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南亚热带不同树种人工林生态系统碳氮特征研究
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摘要
20世纪80年代,在我国热带和亚热带地区发起了大规模的造林运动,对退化荒坡进行生态恢复。然而在我国热带和亚热带林区造林恢复过程中,普遍存在着人工针叶纯林所占比重较大,由此引起生态稳定性较差、生态服务功能低、易受病虫害的攻击等一系列的问题。为了减少这些针叶人工纯林所带来的不利影响,许多不同功能型的阔叶树种(如速生树种和乡土珍贵树种,固氮树种和非固氮树种等)用于改造人工林经营模式已成为我国该地区人工林经营的发展趋势。关于不同功能型乡土珍贵阔叶树种,人们更多的是关注其木材收益,缺乏对其人工林生态系统碳氮特征的研究。本研究以中国林业科学研究院热带林业实验中心为研究地点,选取立地条件、林龄和经营历史相似的南亚热带不同树种人工林:格木(Erythrophleum fordii)人工林、红椎(Castanopsis hystrix)人工林和马尾松(Pinus massoniana)人工林,主要运用常规理化实验分析方法、气压过程分离技术(BaPS)、磷脂脂肪酸法(PLFA)和凋落物分解袋法,研究了:(1)不同树种人工林生态系统不同组分碳氮储量及其分配格局;(2)不同树种人工林土壤碳、氮元素转化的基本规律及其环境响应;(3)不同树种人工林土壤微生物群落结构组成及其对土壤碳氮转化的影响;(4)不同树种凋落物叶和细根分解特征及其相关关系。主要目的是通过对南亚热带不同树种人工林生态系统碳氮特征的比较研究,以期能为该区人工林营建中的树种选择以及人工碳汇林的经营管理提供科学参考。主要研究结果如下:
     (1)不同树种人工林乔木层各器官碳的分布与器官年龄的关系不明显,而氮的分布与器官年龄的关系则较为密切,表现为幼嫩器官中的氮含量大于老化器官,而老化器官的C/N比值大于幼嫩器官。说明碳具有相对稳定性,而氮具有流动性,并且氮素对幼嫩器官的生长具有重要作用。由于树种不同,其土壤有机碳和全氮含量具有显著差异,表土层有机碳和全氮含量均是乡土固氮树种格木林表现为最高,其次是红椎林,说明在本研究区乡土阔叶树种是最具有潜力的土壤改良树种。格木、红椎和马尾松人工林生态系统碳储量分别为236.22t·hm~(-2)、267.84t·hm~(-2)和200.57t·hm~(-2),氮储量分别为17.91t·hm~(-2)、12.38t·hm~(-2)和10.59t·hm~(-2)。乔木层碳储量分别占42.57%、36.31%和40.28%,0~(-1)00cm土壤碳储量分别占55.77%、62.52%和57.83%;氮储量则是土壤占绝对优势,分别为92.00%、93.72%和95.53%。以上结果表明,在本研究区乡土阔叶树种人工林具有较高的碳氮储存量。
     (2)不同树种人工林土壤呼吸及土壤总硝化表现出明显的季节变化,且雨季碳、氮转化速率显著高于干季。所有林分土壤呼吸及土壤总硝化的季节动态变化很大程度上依赖于土壤温度和土壤水分含量,土壤温度分别解释了土壤呼吸和土壤总硝化变异的76-86%和54-79%;土壤水分含量分别解释了土壤呼吸和土壤总硝化变异的31-56%和14-32%。由于不同树种对土壤环境的影响不同,不同林分间土壤呼吸速率及土壤总硝化速率存在显著差异。与其他两种林分相比,固氮树种格木林林下土壤具有较低的C/N比值和较高的有机碳含量、全氮含量及有效氮含量,因此,格木林土壤呼吸速率及总硝化速率显著高于红椎林和马尾松林。
     (3)不同树种人工林林分间土壤微生物生物量和土壤碳氮转化存在显著差异,土壤有机碳、全氮含量较高的乡土阔叶树种红椎林和格木林下土壤微生物生物量和总PLFAs量也较高,固氮树种格木林下土壤碳氮转化速率表现为最高,且由于格木林下土壤较低的C/N比和pH值,导致格木林下土壤真菌生物量显著低于其它两种林分。产生这种差异的主要原因是不同树种由于自身凋落物组分和质量的差异而改变土壤的化学性质、土壤微生物特征,从而影响土壤碳氮转化速率。从季节变化来看,不同林分下土壤微生物生物量均表现为干季大于雨季,而土壤碳氮转化速率却表现为雨季最大,造成这种格局的主要原因是雨季(植物生长的旺盛期)植物对土壤养分的大量需求限制了土壤微生物对养分的可利用性,因此减少了微生物生物量的固持。这也暗示了植物生长对养分的吸收与土壤微生物对体内养分的保持具有同步性。
     (4)格木、红椎和马尾松凋落物叶分解系数分别为0.98a~(-1)、0.88a~(-1)和0.62a~(-1),而细根分解系数则分别为0.65a~(-1)、0.59a~(-1)和0.47a~(-1)。不同树种对凋落物分解的影响不仅受凋落物自身化学性质的影响,还受不同树种林分内环境条件的影响,不同树种凋落物分解速率均与凋落物中氮含量呈正比,与C/N比、木质素/N比呈反比,与土壤水分含量的关系也较密切。不同树种凋落叶分解速率和细根分解速率表现出明显的正相关性,这归因于土壤水分含量和凋落叶、细根基质质量对凋落叶分解速率和细根分解速率的影响具有明显的相似性。
In the1980s, China’s tropical and subtropical regions launched a massive afforestationcampaign for ecological restoration of degraded slopes. In tropical and subtropical area ofChina, most of the plantations are composed of pure coniferous species. These pure coniferousspecies caused a series of problems, such as low ecosystem service and ecological instability,susceptible to pests and diseases attack.
     Many different functional hardwood species (such as fast-growing tree species and nativevaluable tree species, nitrogen-fixing and non-fixing tree species) are being advocated as aprospective silvicultural management to substitute large coniferous plantations in subtropicalChina. However, to different functional native hardwood species, people often pay moreattention to their timber income, little information is known about characteristics of ecosystemcarbon and nitrogen.
