小兴安岭7种典型林型林分生物量碳密度与固碳能力

doi:10.17521/cjpe.2015.0014

植物生态学报 ›› 2015, Vol. 39 ›› Issue (2): 140-158.DOI: 10.17521/cjpe.2015.0014

所属专题：碳循环；碳储量

小兴安岭7种典型林型林分生物量碳密度与固碳能力

胡海清¹, 罗碧珍¹, 魏书精^1,^2,³, 魏书威⁴, 孙龙¹, 罗斯生¹, 马洪斌^1,^*()

¹东北林业大学林学院, 哈尔滨 150040
²桂林理工大学土木与建筑工程学院, 广西桂林 541004
³广西建筑新能源与节能重点实验室, 广西桂林 541004
⁴兰州理工大学设计艺术学院, 兰州 730050

收稿日期:2014-08-11 接受日期:2014-12-01 出版日期:2015-02-01 发布日期:2015-03-10
通讯作者: 马洪斌
作者简介:
# 共同第一作者
基金资助:
黑龙江省博士后基金(LBH-Z13012)、广西自然科学基金(2014GXNSFBA118108)、国家公益性行业科研重大专项(201404402)、国家科技支撑计划项目(2011BAD37B01)、国家自然科学基金(51208244和31070544)、黑龙江省科技攻关重点项目(GA09B201-06)和国家重点基础研究发展计划(2011CB403203)、林业公益性行业科研专项(2010- 04003-6)

Biomass carbon density and carbon sequestration capacity in seven typical forest types of the Xiaoxing’an Mountains, China

HU Hai-Qing¹, LUO Bi-Zhen¹, WEI Shu-Jing^1,^2,³, WEI Shu-Wei⁴, SUN Long¹, LUO Si-Sheng¹, MA Hong-Bin^1,^*()

¹College of Forestry, Northeast Forestry University, Harbin 150040, China
²College of Civil Engineering and Architecture, Guilin University of Technology, Guilin, Guangxi 541004, China
³Guangxi Key Laboratory of New Energy and Building Energy Saving, Guilin, Guangxi 541004, China
⁴College of Design Art, Lanzhou University of Technology, Lanzhou 730050, China

Received:2014-08-11 Accepted:2014-12-01 Online:2015-02-01 Published:2015-03-10
Contact: Hong-Bin MA
About author:
# Co-first authors

摘要/Abstract

摘要：

森林生物碳储量作为森林生态系统碳库的重要组成部分, 在全球碳循环中发挥着重要作用。以小兴安岭7种典型林型为研究对象, 通过外业样地调查与室内实验分析相结合的方法, 从林分尺度对林分生物量与碳密度进行计量, 分析了林分生物碳储量的空间分配格局, 并对林分年固碳能力与碳汇潜力进行了探讨。结果表明: 小兴安岭不同林型从幼龄林到成熟林的乔木层碳密度增长速率为: 蒙古栎(Quercus mongolica)林>兴安落叶松(Larix gmelinii)林>云冷杉(Picea-Abies)林>樟子松(Pinus sylvestris var. mongolica)林>山杨(Populus davidiana)林>红松(Pinus koraiensis)林>白桦(Betula platyphylla)林。7种典型林型不同龄组(幼龄林、中龄林、近熟林和成熟林)林分生物量碳密度分别为: 红松林31.4、74.7、118.4和130.2 t·hm^-2; 兴安落叶松林28.9、44.3、74.2和113.3 t·hm^-2; 樟子松林22.8、52.0、71.1和92.6 t·hm^-2; 云冷杉林23.1、44.1、77.6和130.3 t·hm^-2; 白桦林18.8、35.3、66.6和88.5 t·hm^-2; 蒙古栎林25.0、20.0、47.5和68.9 t·hm^-2; 山杨林19.8、28.7、43.7和76.6 t·hm^-2。红松林、兴安落叶松林、樟子松林和蒙古栎林在幼龄林时林分年固碳量较高, 其他林型在成熟林时林分年固碳量较高。7种典型林型不同龄组的林分生物量碳密度均随林龄增长而增加, 但不同林型的碳汇功能存在差异, 同一林型不同林龄的生物量碳密度增幅差异也较大。林分年固碳量在0.4-2.8 t·hm^-2之间, 碳汇能力较强、碳汇潜力较大。尤其是小兴安岭目前林分质量较差, 幼龄林和中龄林所占的比重较大, 具有较大的碳汇潜力。研究结果可为森林经营管理及碳汇功能评价提供参考。

关键词: 林分生物量, 碳密度, 固碳能力, 年固碳量, 碳汇管理路径, 小兴安岭

Abstract: Aims

Forests are the world’s largest carbon (C) pool and sink among the terrestrial ecosystems. The amount of C in vegetation plays an important role in the global C cycle and balance. Our objectives were to assess C density and sequestration capacity in seven typical forest types of the Xiaoxing’an Mountains, Heilongjiang Province, China and to understand the implication of the C sink to the regional C budget and future forest C management.

