土壤有机碳稳定机制和评估碳储量及其周转具有重要意义。     

Phenotypic variation in Streptomyces sp. DSM 40537, a lipoteichoic acid producing actinomycete

Aims:  To reinvestigate the production of lipoteichoic acid (LTA) by the actinomycete strain Streptomyces sp. DSM 40537 (=ATCC 3351).
Methods and Results:  LTA was extracted and purified from strain Streptomyces sp. DSM 40537. The identification of the LTA was confirmed by Western blotting with a monoclonal antibody. During these studies, two stable phenotypic variants of DSM 40537 were obtained, one of which released a distinctive orange pigment. 16S rRNA gene sequencing of each variant yielded identical sequences and allowed phylogenetic analysis to be performed.
Conclusions:  Streptomyces sp. DSM 40537 was shown to exhibit stable morphological variation. The strain was confirmed to be a LTA-producing actinomycete and to belong to the Streptomyces albidoflavus cluster within the genus Streptomyces .
Significance and Impact of the Study:  These data provide important support for the hypothesis that the distribution of LTA is linked to that of wall teichoic acids and emphasizes the need to reinvestigate LTA distribution in actinomycetes.     

单点突变葡萄糖异构酶(GIG138P)基因在变铅青链霉菌中的高效表达及其稳定性研究

通过三步亚克隆 ,将单点突变葡萄糖异构酶 ( GIG1 38P)基因及其调控序列插入链霉菌质粒p IJ40 83,构建重组表达质粒 p IJ40 83- GI1 .用重组质粒转化变铅青链霉菌 TK54原生质体 ,经硫链丝菌素抗性 ( Th R)筛选 ,获得重组菌株 TK54/p IJ40 83- GI1 .酶活力测定和 SDS- PAGE分析表明 ,GIG1 38P基因在变铅青链霉菌中得到高效表达 ,GI1粗酶液比活力为 1 5U/mg,GI1表达量约占菌体可溶性蛋白的 2 5% .同时也研究了重组质粒的遗传稳定性 .重组菌株在无选择压力条件下经液体连续传代培养 ,GI1比活力和 GI1表达量在 2 0 0 h传代时间中呈平缓下降趋势     

Elevated temperature shifts soil N cycling from microbial immobilization to enhanced mineralization,nitrification and denitrification across global terrestrial ecosystems

We assessed the response of soil microbial nitrogen (N) cycling and associated functional genes to elevated temperature at the global scale. A meta‐analysis of 1,270 observations from 134 publications indicated that elevated temperature decreased soil microbial biomass N and increased N mineralization rates, both in the presence and absence of plants. These findings infer that elevated temperature drives microbially mediated N cycling processes from dominance by anabolic to catabolic reaction processes. Elevated temperature increased soil nitrification and denitrification rates, leading to an increase in N₂O emissions of up to 227%, whether plants were present or not. Rates of N mineralization, denitrification and N₂O emission demonstrated significant positive relationships with rates of CO₂ emissions under elevated temperatures, suggesting that microbial N cycling processes were associated with enhanced microbial carbon (C) metabolism due to soil warming. The response in the abundance of relevant genes to elevated temperature was not always consistent with changes in N cycling processes. While elevated temperature increased the abundances of the nirS gene with plants and nosZ genes without plants, there was no effect on the abundances of the ammonia‐oxidizing archaea amoA gene, ammonia‐oxidizing bacteria amoA and nirK genes. This study provides the first global‐scale assessment demonstrating that elevated temperature shifts N cycling from microbial immobilization to enhanced mineralization, nitrification and denitrification in terrestrial ecosystems. These findings infer that elevated temperatures have a profound impact on global N cycling processes with implications of a positive feedback to global climate and emphasize the close linkage between soil microbial C and N cycling.     