     In Tropical Forestry Experimental Center of Chinese Academy of Forestry Science, thethree adjacent monospecific plantations were selected to examine carbon and nitrogen storageunder different plantations, the effects of environmental factors on the transformation of carbonand nitrogen, the effects of soil microbial biomass and community composition on thetransformation of carbon and nitrogen, and the decomposition of leaf litter and fine root ofdifferent functional species, by using elemental analysis, barometric process separation (BaPS),phospholipid fatty acid (PLFA), and litter/root decomposition bags methods. One coniferousplantation was composed of Pinus massoniana, and the other broadleaf plantations wereErythrophleum fordii and Castanopsis hystrix. The main results are as follows:
     (1) The allocation of carbon in the organs of the different tree species had no significantcorrelation with their age, while that of nitrogen had closer relationship with the age. Thenitrogen concentration in young organs was higher than that in aged ones and the C/N ratio was higher in aged organs than that in young ones. It means that carbon is relatively stable, andnitrogen has an important role in the growth of young organs. Variations in soil organic carbonand total nitrogen among tree species could be primarily explained by the differentcharacteristics of tree species. The soil organic carbon and total nitrogen concentration werethe highest under the nitrogen-fixing species (E. fordii plantation), followed by C. hystrixplantations, suggesting that indigenous broadleaf tree species in this study area are the mostpotential species for soil amelioration. The total ecosystem carbon storage of E. fordii, C.hystrix and P. massoniana plantations was236.22t·hm~(-2),267.84t·hm~(-2)and200.57t·hm~(-2)andnitrogen storage was17.91t·hm~(-2),12.38t·hm~(-2)and10.59t·hm~(-2)respectively. Carbon storageof tree layer occupied42.57%,36.31%and40.28%while0~(-1)00cm soil occupied55.77%,62.52%and57.83%, respectively. Nitrogen storage of soil occupied92.00%,93.72%and95.53%. Our study indicated that the higher carbon and nitrogen sequestration ability in thenative broadleaf plantations.
     (2) Soil respiration and gross nitrification at all three plantations showed a pronouncedseasonal pattern with significantly higher rates during the wet versus dry season. Seasonalvariations of soil respiration and gross nitrification of the three plantations largely depended onsoil temperature and water content. Regression analysis showed that soil temperature explained76-86and54-79percent of the observed variance of soil respiration and gross nitrification,respectively, and soil water content explained31-56and14-32percent of the observedvariance of soil respiration and gross nitrification, respectively. The significant differences insoil respiration and gross nitrification rates between the three plantations could also beattributed to the influences of the tree species on the soil environment. Soil respiration andgross nitrification rates of the E. fordii plantation were much higher than those of the other twoplantations. These differences probably reflect the narrower C/N ratio and higher organic Ccontents in the soils of the E. fordii plantation.
     (3) The soil microbial community composition and the effects of soil microbialcommunity composition on the transformation of carbon and nitrogen were investigated in south subtropical plantations, in China. The results showed that the soil microbial biomass andsoil microbial community composition and C, N turnover rates were significantly influencedby plantation type. The soil organic carbon, total nitrogen, microbial biomass and total PLFAswere higher under the native broadleaf plantations, the highest turnover rates of C and N werefound under the soil of E. fordii plantation. Moreover, we found that the highest C and Nturnover rates coincided with the lowest fungal biomass could be primarily explained by thelower C/N ratio and pH value in E. fordii plantation. We also found the lowest microbialbiomass during the wet season, during the period of the lowest microbial biomass, however, weobserved the highest soil respiration and gross nitrification rates. These differences could bemostly attributed to the relatively greater nutrient demand by plants during the wet season (thepeak vegetative growth period) limited the availability of nutrients to soil microbes and therebyreduced their immobilization in microbial biomass. This also implies that the plant absorbnutrients for growth and soil microorganisms immobilize nutrients for microbial biomasswhich the two processes occur concurrently.
     (4) Decomposition parameter of leaf litter of E. fordii, C. hystrix and P. massoniana was0.98year~(-1),0.88year~(-1)and0.62year~(-1)and decomposition parameter of fine root was0.65year~(-1),0.59year~(-1)and0.47year~(-1), respectively. Decomposition rates of leaf litter and fine root wereinfluenced not only by the chemical properties of the litter, but also by the environmentalfactors in different plantations. The leaf litter and fine root decomposition rates showedsignificant similarity among tree species. Leaf litter and fine root decomposition rates in threestands were positively correlated with nitrogen content and soil water content, negativelycorrelated with C/N ratio, lignin/N ratio. The significant correlation between leaf litter and fineroot decomposition rates could also be attributed to soil water content and chemical propertiesof the litter on decomposition rates of leaf litter and fine root were very similar.
引文
Aerts R, Callaghan TV, Dorrepaal E, et al. Seasonal climate manipulations have only minor effects on litterdecomposition rates and N dynamics but strong effects on litter P dynamics of sub-arctic bog species.Oecologia,2012,170:809-819
    Aerts R, De Caluwe H. Nutritional and plant mediated controls on leaf litter decomposition of Carex species.Ecology,1997,78:244-260
    Aerts R. Climate, leaf litter chemistry and leaf litter decomposition in terrestrial ecosystems: a triangularrelationship. Oikos,1997:439-449
    Arunachalam A, Maithani K, Pandey HN, et al. Leaf litter decomposition and nutrient mineralizationpatterns in regrowing stands of a humid subtropical forest after tree cutting. Forest Ecology andManagement,1998,109:151-161