Methods

Field surveys were combined with laboratory analysis and allometric equations for obtaining data for a variety of variables. Seven typical forest types in the Xiaoxing’an Mountains were studied based on age groups and plant functional groups (trees, shrubs, herbaceous and litter), including Pinus koraiensis, Larix gmelinii, Pinus sylvestris var. mongolica, Picea-Abies, Betula platyphylla, Quercus mongolica, and Populus davidiana forests. Surveys were made on C density and annual carbon gains in trees, understory shrubs, herbaceous plants and litter for each forest type. The forest stands were classified into age groups for estimating the biomass and C density of the study area.

Important findings

The C density of the seven forest types in different age groups varied widely. The C density per unit area for young, middle-aged, near mature and mature forests of each forest type were as follows: 31.4, 74.7, 118.4 and 130.2 t·hm^-2 in Pinus koraiensis; 28.9, 44.3, 74.2 and 113.3 t·hm^-2 in L. gmelinii; 22.8, 52.0, 71.1 and 92.6 t·hm^-2 in Pinus sylvestris var. mongolica; 23.1, 44.1, 77.6 and 130.3 t·hm^-2 in Picea-Abies; 18.8, 35.3, 66.6 and 88.5 t·hm^-2 in B. platyphylla; 25.0, 20.0, 47.4 and 68.9 t·hm^-2 in Q. mongolica; and 19.8, 28.7, 43.7 and 76.6 t·hm^-2 in Populus davidiana forests, respectively. These results show that biomass C stocks in the Xiao- xing’an Mountains play an important role in the C cycle and regional C balance. Different forest types and stands of different age groups varied greatly in C stocks. Because most growth in the seven forest types occurs in the young and middle-aged forest stands, these age groups are considered to have a great potential to increase the biomass C density. This significant C sink will be further enhanced in the Xiaoxing’an Mountains with the development and restoration designed to provide specific ecological services including C sequestration.

Key words: forest stand biomass, carbon density, carbon sequestration capacity, annual carbon sequestration, carbon sink management path, Xiaoxing’an Mountains

胡海清, 罗碧珍, 魏书精, 魏书威, 孙龙, 罗斯生, 马洪斌. 小兴安岭7种典型林型林分生物量碳密度与固碳能力. 植物生态学报, 2015, 39(2): 140-158. DOI: 10.17521/cjpe.2015.0014

HU Hai-Qing,LUO Bi-Zhen,WEI Shu-Jing,WEI Shu-Wei,SUN Long,LUO Si-Sheng,MA Hong-Bin. Biomass carbon density and carbon sequestration capacity in seven typical forest types of the Xiaoxing’an Mountains, China. Chinese Journal of Plant Ecology, 2015, 39(2): 140-158. DOI: 10.17521/cjpe.2015.0014