Tannin impacts on microbial diversity and the functioning of alpine soils: a multidisciplinary approach

In alpine ecosystems, tannin-rich-litter decomposition occurs mainly under snow. With global change, variations in snowfall might affect soil temperature and microbial diversity with biogeochemical consequences on ecosystem processes. However, the relationships linking soil temperature and tannin degradation with soil microorganisms and nutrients fluxes remain poorly understood. Here, we combined biogeochemical and molecular profiling approaches to monitor tannin degradation, nutrient cycling and microbial communities (Bacteria, Crenarcheotes, Fungi) in undisturbed wintertime soil cores exposed to low temperature (0°C/−6°C), amended or not with tannins, extracted from Dryas octopetala . No toxic effect of tannins on microbial populations was found, indicating that they withstand phenolics from alpine vegetation litter. Additionally at −6°C, higher carbon mineralization, higher protocatechuic acid concentration (intermediary metabolite of tannin catabolism), and changes in fungal phylogenetic composition showed that freezing temperatures may select fungi able to degrade D. octopetala 's tannins. In contrast, negative net nitrogen mineralization rates were observed at −6°C possibly due to a more efficient N immobilization by tannins than N production by microbial activities, and suggesting a decoupling between C and N mineralization. Our results confirmed tannins and soil temperatures as relevant controls of microbial catabolism which are crucial for alpine ecosystems functioning and carbon storage.     

The influence of nematodes on below-ground processes in grassland ecosystems

This review summarises recent information on beneficial roles that soil nematodes play in the cycling of carbon and other plant nutrients in grassland ecosystems. In particular, we focus on the role of the two dominant functional groups of nematodes, namely the microbial- and root-feeders, and how their activities may enhance soil ecosystem-level processes of nutrient cycling and, ultimately, plant productivity in managed and unmanaged grassland ecosystems. We report recent experiments which show that low amounts of root herbivory by nematodes can increase the allocation of photoassimilate carbon to roots, leading to increased root exudation and microbial activity in the rhizosphere. The effects of these interactions on soil nutrient cycling and plant productivity are discussed. Evidence is presented to show that the feeding activities of microbial-feeding nematodes can enhance nutrient mineralization and plant nutrient uptake in grasslands, but that these responses are highly species-specific and appear to be strongly regulated by higher trophic groups of fauna (top-down regulation). We recommend that future studies of the roles of nematodes in grasslands ecosystems should consider these more complex trophic interactions and also the effects of species diversity of nematodes on soil ecosystem-level processes. This revised version was published online in June 2006 with corrections to the Cover Date.     

水分对武夷山草甸土壤有机碳激发效应的影响

水分是影响土壤有机碳激发效应的重要因子,但水分如何影响山地草甸土有机碳激发效应尚不清楚。本试验以武夷山高海拔(2130 m)山地草甸土为研究对象,通过室内添加¹³C标记的葡萄糖结合控制土壤水分(30%FWC和60%FWC,FWC为田间持水量),进行为期126 d的室内培养试验,定期测定CO₂浓度和¹³C-CO₂丰度值,研究不同水分条件下土壤有机碳矿化特征和激发效应的差异及其影响因素。结果表明: 山地草甸土碳矿化随着水分增加而增加。不同土壤水分山地草甸土激发效应随培养时间延长呈现逐渐降低的趋势,低含水量土壤激发效应显著大于高含水量土壤,培养结束时低含水量土壤累积激发碳量比高含水量土壤高61.4%。与低含水量土壤相比,高含水量土壤由葡萄糖矿化产生的CO₂量较多,且低含水量土壤的累积激发碳量与葡萄糖矿化量的比值显著大于高含水量土壤,说明高含水量土壤微生物更多地矿化外源添加的葡萄糖,且激发效率较低,最终高含水量土壤激发效应小于低含水量土壤。相关分析表明,土壤激发效应与土壤微生物生物量碳(MBC)、微生物生物量碳与氮比值(MBC/MBN)和NH₄⁺-N变化量呈显著正相关,说明低含水量条件会通过改变山地草甸土壤微生物数量和组成,进而提高土壤微生物对氮的“挖掘”,最终增加激发效应。因此,全球气候变化背景下若山地草甸土壤水分降低可能会增加通过激发效应引起的碳损失。     