    Augusto L, Ranger J, Binkley D, et al. Impact of several common tree species of European temperate forestson soil fertility. Annals of Forest Science,2002,59:233-253
    Austin AT, Ballaré CL. Dual role of lignin in plant litter decomposition in terrestrial ecosystems. PNAS,2010,107:4618-4622
    Austin AT, Vitousek PM. Precipitation, decomposition and litter decomposability of Metrosiderospolymorpha in native forest on Hawai’i. Journal of Ecology,2000,88:129-138
    B th E, Anderson TH. Comparison of soil fungal/bacterial ratios in a pH gradient using physiological andPLFA-based techniques. Soil Biology and Biochemistry,2003,35:955-963
    Balser TC, Firestone MK. Linking microbial community composition and soil processes in a Californiaannual grassland and mixed-conifer forest. Biogeochemistry,2005,73:395-415
    Barbhuiya AR, Arunachalam A, Pandey HN, et al. Dynamics of soil microbial biomass C, N and P indisturbed and undisturbed stands of a tropical wet-evergreen forest. European Journal of Soil Biology,2004,40:113-121
    Bardgett RD, Frankland JC, Whittaker JB. The effects of agricultural management on the soil biota of someupland grasslands. Agriculture, Ecosystems and Environment,1993,45:25-45
    Bardgett RD, Hobbs PJ, Frosteg rd. Changes in soil fungal:bacterial biomass ratios following reductionsin the intensity of management of an upland grassland. Biology and Fertility of Soils,1996,22:261-264
    Bartelt-Ryser J, Joshi J, Schmid B, et al. Soil feedbacks of plant diversity on soil microbial communities andsubsequent plant growth. Perspectives in Plant Ecology, Evolution and Systematics,2005,7:27-49
    Batjes NH. Total carbon and nitrogen in the soils of the world. European Journal of Soil Science,1996,47:151-163
    Bauhus J, Paré D, Coté L. Effects of tree species, stand age and soil type on soil microbial biomass and itsactivity in a southern boreal forest. Soil Biology and Biochemistry,1998,30:1077-1089
    Bengtson P, Falkengren-Grerup U, Bengtsson G. Relieving substrate limitation-soil moisture and temperaturedetermine gross N transformation rates. Oikos,2005,111:81-90
    Berg B, Berg MP, Bottner P, et al. Litter mass loss rates in pine forests of Europe and Eastern United States:some relationships with climate and litter quality. Biogeochemistry,1993,20:127-159
    Berg B, Matzner E. Effect of N deposition on decomposition of plant litter and soil organic matter in forestsystems. Environmental Reviews,1997,5:1-25
    Berg B. Litter decomposition and organic matter turnover in northern forest soils. Forest Ecology andManagement,2000,133:13-22
    Binkley D, Giardina C, Bashkin MA. Soil phosphorus pools and supply under the influence of Eucalyptussaligna and nitrogen-fixing Albizia facaltaria. Forest Ecology and Management,2000,128:241-247
    Binkley D, Giardina C. Why do tree species affect soils? The warp and woof of tree-soil interactions.Biogeochemistry,1998,42:89-106
    Bligh EG, Dyer WJ. A rapid method of total lipid extraction and purification. Canadian journal ofbiochemistry and physiology,1959,37:911-917
    Borken W, Beese F. Methane and nitrous oxide fluxes of soils in pure and mixed stands of European beechand Norway spruce. European Journal of Soil Science,2006,57:617-625
    Borken W, Matzner E. Reappraisal of drying and wetting effects on C and N mineralization and fluxes insoils. Global Change Biology,2009,15:808-824
    Bossio DA, Scow KM. Impacts of carbon and flooding on soil microbial communities: phospholipid fattyacid profiles and substrate utilization patterns. Microbial Ecology,1998,35:265-278
    Boyle SA, Yarwood RR, Bottomley PJ, et al. Bacterial and fungal contributions to soil nitrogen cyclingunder Douglas fir and red alder at two sites in Oregon. Soil Biology and Biochemistry,2008,40:443-451
    Bremner JM. Nitrogen-total, in: Sparks, D.L.(Ed.), Methods of Soil Analysis. SSSA Book Ser., Madison,Wisconsin,1996,1085-1122
    Breuer L, Kiese R, Butterbach-Bahl K. Temperature and moisture effects on nitrification rates in tropicalrain-forest soils. Soil Science Society of America Journal,2002,66:834-844
    Brookes PC. The use of microbial parameters in monitoring soil pollution by heavy metals. Biology andFertility of Soils,1995,19:269-279
    Brüggemann N, Rosenkranz P, Papen H, et al. Pure stands of temperate forest tree species modify soilrespiration and N turnover. Biogeosciences Discussions,2005,2:303-331
    Burton AJ, Pregitzer KS. Field measurements of root respiration indicate little to no seasonal temperatureacclimation for sugar maple and red pine. Tree Physiology,2003,23:273-280
    Campbell JL, Sun OJ, Law BE. Supply-side controls on soil respiration among Oregon forests. GlobalChange Biology,2004,10:1857-1869
    Cao YS, Fu SL, Zou XM, et al. Soil microbial community composition under Eucalyptus plantations ofdifferent age in subtropical China. European Journal of Soil Biology,2010,46:128-135
    Carnevale NJ, Montagnini F. Facilitating regeneration of secondary forests with the use of mixed and pureplantations of indigenous tree species. Forest Ecology and Management,2002,163:217-227
    Chapin III FS, Matson PA, Mooney HA. Principles of Terrestrial Ecosystem Ecology. New York: Springer,2002
    Chen CR, Xu ZH, Blumfield TJ, et al. Soil microbial biomass during the early establishment of hoop pineplantation: seasonal variation and impacts of site preparation. Forest Ecology and Management,2003,186:213-225
    Chen H, Harmon ME, Sexton J, et al. Fine root decomposition and N dynamic in coniferous forests of thePacific Northwest, USA. Canadian Journal of Forest Research,2002,32:320-331
    Chen YT, Borken W, Stange CF, et al. Effects of decreasing water potential on gross ammonification andnitrification in an acid coniferous forest soil. Soil Biology and Biochemistry,2011,43:333-338
    Cotrufo MF, Ineson P. Effects of enhanced atmospheric CO2and nutrient supply on the quality andsubsequent decomposition of fine roots of Betula pendula Roth. and Picea sitchensis (Bong.) Carr.Plant and Soil,1995,170:267-277
    Cusack DF, Chou WW, Yang WH, et al. Controls on long-term root and leaf litter decomposition inneotropical forests. Global Change Biology,2009,15:1339-1355
    Das AK, Boral L, Tripathi RS, et al. Nitrogen mineralisation and microbial biomass-N in a subtropical humidforest of Meghalaya, India. Soil Biology and Biochemistry,1997,29:1609-1612