导出引用管理器 EndNote|Ris|BibTeX

链接本文: https://www.plant-ecology.com/CN/10.17521/cjpe.2015.0014

https://www.plant-ecology.com/CN/Y2015/V39/I2/140

图/表 7

参考文献 53

1	Adams JM, Piovesan G (2002). Uncertainties in the role of land vegetation in the carbon cycle.Chemosphere, 49, 805-819.
2	Amiro BD, MacPherson JI, Desjardins RL, Chen JM, Liu J (2003). Post-fire carbon dioxide fluxes in the western Canadian boreal forest: Evidence from towers, aircraft and remote sensing.Agricultural and Forest Meteorology, 115, 91-107.
3	Blackstone NW (1987). Allometry and relative growth: Pattern and process in evolutionary studies.Systematic Zoology, 36, 76-78.
4	Dixon RK, Solomon AM, Brown S, Houghton RA, Trexier MC, Wisniewski J (1994). Carbon pools and flux of global forest ecosystems.Science, 263, 185-190.
5	Dixon RK, Krankina ON (1993). Forest fires in Russia: Carbon dioxide emissions to the atmosphere.Canadian Journal of Forest Research, 23, 700-705.
6	Fang JY, Chen AP (2001). Dynamic forest biomass carbon pools in China and their significance.Acta Botanica Sinica, 43, 967-973.(in Chinese with English abstract)
	[方精云, 陈安平 (2001). 中国森林植被碳库的动态变化及其意义. 植物学报, 43, 967-973.]
7	Fang JY, Liu GH, Xu SL (1996). Biomass and net production of forest vegetation in China.Acta Ecologica Sinica, 16, 497-508.(in Chinese with English abstract)
	[方精云, 刘国华, 徐嵩龄 (1996). 我国森林植被的生物量和净生产量. 生态学报, 16, 497-508.]
8	FAO (Food and Agriculture Organization of the United Nations) (2010). Global Forest Resources Assessment 2010. Viale delle Terme di Caracalla, FAO, Rome.
9	Foley JA (1995). An equilibrium model of the terrestrial carbon budget.Tellus, 47, 310-319.
10	González-Pérez JA, González-Vila FJ, Almendros G, Knicker H (2004). The effect of fire on soil organic matter: A review.Environment International, 30, 855-870.
11	Houghton JT, Ding Y, Griggs DJ, Noguer M, van der Linden PJ, Dai X, Maskell K, Johnson CA (2010). Climate Change 2001: The Scientific Basis Cambridge University Press, New York The Scientific Basis. Cambridge University Press, New York.
12	Houghton RA (2005). Aboveground forest biomass and the global carbon balance.Global Change Biology, 11, 945-958.
13	Hu HQ, Luo BZ, Wei SJ, Wei SW, Sun L, Wen ZM (2013a). Estimation of carbonaceous gases emission from forest fires in Xiao Xing’an Mountains of Northeast China in 1953-2011.Chinese Journal of Applied Ecology, 24, 3065-3076.(in Chinese with English abstract)
	[胡海清, 罗碧珍, 魏书精, 魏书威, 孙龙, 文正敏 (2013a). 1953- 2011年小兴安岭森林火灾含碳气体排放的估算. 应用生态学报, 24, 3065-3076.]
14	Hu HQ, Wei SJ, Sun L (2012a). Estimation of carbon emissions due to forest fire in Daxing’an Mountains from 1965 to 2010.Chinese Journal of Plant Ecology, 36, 629-644.(in Chinese with English abstract)
	[胡海清, 魏书精, 孙龙 (2012a). 1965-2010年大兴安岭森林火灾碳排放的估算研究, 植物生态学报, 36, 629-644.]
15	Hu HQ, Wei SJ, Sun L (2012b). Estimating carbon emissions from forest fires during 2001 to 2010 in Daxing’anling Mountain.Acta Ecologica Sinica, 32, 5373-5386.(in Chinese with English abstract)
	[胡海清, 魏书精, 孙龙 (2012b). 大兴安岭2001—2010年森林火灾碳排放的计量估算. 生态学报, 32, 5373-5386.]
16	Hu HQ, Wei SJ, Jin S, Sun L (2012c). Measurement model of carbon emission from forest fire: A review.Chinese Journal of Applied Ecology, 23, 1423-1434.(in Chinese with English abstract)
	[胡海清, 魏书精, 金森, 孙龙 (2012c). 森林火灾碳排放计量模型研究进展. 应用生态学报, 23, 1423-1434.]
17	Hu HQ, Wei SJ, Sun L (2012d). Estimating carbon emissions from forest fires in 2010 from huzhong of Daxing’anling Mountain.Scientia Silvae Sinicae, 48(10), 109-119.(in Chinese with English abstract)
	[胡海清, 魏书精, 孙龙 (2012d). 大兴安岭呼中区2010年森林火灾碳排放的计量估算, 林业科学, 48(10), 109-119.]
18	Hu HQ, Wei SJ, Sun L, Wang MY (2013b). Interaction among climate change, fire disturbance and ecosystem carbon cycle.Arid Land Geography, 36, 57-75.(in Chinese with English abstract)
	[胡海清, 魏书精, 孙龙, 王明玉 (2013b). 气候变化、火干扰与生态系统碳循环. 干旱区地理, 36, 57-75.]
19	Huang CD, Zhang J, Yang WQ, Tang X, Zhao AJ (2008). Dynamics on forest carbon stock in Sichuan Province and Chongqing City.Acta Ecologica Sinica, 28, 966-975.(in Chinese with English abstract)
	[黄从德, 张健, 杨万勤, 唐宵, 赵安玖 (2008). 四川省及重庆地区森林植被碳储量动态. 生态学报, 28, 966-975.]
20	Huxley JS (1932). Problems of Relative Growth. Dial Press, New York. 1-9.
21	IPCC (Intergovernmental Panel on Climate Change) (2000). Land use, land-use change, and forestry. In: Watson RT, Noble IR, Bolin B, Ravindranath NH, Verardo DJ, Dokken DJ eds. A Special Report of the Intergovernmental Panel on Climate Change. Cambridge University Press, Cambridge, UK.
22	IPCC (Intergovernmental Panel on Climate Change) (2006). Agriculture, forestry and other land use. In: Eggleston S, Buendia L, Miwa K, Ngara T, Tanabe K eds. 2006 IPCC Guidelines for National Greenhouse Gas Inventories. Institute for Global Environmental Strategies, Kanagawa, Japan.
23	Isaev AS, Korovin GN, Bartalev SA, Ershov DV, Janetos A, Kasischke ES, Shugart HH, French NHF, Orlick BE, Murphy TL (2002). Using remote sensing to assess Russian forest fire carbon emissions.Climatic Change, 55, 235-249.
24	Jiao Y, Hu HQ (2005). Carbon storage and its dynamics of forest vegetations in Heilongjiang Province. Chinese Journal of Applied Ecology, 16, 2248-2252.(in Chinese with English abstract)
	[焦燕, 胡海清 (2005). 黑龙江省森林植被碳储量及其动态变化. 应用生态学报, 16, 2248-2252.]
25	Jiang YL, Zhou GS (2001). Carbon equilibrium in Larix gmelinii forest and impact of global change on it.Chinese Journal of Applied Ecology, 12, 481-484.(in Chinese with English abstract)
	[蒋延玲, 周广胜 (2001). 兴安落叶松林碳平衡和全球变化影响研究. 应用生态学报, 12, 481-484.]
26	Keeling CD, Chin JFS, Whorf TP (1996). Increased activity of northern vegetation inferred from atmospheric CO2 measurements. Nature, 382, 146-149.
27	King AW, Emanuel WR, Wullschleger SD, Post WM (1995). In search of the missing carbon sink: A model of terrestrial biospheric response to land-use change and atmospheric CO2.Tellus, 47, 501-519.
28	Kolchugina TP, Vinson TS (1993). Comparison of two methods to assess the carbon budget of forest biomes in the Former Soviet Union.Water, Air, & Soil Pollution, 70, 207-221.