Ecologically significant effects of Pseudomonas putida PPO301(pRO103), genetically engineered to degrade 2,4-dichlorophenoxyacetate, on microbial populations and processes in soil

Pseudomonas putida PPO301 (pRO103), genetically engineered to degrade 2,4-dichlorophenoxyacetate, affected microbial populations and processes in a nonsterile xeric soil. In soil amended with 2,4-dichlorophenoxyacetate (500 micrograms/g soil) and inoculated with PPO301 (pRO103), the rate of evolution of carbon dioxide was retarded for approximately 35 days; there was a transient increase in dehydrogenase activity; and the number of fungal propagules decreased below detection after 18 days. In unamended soil inoculated with PPO301(pRO103), the rate of evolution of carbon dioxide and the dehydrogenase activity were unaffected, and the numbers of fungal propagules were reduced by about two orders of magnitude. The numbers of total, spore-forming, and chitin-utilizing bacteria were reduced transiently in soil either amended or unamended with 2,4-dichlorophenoxyacetate and inoculated with PPO301(pRO103). The activities of arylsulfatases and phosphatases in soil were not affected by the presence of PPO301(pRO103), either in the presence or absence of 2,4-dichlorophenoxyacetate. In soil amended with 2,4-dichlorophenoxyacetate and inoculated with the parental strain (PPO301) or not inoculated, the evolution of carbon dioxide, the numbers of fungal propagules and of total, spore-forming, and chitin-utilizing bacteria, and the dehydrogenase activity were not affected as in soil inoculated with PPO301(pRO103). These results demonstrated that a genetically engineered microorganism, in the presence of the substrate on which its novel genes can function, is capable of inducing measurable ecological effects in soil.     

The influence of western hemlock and western redcedar on microbial numbers,nitrogen mineralization,and nitrification

Summary Microbial numbers in the forest floor and mineral soil (Al horizon) under large individual western hemlock (Tsuga heterophylla) and western redcedar (Thuja plicata) trees were compared. The lower pH and base saturation of hemlock samples was associated with higher fungal spore counts while cedar samples had higher total microbial counts and populations of ammonium oxidizing bacteria. Nitrogen mineralization rates were greater in laboratory incubations of hemlock soil but nitrification was only observed in incubations of cedar soil. These differences in nitrogen mineralization and nitrification are aspects of species-specific nutrient cycling regimes.     

Impacts of chronic nitrogen additions vary seasonally and by microbial functional group in tundra soils

Previous studies have shown that fertilization with nitrogen depresses overall microbial biomass and activity in soil. In the present study we broaden our understanding of this phenomenon by studying the seasonality of responses of specific microbial functional groups to chronic nitrogen additions in alpine tundra soils. We measured soil enzyme activities, mineralization kinetics for 8 substrates, biomass of 8 microbial functional groups, and changes in N and carbon pools in the soil. Our approach allowed us to compare the ability of the soil microbial biomass to utilize various substrates in addition to allowing us to estimate changes in biomass of microbial functional groups that are involved in carbon and nitrogen cycling. Overall microbial activity and biomass was reduced in fertilized plots, whereas pools of N in the soil and microbial biomass N were higher in fertilized plots. The negative effects of N were most prominent in the summer. Biomass of the dominant microbial functional groups recovered in fertilized soils during the winter and nitrogen storage in microbial biomass was higher in fertilized soils in the autumn and winter than in the summer. Microbial immobilization of N may therefore be a significant sink for added N during autumn and winter months when plants are not active. One large microbial group that did not recover in the winter in fertilized soils was phenol mineralizers, possibly indicating selection against microbes with enzyme systems for the breakdown of phenolic compounds and complex soil organic matter. Overall, this work is a step towards understanding how chronic N additions affect the structure and biogeochemical functioning of soil microbial communities.     

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。