    Davidson EA, Hart SC, Firestone MK. Internal cycling of nitrate in soils of a mature coniferous forest.Ecology,1992,73:1148-1156
    Davidson EA, Hart SC, Shanks CA, et al. Measuring gross nitrogen mineralization, immobilization, andnitrification by15N isotopic pool dilution in intact soil cores. Journey of Soil Science,1991,42:335-349
    Dixon RK, Brown S, Houghton RA, et al. Carbon pools and flux of global forest ecosystems. Scienece,1994,263:185-190
    Drury CF, Mckenney DJ, Findlay WI. Relationships between denitrification, microbial biomass andindigenous soil properties. Soil Biology and Biochemistry,1991,23:751-755
    Ebermayer E. Die gesamte lehre der waldstreu mit rücksicht auf die chemische statik des waldbaues. Berlin:Springer.1876
    Eriksson KEL, Blanchette RA, Ander P. Microbial and enzymatic degradation of wood and woodcomponents. Berlin, Germany: Springer.1990
    FAO. State of The World’s Forests. Food and Agriculture Organization of the United Nations, Rome.2007
    Fierer N, Bradford MA, Jackson RB. Toward an ecological classification of soil bacteria. Ecology,2007,88:1354-1364
    Fierer N, Jackson RB. The diversity and biogeography of soil bacterial communities. Proceedings of theNational Academy of Sciences of the United States of America,2006,103:626-631
    Finér L, Mannerkoski H, Piirainen S, et al. Carbon and nitrogen pools in an old-growth, Norway sprucemixed forest in eastern Finland and changes associated with clear-cutting. Forest Ecology andManagement,2003,174:51-63
    Fioretto A, Musacchio A, Andolfi G, et al. Decomposition dynamics of litters of various pine species in aCorsican pine forest. Soil Biology and Biochemistry,1998,30:721-727
    Franzluebbers AJ. Water infiltration and soil structure related to organic matter and its stratification withdepth. Soil and Tillage Research,2002,66:197-205
    Fraterrigo JM, Balser TC, Turner MG. Microbial community variation and its relationship with nitrogenmineralization in historically altered forests. Ecology,2006,87:570-579
    Frosteg rd A, B th E. The use of phospholipid fatty acid analysis to estimate bacterial and fungal biomassin soil. Biology and Fertility of Soils,1996,22:59-65
    Frosteg rd, Tunlid A, B th E. Phospholipid fatty acid composition, biomass, and activity of microbialcommunities from two soil types experimentally exposed to different heavy metals. Applied andEnvironmental Microbiology,1993,59:3605-3617
    Frosteg rd A, Tunlid A, B th E. Use and misuse of PLFA measurements in soils. Soil Biology andBiochemistry,2011,43:1621-1625
    Galloway JN, Cowling EB. Reactive nitrogen and the world:200years of change. Ambio,2002,31:64-71
    Garcia-Pausas J, Casals P, Romanyà J. Litter decomposition and faunal activity in Mediterranean forest soils:effects of N content and the moss layer. Soil Biology and Biochemistry,2004,36:989-997
    Gessner MO. Functional leaf traits and biodiversity effects on litter decomposition in a stream: reply.Ecology,2010,91:1869-1871
    Gholz HL, Wedin DA, Smitherman SM, et al. Long-term dynamics of pine and hardwood litter incontrasting environments: toward a global model of decomposition. Global Change Biology,2000,6:75l-765
    Gijsman AJ, Alarcón HF, Thomas RJ. Root decomposition in tropical grasses and legumes, as affected bysoil texture and season. Soil Biology and Biochemistry,1997,29:1443-1450
    G dde M, Conrad R. Influence of soil properties on the turnover of nitric oxide and nitrous oxide bynitrification and denitrification at constant temperature and moisture. Biology and Fertility of Soils,2000,32:120-128
    Grabovich MY, Dubinina GA, Churikova VV, et al. Mechanisms of synthesis and utilization of oxalateinclusions in the colorless sulfur bacterium Macromonas bipunctata. Mikrobiologiya,1995,64:630-636
    Grayston SJ, Campbell CD, Bardgett RD, et al. Assessing shifts in microbial community structure across arange of grasslands of differing management intensity using CLPP, PLFA and community DNAtechniques. Applied Soil Ecology,2004,25:63-84
    Grayston SJ, Prescott CE. Microbial communities in forest floors under four tree species in coastal BritishColumbia. Soil Biology and Biochemistry,2005,37:1157-1167
    Grenon F, Bradley RL, Titus BD. Temperature sensitivity of mineral N transformation rates, andheterotrophic nitrification: possible factors controlling the post-disturbance mineral N flush in forestfloors. Soil Biology and Biochemistry,2004,36:1465-1474
    Güsewell S. N:P ratios in terrestrial plants: variation and functional significance. New Phytologist,2004,164:243-266
    Hackl E, Pfeffer M, Donat C, et al. Composition of the microbial communities in the mineral soil underdifferent types of natural forest. Soil Biology and Biochemistry,2005,37:661-671
    Hankinson TR, Schmidt EL. An acidophilic and a neutrophilic Nitrobacter strain isolated from thenumerically predominant nitrite-oxidizing population of an acid forest soil. Applied and EnvironmentalMicrobiology,1988,54:1536-1540
    H ttenschwiler S, Tiunov AV, Scheu S. Biodiversity and litter decomposition in terrestrial ecosystems.Annual Review of Ecology, Evolution, and Systematics,2005,36:191-218
    Hessen DO, Agren GI, Anerson TR, et al. Carbon sequestration in ecosystems: the role of stoichiometry.Ecology,2004,85:1179-1192
    Hobbie SE, Oleksyn J, Eissenstat DM, et al. Fine root decomposition rates do not mirror those of leaf litteramong temperate tree species. Oecologia,2010,162:505-513
    H gberg MN, B th E, Nordgren A, et al. Contrasting effects of nitrogen availability on plant carbon supplyto mycorrhizal fungi and saprotrophs-a hypothesis based on field observations in boreal forest. NewPhytologist,2003,160:225-238
    H gberg MN, H gberg P, Myrold DD. Is microbial community composition in boreal forest soils determinedby pH, C-to-N ratio, the trees, or all three? Oecologia,2007,150:590-601
    Horvath H, Habenreich TA, Kreiner I, et al. Temporal and spatial variations of the Vienna aerosol. Science ofthe Total Environment,1989,83:127-159
    Huang JJ, Wang XH, Yan ER. Leaf nutrient concentration, nutrient resorption and litter decomposition in anevergreen broad-leaved forest in eastern China. Forest Ecology and Management,2007,239:150-158
    Hunt HW, Wall DH. Modeling the effects of loss of soil biodiversity on ecosystem function. Global ChangeBiology,2002,8:33-50