29	Kurz WA, Webb TM, McNamee PJ, Apps MJ (1993). The carbon budget of the Canadian forest sector: Phase I.Simulation, 61, 139-144.
30	Li B, Fang X, Xiang WH, Tian DL (2013). Carbon storage, carbon density, and carbon sequestration potential of cunninghamia lanceolata plantations in Hunan Province.Scientia Silvae Sinicae, 49(3), 25-32.(in Chinese with English abstract)
	[李斌, 方晰, 项文化, 田大伦 (2013). 湖南省杉木林植被碳贮量、碳密度及碳吸存潜力. 林业科学, 49(3), 25-32.]
31	Li HK, Lei YC, Zeng WS (2011). Forest carbon storage in China estimated using forestry inventory data.Scientia Silvae Sinicae, 47(7), 7-12.(in Chinese with English abstract)
	[李海奎, 雷渊才, 曾伟生 (2011). 基于森林清查资料的中国森林植被碳储量. 林业科学, 47(7), 7-12.]
32	Liu GH, Fu BJ, Fang JY (2000). Carbon dynamics of Chinese forests and its contribution to global carbon balance.Acta Ecologica Sinica, 20, 733-740.(in Chinese with English abstract)
	[刘国华, 傅伯杰, 方精云 (2000). 中国森林碳动态及其对全球碳平衡的贡献. 生态学报, 20, 733-740.]
33	Liu YC, Yu GR, Wang QF, Zhang YJ (2012). Huge carbon sequestration potential in global forests.Journal of Resources and Ecology, 3, 193-201.
34	Neary DG, Klopatek CC, DeBano LF, Ffolliott PF (1999). Fire effects on belowground sustainability: A review and synthesis.Forest Ecology and Management, 122, 51-71.
35	Schlesinger WH (1990). Evidence from chronosequence studies for a low carbon-storage potential of soils.Nature, 348, 232-234.
36	Sun L, Lu JY, Wei SJ, Wu C, Hu HQ (2013). Research progress of forest fuel load estimation methods.Forest Engineering, 29(2), 26-31, 37.(in Chinese with English abstract)
	[孙龙, 鲁佳宇, 魏书精, 武超, 胡海清 (2013). 森林可燃物载量估测方法研究进展. 森林工程, 29(2), 26-31, 37.]
37	Sun YJ, Zhang J, Han AH, Wang XJ, Wang XJ (2007). Biomass and carbon pool of Larix gmelinii young and middle age forest in Xing’an Mountains Inner Mongolia.Acta Ecologica Sinica, 27, 1756-1762.(in Chinese with English abstract)
	[孙玉军, 张俊, 韩爱惠, 王雪军, 王新杰 (2007). 兴安落叶松(Larix gmelinii)幼中龄林的生物量与碳汇功能. 生态学报, 27, 1756-1762.]
38	Tumer DP, Koepper GJ, Harmon ME, Lee JJ (1995). A carbon budget for forests of the conterminous United States.Ecological Applications, 5, 421-436.
39	Vloedbeld M, Leemans R (1993). Quantifying feedback processes in the response of the terrestrial carbon cycle to global change: The modeling approach of image-2.Water, Air, & Soil Pollution, 70, 615-628.
40	Wang HY, Wang WJ, Qiu L, Su DX, An J, Zheng GY, Zu YG (2012). Differences in biomass, litter layer mass and SOC storage changing with tree growth in Larix gmelinii plantations in Northeast China.Acta Ecologica Sinica, 32, 833-843.(in Chinese with English abstract)
	[王洪岩, 王文杰, 邱岭, 苏冬雪, 安静, 郑广宇, 祖元刚 (2012). 兴安落叶松林生物量、地表枯落物量及土壤有机碳储量随林分生长的变化差异. 生态学报, 32, 833-843.]
41	Wang SQ, Zhou CH, Luo CW (1999). Studying carbon storage spatial distribution of terrestrial natural vegetation in China.Progress in Geography, 18, 238-244.(in Chinese with English abstract)
	[王绍强, 周成虎, 罗承文 (1999). 中国陆地自然植被碳量空间分布特征探讨. 地理科学进展, 18, 238-244.]
42	Wang XK, Feng ZW (2000). The potential to sequester atmospheric carbon through forest ecosystems in China.Chinese Journal of Ecology, 19(4), 72-74.(in Chinese with English abstract)
	[王效科, 冯宗炜 (2000). 中国森林生态系统中植物固定大气碳的潜力. 生态学杂志, 19(4), 72-74.]
43	Wang XK, Feng ZW, Ouyang ZY (2001). Vegetation carbon storage and density of forest ecosystems in China.Chinese Journal of Applied Ecology, 12, 13-16.(in Chinese with English abstract)
	[王效科, 冯宗炜, 欧阳志云 (2001). 中国森林生态系统的植物碳储量和碳密度研究. 应用生态学报, 12, 13-16.]
44	Wei SJ (2013). Quantitative Evaluation Methods of Carbon Emissions from Forest Fires in Heilongjiang Province, China. PhD dissertation, Northeast Forestry University, Harbin. 1-10.(in Chinese with English abstract)
	[魏书精 (2013). 黑龙江省森林火灾碳排放定量评价方法研究. 博士学位论文, 东北林业大学, 哈尔滨. 1-10.]
45	Wei WJ, Wang B, Li SN, Ma XQ, Sun JJ, Chen FJ (2007). Carbon storage and density of tree stratum in forests in Jiangxi Province.Acta Agriculturae Universitatis Jiangxiensis, 29, 767-772.(in Chinese with English abstract)
	[魏文俊, 王兵, 李少宁, 马向前, 孙建军, 陈方建 (2007). 江西省森林植被乔木层碳储量与碳密度研究. 江西农业大学学报, 29, 767-772.]
46	World Meteorological Organization (2011). WMO Greenhouse Gas Bulletin: The State of Greenhouse Gases in the Atmosphere Based on Global Observations through 2011. World Meteorological Organization, Geneva. 1-4.
47	Xi TT, Li SL (2006). Analysis of forestry carbon mitigation potential in Heilongjiang Province.Problems of Forestry Economics, 26, 519-522, 526.(in Chinese with English abstract)
	[郗婷婷, 李顺龙 (2006). 黑龙江省森林碳汇潜力分析. 林业经济问题, 26, 519-522, 526.]
48	Xu XL, Cao MK, Li KR (2007). Temporal-spatial dynamics of carbon storage of forest vegetation in China.Progress in Geography, 26(6), 1-10.(in Chinese with English abstract)
	[徐新良, 曹明奎, 李克让 (2007). 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, 26(6), 1-10.]
49	Ye JS, She GH (2010). Forest carbon dynamics in Guangdong Province. Journal of Nanjing Forestry University (Natural Science Edition), 34(4), 7-12.(in Chinese with English abstract)
	[叶金盛, 佘光辉 (2010). 广东省森林植被碳储量动态研究. 南京林业大学学报(自然科学版), 34(4), 7-12.]
50	Zhang MY, Luo WJ, Liu HY, Zhang CH, Yue YM, Wang KL (2013). Spatial distribution and change of vegetation carbon in Northwest Guangxi, China on the basis of vegetation inventory data.Acta Ecologica Sinica, 33, 5067-5077.(in Chinese with English abstract)
	[张明阳, 罗为检, 刘会玉, 章春华, 岳跃民, 王克林 (2013). 基于林业清查资料的桂西北植被碳空间分布及其变化特征. 生态学报, 33, 5067-5077.]
51	Zhao M, Zhou GS (2004). Carbon storage of forest vegetation and its relationship with climatic factors.Scientia Geographica Sinica, 24, 50-54.(in Chinese with English abstract)
	[赵敏, 周广胜 (2004). 中国森林生态系统的植物碳贮量及其影响因子分析. 地理科学, 24, 50-54.]
52	Zhou GY, Liu SG, Li ZA, Zhang DQ, Tang XL, Zhou CY, Yan JH, Mo JM (2006). Old-growth forests can accumulate carbon in soils.Science, 314, 1417.
53	Zhou YR, Yu ZL, Zhao SD (2000). Carbon storage and budget of major Chinese forest types.Acta Phytoecologica Sinica, 24, 518-522.(in Chinese with English abstract)
	[周玉荣, 于振良, 赵士洞 (2000). 我国主要森林生态系统碳贮量和碳平衡. 植物生态学报, 24, 518-522.]

林型 Forest type	龄组划分 Age group
林型 Forest type	幼龄林 Young forest (a)	中龄林 Middle forest (a)	近熟林 Premature forest (a)	成熟林 Mature forest (a)
红松林 Pinus koraiensis forest	≤60	61-100	101-120	120-160
兴安落叶松林 Larix gmelinii forest	≤40	41-80	81-100	101-140
樟子松林 Pinus sylvestris var. mongolica forest	≤40	41-80	81-100	101-140
云冷杉林 Picea-Abies forest	≤60	61-100	101-120	120-160
白桦林 Betula platyphylla forest	≤30	31-50	51-60	61-80
蒙古栎林 Quercus mongolica forest	≤40	41-60	61-80	81-120
山杨林 Populus davidiana forest	≤10	11-15	16-20	21-30

林型 Forest type	龄组划分 Age group
林型 Forest type	幼龄林 Young forest (a)	中龄林 Middle forest (a)	近熟林 Premature forest (a)	成熟林 Mature forest (a)
红松林 Pinus koraiensis forest	≤60	61-100	101-120	120-160
兴安落叶松林 Larix gmelinii forest	≤40	41-80	81-100	101-140
樟子松林 Pinus sylvestris var. mongolica forest	≤40	41-80	81-100	101-140
云冷杉林 Picea-Abies forest	≤60	61-100	101-120	120-160
白桦林 Betula platyphylla forest	≤30	31-50	51-60	61-80
蒙古栎林 Quercus mongolica forest	≤40	41-60	61-80	81-120
山杨林 Populus davidiana forest	≤10	11-15	16-20	21-30