    Ingwersen J, Butterbach-Bahl K, Gasche R, et al. Barometric process separation: new method forquantifying nitrification, denitrification, and nitrous oxide sources in soils. Soil Science Society ofAmerica Journal,1999,63:117-128
    Ingwersen J, Schwarz U, Stange CF, et al. Shortcomings in the commercialized barometric processseparation measuring system. Soil Science Society of America Journal,2008,72:135-142
    Janssens IA, Lankreijer H, Matteucci G, et al. Productivity overshadows temperature in determining soil andecosystem respiration across European forests. Global Change Biology,2001,7:269-278
    Joergensen RG, Brookes PC. Ninhydrin-reactive nitrogen measurements of microbial biomass in0.5mK2SO4soil extracts. Soil Biology and Biochemistry,1990,22:1023-1027
    Kao-Kniffin J, Balser TC. Soil fertility and the impact of exotic invasion on microbial communities inHawaiian forests. Microbial Ecology,2008,56:55-63
    Kieft T, Ringelberg DB, White DC. Changes in ester-linked phospholipid fatty acid profiles of subsurfacebacteria during starvation and desiccation in a porous medium. Applied and EnvironmentalMicrobiology,1994,60:3292-3299
    Kiese R, Hewett B, Butterbach-Bahl K. Seasonal dynamic of gross nitrification and N2O emission at twotropical rainforest sites in Queensland, Australia. Plant and Soil,2008,309:105-117
    Kiese R, Papen H, Zumbusch E, et al. Nitrification activity in tropical rain forest soils of the CoastalLowlands and Atherton Tablelands, Queensland, Australia. Journal of Plant Nutrition and Soil Science,2002,165:682-685
    Kitayama K. Soil nitrogen dynamics along a gradient of long-term soil development in a Hawaiian wetmontane rain forest. Plant and Soil,1996,183:253-262
    Kraus TEC, Zasoski RJ, Dahlgren RA, et al. Carbon and nitrogen dynamics in a forest soil amended withpurified tannins from different plant species. Soil Biology and Biochemistry,2004,36:309-321
    Lal R. Forest soils and carbon sequestration. Forest Ecology and Management,2005,220:242-258
    Leckie SE, Prescott CE, Grayston SJ, et al. Characterization of humus microbial communities in adjacentforest types that differ in nitrogen availability. Microbial Ecology,2004,48:29-40
    Li ZA, Peng SL, Rae DJ, et al. Litter decomposition and nitrogen mineralization of soils in subtropicalplantation forests of southern China, with special attention to comparisons between legumes andnon-legumes. Plant and Soil,2001,229:105-116
    Liang C, Fujinuma R, Wei LP, et al. Tree species-specific effects on soil microbial residues in an upperMichigan old-growth forest system. Forestry,2007,80:65-72
    Liu L, Gundersen P, Zhang T, et al. Effects of phosphorus addition on soil microbial biomass and communitycomposition in three forest types in tropical China. Soil Biology and Biochemistry,2012,44:31-38
    Lu XY, Yan Y, Fan JH, et al. Gross nitrification and denitrification in Alpine Grassland Ecosystems on theTibetan Plateau. Arctic, Antarctic, and Alpine Research,2012,44:188-196
    Luan JW, Liu SR, Wang JX, et al. Rhizospheric and heterotrophic respiration of a warm-temperate oakchronosequence in China. Soil Biology and Biochemistry,2011,43:503-512
    Maithani K, Tripathi RS, Arunachalam A, et al. Seasonal dynamics of microbial biomass C, N and P duringregrowth of a disturbed subtropical humid forest in north-east India. Applied Soil Ecology,1996,4:31-37
    Malhi Y, Grace J. Tropical forests and atmospheric carbon dioxide. Trends in Ecology and Evolution,2000,15:332-337
    Mallik AU, Hu D. Soil respiration following site preparation treatments in boreal mixedwood forest. ForestEcology and Management,1997,97:265-275
    Mao DM, Min YW, Yu LL, et al. Effect of afforestation on microbial biomass and activity in soils of tropicalChina. Soil Biology and Biochemistry,1992,24:865-872
    Martikainen PJ, De Boer W. Nitrous oxide production and nitrification in acidic soil from a dutch coniferousforest. Soil Biology and Biochemistry,1993,25:343-347
    Matejek B, Huber C, Dannenmann M, et al. Microbial nitrogen-turnover processes within the soil profile ofa nitrogen-saturated spruce forest and their relation to the small-scale pattern of seepage-water nitrate.Journal of plant nutrition and soil science,2010,173:224-236
    Matejek B, Kohlpaintner M, Gasche R, et al. The small-scale pattern of seepage water nitrate concentrationin an N saturated spruce forest is regulated by net N mineralization in the organic layer. Plant and Soil,2008,310:167-179
    McClaugherty CA, Berg B. Cellulose, lignin, and nitrogen concentrations as rate regulating factors in latestage of forest litter decomposition. Pedobiologia,1987,30:101-112
    McClaugherty CA, Pastor J, Aber JD, et al. Forest litter decomposition in relation to soil nitrogen dynamicsand litter quality. Ecology,1985,66:266-275
    McGroddy ME, Daufresne T, Hedin LO. Scaling of C:N:P stoichiometry in forests worldwide: implicationsof terrestrial Redfield-type ratios. Ecology,2004,85:2390-2401
    Meier CL, Bowman WD. Links between plant litter chemistry, species diversity, and below-groundecosystem function. Proceedings of the National Academy of Sciences,2008,105:19780-19785
    Melillo JM, Aber JD, Muratore JF. Nitrogen and lignin control of hardwood leaf litter decompositiondynamics. Ecology,1982,63:621-626
    Mendham DS, Sankaran KV, O’Connell AM, et al. Eucalyptus globulus harvest residue management effectson soil carbon and microbial biomass at1and5years after plantation establishment. Soil Biology andBiochemistry,2002,34:1903-1912
    Mo JM, Brown S, Xue JH, et al. Response of litter decomposition to simulated N deposition in disturbed,rehabilitated and mature forests in subtropical China. Plant and Soil,2006,282:135-151
    Moore TR, Trofymow JA, Prescott CE, et al. Patterns of carbon, nitrogen and phosphorus dynamics indecomposing foliar litter in Canadian forests. Ecosystems,2006,9:46-62
    Müller C, Abbasi MK, Kammann C, et al. Soil respiratory quotient determined via barometric processseparation combined with nitrogen-15labeling. Soil Science Society of America Journal,2004,68:1610-1615
    Munson AD, Timmer VR. Soil nitrogen dynamics and nutrition of pine following silvicultural treatments inboreal and Great Lakes-St. Lawrence plantations. Forest Ecology and Management,1995,76:169-179
    Myers RT, Zak DR, White DC, et al. Landscape-level patterns of microbial community composition andsubstrate use in upland forest ecosystems. Soil Science Society of America Journal,2001,65:359-367