林型 Forest type	组分 Component	a	b	决定系数 Coefficient of determination (R²)	样本数 No. of samples (N)
红松林 Pinus koraiensis forest	干 Trunk	0.046 65	0.902 37	0.97	30
	枝 Branch	0.031 23	0.612 48	0.99	30
	叶 Leaf	0.012 35	0.643 47	0.95	30
	皮 Bark	0.029 57	0.564 89	0.90	30
	根 Root	0.009 25	0.739 65	0.96	30
兴安落叶松林 Larix gmelinii forest	干 Trunk	0.013 02	1.021 54	0.99	30
	枝 Branch	0.001 29	1.039 98	0.92	30
	叶 Leaf	0.011 12	0.637 45	0.95	30
	皮 Bark	0.031 27	0.615 24	0.97	30
	根 Root	0.041 25	0.684 51	0.99	30
樟子松林 Pinus sylvestris var. mongolica forest	干 Trunk	0.051 41	0.862 14	0.94	30
	枝 Branch	0.014 63	0.724 58	0.97	30
	叶 Leaf	0.021 24	0.524 78	0.91	30
	皮 Bark	0.057 81	0.442 87	0.92	30
	根 Root	0.026 31	0.686 56	0.95	30
云冷杉林 Picea-Abies forest	干 Trunk	0.322 91	0.679 19	0.97	30
	枝 Branch	0.022 57	0.635 64	0.90	30
	叶 Leaf	0.004 18	0.821 35	0.92	30
	皮 Bark	0.024 21	0.572 15	0.94	30
	根 Root	0.011 54	0.812 34	0.94	30
白桦林 Betula platyphylla forest	干 Trunk	0.011 75	1.102 52	0.97	30
	枝 Branch	0.010 24	0.805 47	0.97	30
	叶 Leaf	0.013 47	0.649 47	0.90	30
	皮 Bark	0.024 69	0.631 01	0.92	30
	根 Root	0.048 87	0.632 46	0.96	30
蒙古栎林 Quercus mongolica forest	干 Trunk	0.011 97	1.092 48	0.91	30
	枝 Branch	0.008 45	0.894 18	0.90	30
	叶 Leaf	0.006 24	0.828 54	0.91	30
	皮 Bark	0.008 72	0.817 59	0.92	30
	根 Root	0.010 54	0.835 38	0.93	30
山杨林 Populus davidiana forest	干 Trunk	0.235 14	0.853 24	0.93	30
	枝 Branch	0.021 54	0.862 15	0.98	30
	叶 Leaf	0.009 79	0.856 14	0.96	30
	皮 Bark	0.052 23	0.632 17	0.97	30
	根 Root	0.125 87	0.558 74	0.98	30

林型 Forest type	组分 Component	a	b	决定系数 Coefficient of determination (R²)	样本数 No. of samples (N)
红松林 Pinus koraiensis forest	干 Trunk	0.046 65	0.902 37	0.97	30
	枝 Branch	0.031 23	0.612 48	0.99	30
	叶 Leaf	0.012 35	0.643 47	0.95	30
	皮 Bark	0.029 57	0.564 89	0.90	30
	根 Root	0.009 25	0.739 65	0.96	30
兴安落叶松林 Larix gmelinii forest	干 Trunk	0.013 02	1.021 54	0.99	30
	枝 Branch	0.001 29	1.039 98	0.92	30
	叶 Leaf	0.011 12	0.637 45	0.95	30
	皮 Bark	0.031 27	0.615 24	0.97	30
	根 Root	0.041 25	0.684 51	0.99	30
樟子松林 Pinus sylvestris var. mongolica forest	干 Trunk	0.051 41	0.862 14	0.94	30
	枝 Branch	0.014 63	0.724 58	0.97	30
	叶 Leaf	0.021 24	0.524 78	0.91	30
	皮 Bark	0.057 81	0.442 87	0.92	30
	根 Root	0.026 31	0.686 56	0.95	30
云冷杉林 Picea-Abies forest	干 Trunk	0.322 91	0.679 19	0.97	30
	枝 Branch	0.022 57	0.635 64	0.90	30
	叶 Leaf	0.004 18	0.821 35	0.92	30
	皮 Bark	0.024 21	0.572 15	0.94	30
	根 Root	0.011 54	0.812 34	0.94	30
白桦林 Betula platyphylla forest	干 Trunk	0.011 75	1.102 52	0.97	30
	枝 Branch	0.010 24	0.805 47	0.97	30
	叶 Leaf	0.013 47	0.649 47	0.90	30
	皮 Bark	0.024 69	0.631 01	0.92	30
	根 Root	0.048 87	0.632 46	0.96	30
蒙古栎林 Quercus mongolica forest	干 Trunk	0.011 97	1.092 48	0.91	30
	枝 Branch	0.008 45	0.894 18	0.90	30
	叶 Leaf	0.006 24	0.828 54	0.91	30
	皮 Bark	0.008 72	0.817 59	0.92	30
	根 Root	0.010 54	0.835 38	0.93	30
山杨林 Populus davidiana forest	干 Trunk	0.235 14	0.853 24	0.93	30
	枝 Branch	0.021 54	0.862 15	0.98	30
	叶 Leaf	0.009 79	0.856 14	0.96	30
	皮 Bark	0.052 23	0.632 17	0.97	30
	根 Root	0.125 87	0.558 74	0.98	30

林型 Forest type	龄组 Age group	平均林龄 Average forest age (a)	平均胸径 Average diameter at breast height (cm)	平均树高 Average tree height (m)
红松林 Pinus koraiensis forest	幼龄林 Young forest	24.23 ± 2.21	11.94 ± 1.34	9.95 ± 0.97
	中龄林 Middle-aged forest	68.54 ± 7.24	17.66 ± 2.45	16.54 ± 3.74
	近熟林 Near mature forest	109.19 ± 3.26	20.48 ± 2.18	21.62 ± 5.86
	成熟林 Mature forest	123.50 ± 12.34	21.31 ± 5.67	22.46 ± 4.59
兴安落叶松林 Larix gmelinii forest	幼龄林 Young forest	21.66 ± 1.78	9.46 ± 1.15	9.44 ± 0.91
	中龄林 Middle-aged forest	63.78 ± 10.51	13.51 ± 2.30	12.13 ± 3.48
	近熟林 Near mature forest	84.50 ± 2.96	17.12 ± 6.47	17.59 ± 3.17
	成熟林 Mature forest	135.47 ± 7.28	21.04 ± 6.19	20.27 ± 5.89
樟子松林 Pinus sylvestris var. mongolica forest	幼龄林 Young forest	25.48 ± 3.12	9.11 ± 1.62	8.83 ± 1.45
	中龄林 Middle-aged forest	62.53 ± 8.84	16.77 ± 3.57	15.38 ± 2.84
	近熟林 Near mature forest	89.18 ± 4.16	18.91 ± 3.66	17.01 ± 7.11
	成熟林 Mature forest	122.45 ± 10.47	21.31 ± 6.41	19.44 ± 6.97
云冷杉林 Picea-Abies forest	幼龄林 Young forest	29.60 ± 4.15	7.26 ± 1.01	9.77 ± 1.22
	中龄林 Middle-aged forest	68.00 ± 6.74	11.89 ± 1.34	13.03 ± 1.42
	近熟林 Near mature forest	111.97 ± 3.48	16.57 ± 3.59	16.02 ± 3.47
	成熟林 Mature forest	135.46 ± 15.42	21.54 ± 2.49	22.75 ± 5.64
白桦林 Betula platyphylla forest	幼龄林 Young forest	19.73 ± 3.15	9.55 ± 1.32	10.31 ± 1.46
	中龄林 Middle-aged forest	42.93 ± 5.85	11.63 ± 2.64	13.59 ± 3.69
	近熟林 Near mature forest	56.27 ± 1.42	14.99 ± 4.59	15.03 ± 3.67
	成熟林 Mature forest	74.81 ± 3.00	16.29 ± 5.67	18.04 ± 6.68
蒙古栎林 Quercus mongolica forest	幼龄林 Young forest	23.87 ± 4.25	7.53 ± 0.98	5.87 ± 0.89
	中龄林 Middle-aged forest	48.00 ± 3.33	11.30 ± 1.28	7.15 ± 0.78
	近熟林 Near mature forest	66.59 ± 4.49	14.72 ± 1.94	12.38 ± 2.00
	成熟林 Mature forest	101.42 ± 10.29	17.03 ± 2.37	13.43 ± 2.79
山杨林 Populus davidiana forest	幼龄林 Young forest	8.64 ± 0.54	5.47 ± 0.24	5.56 ± 0.51
	中龄林 Middle-aged forest	13.75 ± 0.48	6.79 ± 0.84	7.84 ± 0.36
	近熟林 Near mature forest	19.53 ± 0.89	8.73 ± 0.74	9.25 ± 0.49
	成熟林 Mature forest	27.61 ± 1.12	11.39 ± 1.37	10.76 ± 0.87

小兴安岭7种典型林型林分生物量碳密度与固碳能力

Biomass carbon density and carbon sequestration capacity in seven typical forest types of the Xiaoxing’an Mountains, China

全文

PDF (PC)