    Neill C, Piccolo MC, Melillo JM, et al. Nitrogen dynamics in Amazon forest and pasture soils measured by15N pool dilution. Soil Biology and Biochemistry,1999,31:567-572
    Nelson DW, Sommers LE. Total Carbon, Organic Carbon, and Organic Matter, in: second ed.(Eds),Methods of Soil Analysis. American Society of Agronomy Inc., Madison, Wisconsin,1996,961-1010
    Nielsen LP, Glud RN. Denitrification in a coastal sediment measured in situ by the nitrogen isotope pairingtechnique applied to a benthic flux chamber. Marine Ecology Progress Series,1996,137:181-186
    Nilsson LO, Giesler R, B th E, et al. Growth and biomass of mycorrhizal mycelia in coniferous forestsalong short natural nutrient gradients. New Phytologist,2005,165:613-622
    Olson JS, Watts JA, Allison LJ. Carbon in live vegetation of major world ecosystems. Oak Ridge NationalLaboratory,1983
    Olson JS. Energy storage and the balance of producers and decomposers in ecological systems. Ecology,1963,44:322-331
    Olsson PA. Signature fatty acids provide tools for determination of the distribution and interactions ofmycorrhizal fungi in soil. FEMS Microbiology Ecology,1999,29:303-310
    Ostertag R, Marín-Spiotta E, Silver WL, et al. Litterfall and decomposition in relation to soil carbon poolsalong a secondary forest chronosequence in Puerto Rico. Ecosystems,2008,11:701-714
    Paavolainen L, Smolander A. Nitrification and denitrification in soil from a clear-cut Norway spruce (Piceaabies) stand. Soil Biology and Biochemistry,1998,30:775-781
    Paquette A, Messier C. The role of plantations in managing the World’S Forests in the Anthropocene.Frontiers in Ecology and the Environment,2010,8:27-34
    Pastor J, Post WM. Influence of climate, soil moisture, and succession on forest carbon and nitrogen cycles.Biogeochemistry,1986,2:3-27
    Patra AK, Abbadie L, Clays-Josserand A, et al. Effects of management regime and plant species on theenzyme activity and genetic structure of N-fixing, denitrifying and nitrifying bacterial communities ingrassland soils. Environmental Microbiology,2006,8:1005-1016
    Peng SL, Hou YP, Chen BM. Vegetation restoration and its effects on carbon balance in GuangdongProvince, China. Restoration Ecology,2009,17:487-494
    Porazinska DL, Bardgett RD, Blaauw MB, et al. Relationships at the aboveground-belowground interface:plants, soil biota, and soil processes. Ecological Monographs,2003,73:377-395
    Prescott CE, Vesterdal L, Pratt J, et al. Nutrient concentrations and nitrogen mineralization in forest floors ofsingle species conifer plantations in coastal British Columbia. Canadian Journal of Forest Research,2000,30:1341-1352
    Priha O, Grayston SJ, Hiukka R, et al. Microbial community structure and characteristics of the organicmatter in soils under Pinus sylvestris, Picea abies and Betula pendula at two forest sites. Biology andFertility of Soils,2001,33:17-24
    Priha O, Grayston SJ, Pennanen T, et al. Microbial activities related to C and N cycling and microbialcommunity structure in the rhizospheres of Pinus sylvestris, Picea abies and Betula pendula seedlingsin an organic and mineral soil. FEMS Microbiology Ecology,1999,30:187-199
    Priha O, Smolander A. Nitrogen transformations in soil under Pinus sylvestris, Picea abies and Betulapendula at two forest sites. Soil Biology and Biochemistry,1999,31:965-977
    Raghubanshi AS, Srivastava SC, Singh RS, et al. Nutrient release in leaf litter. Nature,1990,346:227
    Reich PB, Hobbie SE, Lee T, et al. Nitrogen limitation constrains sustainability of ecosystem response toCO2. Nature,2006,440:922-925
    Reich PB, Oleksyn J. Global patterns of plant leaf N and P in relation to temperature and latitude. PNASProceedings of the National Academy of Sciences of the United States of A merica,2004,101:11001-11006
    Ren H, Shen WJ, Lu HF, et al. Degraded ecosystems in China: status, causes, and restoration efforts.Landscape and Ecological Engineering,2007,3:1-13
    Rey A, Pegoraro E, Tedeschi V, et al. Annual variation in soil respiration and its components in a coppice oakforest in Central Italy. Global Change Biology,2002,8:851-866
    Riutta T, Slade EM, Bebber DP, et al. Experimental evidence for the interacting effects of forest edge,moisture and soil macrofauna on leaf litter decomposition. Soil Biology and Biochemistry,2012,49:124-131
    Rosenkranz P, Brüggemann N, Papen H, et al. Soil N and C trace gas fluxes and microbial soil N turnover ina sessile oak (Quercus petraea (Matt.) Liebl.) forest in Hungary. Plant and Soil,2006,286:301-322
    Rosenkranz P, Dannenmann M, Brüggemann N, et al. Gross rates of ammonification and nitrification at anitrogen-saturated spruce (Picea abies (L.) Karst.) stand in southern Germany. European Journal of SoilScience,2010,61:745-758
    Ross DS, Lawrence GB, Fredriksen G. Mineralization and nitrification patterns at eight northeastern USAforested research sites. Forest Ecology and Management,2004,188:317-335
    Rousk J, Brookes PC, B th E. The microbial PLFA composition as affected by pH in an arable soil. SoilBiology and Biochemistry,2010,42:516-520
    Ruan HH, Li YQ, Zou XM. Soil communities and plant litter decomposition as influenced by forest debris:Variation across tropical riparian and upland sites. Pedobiologia,2005,49:529-538
    Russell AE, Raich JW, Valverde-Barrantes OJ, et al. Tree species effects on soil properties in experimentalplantations in tropical moist forest. Soil Science Society of America Journal,2007,71:1389-1397
    Ryan MG, Melillo JM, Ricca AA. Comparison of methods for determining proximate carbon fractions offorest litter. Canadian Journal of Forest Research,1990,20:166-171
    Sanchez LF, Garcia-miragaya J, Chacon N. Nitrogen mineralization in soil under grasses and under trees in aprotected Venezuelan savanna. Acta Ecologia,1997,18:27-37
    Sarathchandra SU, Perrott KW, Upsdell MP. Microbiological and biochemical characteristics of a range ofNew Zealand soils under established pasture. Soil Biology and Biochemistry,1984,16:177-183
    Sariyildiz T, Anderson JM. Interactions between litter quality, decomposition and soil fertility: a laboratorystudy. Soil Biology and Biochemistry,2003,35:391-399
    Schimel J, Balser TC, Wallenstein M. Microbial stress-response physiology and its implications forecosystem function. Ecology,2007,88:1386-1394
    Schlesinger WH. Soil organic matter: a source of atmospheric CO2. In Woodwell GM(Ed) The role ofterrestrial vegetation in the global carbon cycle (pp111-127). John Wiley, New York,1984
    Schutter ME, Dick RP. Microbial community profiles and activities among aggregates of winter fallow andcover-cropped soil. Soil Science Society of American Journal,2002,66:142-153
    Scott NA, Binkley D. Foliage litter quality and annual net N mineralization: comparison across NorthAmerican Forest Sites. Oecologia,1997,111:151-159
    Scott-Denton LE, Sparks KL, Monson RK. Spatial and temporal controls of soil respiration rate in ahigh-elevation, subalpine forest. Soil Biology and Biochemistry,2003,35:525-534
    SFA (State Forestry Administration) China’s Forestry1999-2005. China Forestry Publishing House, Beijing.2007
    Silver WL, Miya RK. Global patterns in root decomposition: comparisons of climate and litter quality effects.Oecologia,2001,129:407-419
    Singh JS, Raghubanshi AS, Singh RS, et al. Microbial biomass acts as a source of plant nutrients in drytropical forest and savanna. Nature,1989,338:499-500
    Singh RS, Srivastava SC, Raghubanshi AS, et al. Microbial C, N and P in dry tropical savanna: effects ofburning and grazing. Journal of Applied Ecology,1991,28:869-878
    Singh S, Ghoshal N, Singh KP. Variations in soil microbial biomass and crop roots due to differing resourcequality inputs in a tropical dryland agroecosystem. Soil Biology and Biochemistry,2007,39:76-86
    Sinsabaugh RL, Antibus RK, Linkins AE, et al. Wood decomposition: nitrogen and phosphorus dynamics inrelation to extracellular enzyme activity. Ecology,1993,74:1586-1593
    Sinsabaugh RL, Gallo ME, Lauber C, et al. Extracellular enzyme activities and soil organic matter dynamicsfor Northern hardwood forests receiving simulated nitrogen deposition. Biogeochemistry,2005,75:201-215
    Six J, Frey SD, Thiet RK, et al. Bacterial and fungal contributions to carbon sequestration in agroecosystems.Soil Science Society of America Journal,2006,70:555-569
    Smolander A, Kitunen V. Soil microbial activities and characteristics of dissolved organic C and N inrelation to tree species. Soil Biology and Biochemistry,2002,34:651-660
    Soil Survey Staff of USDA. Keys to soil taxonomy. United States Department of Agriculture (USDA),Natural Resources Conservation Service, Washington, DC,2006
    Staelens J, Rütting T, Huygens D, et al. In situ gross nitrogen transformations differ between temperatedeciduous and coniferous forest soils. Biogeochemistry,2012,108:259-277
    Stange CF, Neue H-U. Measuring and modelling seasonal variation of gross nitrification rates in response tolong-term fertilisation. Biogeosciences,2009,6:2181-2192
    Stark JM, Firestone MK. Mechanisms for soil moisture effects on activity of nitrifying bacteria. Applied andEnvironmental Microbiology,1995,61:218-221
    Stark JM, Hart SC. High rates of nitrification and nitrate turnover in undisturbed coniferous forests. Nature,1997,385:61-64
    Ste-Marie C, Houle D. Forest floor gross and net nitrogen mineralization in three forest types in Quebec,Canada. Soil Biology and Biochemistry,2006,38:2135-2143
    Stroo HF, Klein TM, Alexander M. Heterotrophic nitrification in an acid forest soil and by an acid-tolerantfungus. Applied and Environmental Microbiology,1986,52:1107-1111
    Taylor BR, Parkinson D, Parsons WFJ. Nitrogen and lignin content as predictor of litter decay rates: amicrocosm test. Ecology,1989,70:97-104
    Taylor BR, Prescott CE, Parsons WJF, et al. Substrate control of litter decomposition in four RockyMountain coniferous forests. Canadian Journal of Botany,1991,69:2242-2250
    Templer P, Findlay S, Lovett G. Soil microbial biomass and nitrogen transformations among five tree speciesof the Catskill Mountains, New York, USA. Soil Biology and Biochemistry,2003,35:607-613
    Thevenot M, Dignac MF, Rumpel C. Fate of lignins in soils: A review. Soil Biology and Biochemistry,2010,42:1200-1211
    Thompson JA, Kolka RK. Soil carbon storage estimation in a forested watershed using quantitativesoil-landscape modeling. Soil Science Society of America Journal,2005,69:1086-1093
    Tian G. Soil fauna-mediated decomposition of plant residues under constrained environment and residuequality conditions. IN: Cadisch G, Giller K E. Driven by nature: plant litter quality and decomposition.Wallingford: CAB International,1997,125-144
    Torbert HA, Wood CW. Effects of soil compaction and water-filled pore space on soil microbial activity andN losses. Communications in Soil Science and Plant Analysis,1992,23:1321-1331
    Treseder KK. A meta-analysis of mycorrhizal responses to nitrogen, phosphorus, and atmospheric CO2infield studies. New Phytologist,2004,164:347-355
    Tunlid A, Hoitink HAJ, Low C, et al. Characterization of bacteria that suppress rhizoctonia damping-off inbark compost media by analysis of fatty acid biomarkers. Applied and Environmental Microbiology,1989,55:1368-1374
    Ushio M, Wagai R, Balser TC, et al. Variations in the soil microbial community composition of a tropicalmontane forest ecosystem: Does tree species matter? Soil Biology and Biochemistry,2008,40:2699-2702
    Valá ková V, najdr J, Bittner B, et al. Production of lignocellulose-degrading enzymes and degradation ofleaf litter by saprotrophic basidiomycetes isolated from a Quercus petraea forest. Soil Biology andBiochemistry,2007,39:2651-2660
    Venterea RT, Groffman PM, Verchot LV, et al. Gross nitrogen process rates in temperate forest soilsexhibiting symptoms of nitrogen saturation. Forest Ecology and Management,2004,196:129-142
    Verchot LV, Holmes Z, Mulon L, et al. Gross vs net rates of N mineralization and nitrification as indicatorsof functional differences between forest types. Soil Biology and Biochemistry,2001,33:1889-1901
    Vitousek PM. Beyond Global Warming: Ecology and Global Change. Ecology,1994,75:1861-1876
    Vivanco L, Austin AT. Intrinsic effects of species on leaf litter and root decomposition: a comparison oftemperate grasses from North and South America. Oecologia,2006,150:97-107
    Vivanco L, Austin AT. Tree species identity alters forest litter decomposition through long-term plant andsoil interactions in Patagonia, Argentina. Journal of Ecology,2008,96:727-736
    Wallenda T, Kottke I. Nitrogen deposition and ectomycorrhizas. New Phytologist,1998,139:169-187
    Wang FM, Li ZA, Xia HP, et al. Effects of nitrogen-fixing and non-nitrogen-fixing tree species on soilproperties and nitrogen transformation during forest restoration in southern China. Soil Science andPlant Nutrition,2010,56:297-306
    Wang H, Liu SR, Mo JM, et al. Soil organic carbon stock and chemical composition in four plantations ofindigenous tree species in subtropical China. Ecological Research,2010,25:1071-1079
    Wang H, Liu SR, Mo JM. Correlation between leaf litter and fine root decomposition among subtropical treespecies. Plant and soil,2010,335:289-298
    Wardle DA. A comparative assessment of factors which influence microbial biomass carbon and nitrogenlevels in soil. Biological Reviews,1992,67:321-358
    Westbrook CJ, Devito KJ, Allan CJ. Soil N cycling in harvested and pristine boreal forests and peatlands.Forest Ecology and Management,2006,234:227-237
    Willcock J, Magan N. Impact of environmental factors on fungal respiration and dry matter losses in wheatstraw. Journal of Stored Products Research,2000,37:35-45
    Wright IJ, Reich PB, Westoby M, et al. The worldwide leaf economics spectrum. Nature,2004,428:821-827
    Wu J, Joergensen RG, Pommerening B, et al. Measurement of soil microbial biomass C byfumigation-extraction-an automated procedure. Soil Biology and Biochemistry,1990,22:1167-1169
    Wu JP, Liu ZF, Wang XL, et al. Effects of understory removal and tree girdling on soil microbial community composition and litter decomposition in two Eucalyptus plantations in South China. Functional Ecology,2011,25:921-931
    Xu XN, Hirata EJ. Decomposition patterns of leaf litter of seven common canopy species in a subtropical forest:N and P dynamics. Plant and Soil,2005,273:279-289
    Yao H, He Z, Wilson MJ, et al. Microbial biomass and community structure in a sequence of soils with increasing fertility and changing land use. Microbial Ecology,2000,40:223-237
    Yin HJ, Chen Z, Liu Q. Effects of experimental warming on soil N transformations of two coniferous species, Eastern Tibetan Plateau, China. Soil Biology and Biochemistry,2012,50:77-84
    Yoshitake S, Uchida M, Nakatsubo T, et al. Characterization of soil microflora on a successional glacier foreland in the High Arctic on Ellesmere Island, Nunavut, Canada using phospholipid fatty acid analysis. Polar Bioscience,2006,19:73-84
    Zelles L. Fatty acid patterns of phospholipids and lipopolysaccharides in the characterisation of microbial communities in soil:a review. Biology and Fertility of Soils,1999,29:111-129
    Zhang XL, Wang QB, Li LH, et al. Seasonal variations in nitrogen mineralization under three land use types in a grassland landscape. Acta Oecologica,2008,34:322-330
    Zogg GP, Zak DR, Ringelberg DB, et al. Compositional and functional shifts in microbial communities due to soil warming. Soil Science Society of America Journal,1997,61:475-481
    曹吉鑫.北京北部山区不同林龄的油松和侧柏人工林碳库研究.北京林业大学博士论文,2011
    陈瑾,李扬,黄建辉.内蒙古典型草原4种优势植物凋落物的混合分解研究.植物生态学报,2011,35:9-16
    谌小勇,潘维俦.杉木人工林生态系统中氮素的动态特征.生态学报,1989,9:201-206
    方精云,陈安平.中国森林植被碳库的动态变化及其意义.植物学报,2001,43:967-973
    方晰,田大伦,项文化.不同经营方式对杉木林采伐迹地土壤C储量的影响.中南林学院学报,2004,24:1-5
    葛晓改.三峡库区马尾松林凋落物分解及对土壤碳库动态的影响研究.中国林业科学研究院博士论文,2012
    郭剑芬,杨玉盛,陈光水,等.森林凋落物分解研究进展.林业科学,2006,42:93-100
    何斌,刘运华,余浩光,等.南宁马占相思人工林生态系统碳素密度与贮量.林业科学,2009,45:6-11
    胡婵娟,刘国华,吴雅琼.土壤微生物生物量及多样性测定方法评述.生态环境学报,2011,20:1161-1167
    黄从德.四川森林生态系统碳储量及其空间分异特征.四川农业大学博士论文,2008
    黄宇,冯宗炜,汪思龙,等.杉木,火力楠纯林及其混交林生态系统C,N贮量.生态学报,2005,25:3146-3154
    焦秀梅,项文化,田大伦.湖南省森林植被的碳贮量及其地理分布规律.中南林学院学报,2005,25:4-8
    焦燕,胡海清.黑龙江省森林植被碳储量及其动态变化.应用生态学报,2005,16:2248-2252
    金钊,杨玉盛,董云社,等.2007.福建万木林自然保护区米槠和杉木细根分解动态.地理研究,2007,26:491-499
    康冰,刘世荣,张广军,等.广西大青山南亚热带马尾松,杉木混交林生态系统碳素积累和分配特征.生态学报,2006,26:1320-1329
    李海涛,王珊娜,高鲁鹏,等.赣中亚热带森林植被碳储量.生态学报,2007,27:0693-0704
    李克让,王绍强,曹明奎.中国植被和土壤碳贮量.中国科学(D辑),2003,33:72-80
    李铭红,于明坚,陈启瑞,等.青冈常绿阔叶林的碳素动态.生态学报,1996,16:645-651
    李玉中,祝廷成,Redmann RE.三种利用类型羊草草地氮总矿化、硝化和无机氮消耗速率的比较研究.生态学报,2002,22:668-673
    李跃林,胡成志,张云,等.几种人工林土壤碳储量研究.福建林业科技,2004,31:4-7
    李志安,邹碧,丁永祯,等.森林凋落物分解重要影响因子及其研究进展.生态学杂志,2004,23:77-83
    梁瑞龙.广西乡土阔叶树种资源现状及其发展对策.广西林业科学,2007,36:5-9
    林启美,吴玉光,刘焕龙.熏蒸法测定土壤微生物量碳的改进.生态学杂志,1999,18:63-66
    林生,庄家强,陈婷,等.不同年限茶树根际土壤微生物群落PLFA生物标记多样性分析.生态学杂志,2013,32:64-71
    刘恩,王晖,刘世荣.南亚热带不同林龄红锥人工林碳贮量与碳固定特征.应用生态学报,2012,23:335-340
    .—.:
    ,1996
    ,,,..,2004,43:86-89
    . BaPS-.,2005
    ,,,..,
    2006,12:500-505
    ..,2005
    ,,,..: V,
    2007,34:129-134
    ..:,2000
    ,,,..
    ,2000,13:123-128
    ,,,. V.,2010,
    16:519-522
    ,,,.28.,2012,
    31:1050-1056
    ,,,..,2012,31:794-799
    ..:,1998
    ,,.—.,1997,
    16:17-21
    ,.,.,2002,22:220-228
    ,,..,2005,29:
    304-310
    ..: V.:
    ,1999
    ,,,..
    ,2008,19:37-42
    王华,黄宇,汪思龙,等.中亚热带几种典型森林生态系统碳、氮储存功能研究.中国生态农业学报,2010,18:576-580
    王晖.南亚热带四种人工林土壤碳固持及其主要相关过程研究.中国林业科学研究院博士论文,2010
    王瑾.森林生态系统中养分循环特征的比较研究.中国科学院植物研究所硕士论文,2002
    王其兵,李凌浩,白永飞,等.模拟气候变化对3种草原植物群落混合凋落物分解的影响.植物生态学报,2000,24:674-679
    王卫霞,史作民,罗达,等.我国南亚热带几种人工林生态系统碳氮储量研究,生态学报,2013,33:925-933
    王希华,黄建军,闫思荣.天童国家森林公园常见植物凋落叶分解的研究.植物生态学报,2004,28:457-467
    吴海斌.末次盛冰期以来中国陆地生态系统碳储量变化研究.中国科学院地质与地球物理研究所博士论文,2002
    项文化,田大伦.不同年龄阶段马尾松人工林养分循环的研究.植物生态学报,2002,26:89-95
    徐德应.人类经营活动对森林土壤碳的影响.世界林业研究,1994,5:26-32
    徐国良,莫江明,周国逸.模拟氮沉降增加对南亚热带主要森林土壤动物的早期影响.应用生态学报,2005,16:1235-1240
    徐继荣,王友绍,殷建平,等.珠江口入海河段DIN形态转化与硝化和反硝化作用.环境科学学报,2005,25:686-692
    徐新良,曹明奎,李克让.中国森林生态系统植被碳储量时空动态变化研究.地理科学进展,2007,26:5-7
    徐振锋,尹华军,赵春章,等.陆地生态系统凋落物分解对全球气候变暖的响应.植物生态学报,2009,33:1208-1219
    杨洪晓,吴波,张金屯,等.森林生态系统的固碳功能和碳储量研究进展.北京师范大学学报:自然科学版,2005,41:172-177
    杨万勤,邓仁菊,张健.森林凋落物分解及其对全球气候变化的响应.应用生态学报,2007,18:2889-2895
    杨晓菲,鲁绍伟,饶良懿,等.中国森林生态系统碳储量及其影响因素研究进展.西北林学院学报,2011,26:73-78
    杨玉盛,郭剑芬,林鹏,等.格氏栲天然林与人工林枯枝落叶层碳库及养分库.生态学报,2004,24:359-367
    杨曾奖,曾杰,徐大平,等.森林枯枝落叶分解及其影响因素.生态环境,2007,16:649-654
    余作岳,彭少麟.热带亚热带退化生态系统植被恢复生态学研究.广州:广东科技出版社,1996
    曾锋,邱治军,许秀玉.森林凋落物分解研究进展.生态环境学报,2010,19:239-243
    张春娜,延晓冬,杨剑虹.中国森林土壤氮储量估算.西南农业大学学报,2004,26:572-575
    张萍,张进.森林生物量与碳储量研究综述.中国林业,2009,5:56
    张瑞娟,李华,林勤保,等.土壤微生物群落表征中磷脂脂肪酸(PLFA)方法研究进展.山西农业科学,2011,39:1020-1024
    张秀娟.水曲柳落叶松细根分解与养分释放.东北林业大学硕士论文,2004
    昭日格,岳永杰,杨云峰.内蒙古自治区森林碳储量及其动态变化.干旱区资源与环境,2011,25:80-84
    中国科学院中国植物志编辑委员会主编.中国植物志.北京:科学出版社,1988,39:10
    中国科学院中国植物志编辑委员会主编.中国植物志.北京:科学出版社,2004a,22:28
    中国科学院中国植物志编辑委员会主编.中国植物志.北京:科学出版社,2004b,7:263
    周才平.中国主要类型森林生态系统及区域氮循环研究.中国科学院地理所博士论文,2000
    周玉荣,于振良,赵士洞.我国主要森林生态系统碳贮量和碳平衡.植物生态学报,2000,24:518-522
    邹国元,张福锁.根际反硝化作用与N2O释放.中国农业大学学报,2002,7:77-82

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