可视化

被引次数

摘要/Abstract

引用本文

使用本文

图/表 7

参考文献 53

相关文章 15

编辑推荐

Metrics

本文评价

林型 Forest type	龄组 Age group	乔木层 Tree						灌木层 Shrub layer	草本层 Herbaceous layer	凋落物层 Litter layer	林分生物量 Stand biomass
林型 Forest type	龄组 Age group	干 Trunk	枝 Branch	叶 Leaf	皮 Bark	根 Root	小计 Total	灌木层 Shrub layer	草本层 Herbaceous layer	凋落物层 Litter layer	林分生物量 Stand biomass
红松林 Pinus koraiensis forest	幼龄林 Young forest	32.58 ± 3.27	2.66 ± 0.24	1.32 ± 0.21	1.78 ± 0.45	1.98 ± 0.42	40.33 ± 3.59	10.57 ± 2.16	3.24 ± 0.68	8.99 ± 2.03	63.13 ± 4.26
	中龄林 Middle-aged forest	104.45 ± 11.49	5.87 ± 1.03	3.02 ± 0.57	3.70 ± 0.89	5.15 ± 0.67	122.19 ± 13.45	12.34 ± 1.85	4.57 ± 0.94	9.54 ± 1.18	148.64 ± 15.68
	近熟林 Near mature forest	173.78 ± 22.37	8.29 ± 1.55	4.35 ± 1.34	5.09 ± 1.32	7.82 ± 1.23	199.32 ± 26.34	15.24 ± 1.97	5.21 ± 0.86	10.55 ± 1.69	230.32 ± 28.56
	成熟林 Mature forest	193.23 ± 19.57	8.91 ± 1.33	4.69 ± 0.76	5.44 ± 1.42	8.53 ± 1.67	220.79 ± 21.45	8.24 ± 1.59	5.57 ± 0.74	18.57 ± 2.87	253.17 ± 22.43
兴安落叶松林 Larix gmelinii forest	幼龄林 Young forest	12.72 ± 1.69	1.43 ± 0.17	0.82 ± 0.37	1.98 ± 0.34	4.16 ± 0.86	21.09 ± 2.26	18.66 ± 4.19	7.59 ± 1.47	10.21 ± 2.46	57.55 ± 2.85
	中龄林 Middle-aged forest	34.03 ± 4.58	3.89 ± 0.78	1.51 ± 0.56	3.57 ± 0.86	8.04 ± 1.27	51.04 ± 5.26	9.58 ± 1.51	11.28 ± 1.39	14.59 ± 3.45	86.49 ± 6.97
	近熟林 Near mature forest	80.70 ± 16.74	9.36 ± 1.67	2.59 ± 0.34	6.01 ± 1.26	14.34 ± 2.19	112.99 ± 18.75	4.24 ± 0.24	8.84 ± 1.75	15.37 ± 3.31	141.44 ± 20.17
	成熟林 Mature forest	142.14 ± 25.67	16.66 ± 3.49	3.68 ± 0.81	8.46 ± 1.78	20.95 ± 2.87	191.88 ± 25.79	2.27 ± 0.15	3.21 ± 0.67	16.19 ± 3.60	213.55 ± 27.59
樟子松林 Pinus sylvestris var. mongolica forest	幼龄林 Young forest	15.17 ± 2.10	1.74 ± 0.24	0.68 ± 0.18	1.07 ± 0.24	2.44 ± 0.37	21.10 ± 2.34	10.21 ± 1.51	12.67 ± 2.46	3.27 ± 0.59	47.25 ± 2.85
	中龄林 Middle-aged forest	70.11 ± 16.98	6.31 ± 0.97	1.72 ± 0.34	2.36 ± 0.57	8.25 ± 1.28	88.75 ± 17.12	4.37 ± 0.64	7.97 ± 1.10	5.16 ± 1.00	106.25 ± 19.45
	近熟林 Near mature forest	94.07 ± 13.56	8.07 ± 1.74	2.06 ± 0.38	2.74 ± 0.45	10.43 ± 2.19	117.37 ± 14.62	7.67 ± 1.27	7.78 ± 1.19	10.27 ± 1.59	143.09 ± 16.51
	成熟林 Mature forest	129.70 ± 19.99	10.58 ± 2.18	2.50 ± 0.51	3.23 ± 0.67	13.46 ± 2.26	159.47 ± 20.16	6.63 ± 1.67	6.97 ± 0.98	11.94 ± 2.45	185.01 ± 23.34
云冷杉林 Picea-Abies forest	幼龄林 Young forest	22.43 ± 1.57	1.19 ± 0.28	0.71 ± 0.24	0.86 ± 0.10	1.84 ± 0.26	27.04 ± 1.89	6.57 ± 1.66	0.41 ± 0.08	11.54 ± 2.16	45.56 ± 2.01
	中龄林 Middle-aged forest	53.31 ± 9.85	2.69 ± 0.31	2.01 ± 0.39	1.79 ± 0.38	5.18 ± 1.01	64.98 ± 10.85	5.17 ± 1.28	0.23 ± 0.03	15.57 ± 2.85	85.95 ± 12.32
	近熟林 Near mature forest	96.29 ± 10.23	4.67 ± 0.86	4.11 ± 0.85	2.94 ± 0.96	10.52 ± 2.27	118.52 ± 11.32	9.47 ± 2.94	2.54 ± 0.34	18.37 ± 2.64	148.9 ± 11.25
	成熟林 Mature forest	174.50 ± 30.42	8.15 ± 1.37	8.43 ± 0.64	4.85 ± 1.06	21.41 ± 3.48	217.34 ± 31.28	3.66 ± 0.31	2.37 ± 0.45	24.27 ± 3.88	247.64 ± 2.37
白桦林 Betula platyphylla forest	幼龄林 Young forest	22.29 ± 1.46	2.54 ± 0.89	1.15 ± 0.17	1.86 ± 0.57	3.71 ± 0.46	31.55 ± 2.00	2.45 ± 0.41	5.38 ± 0.76	1.69 ± 0.21	41.07 ± 2.37
	中龄林 Middle-aged forest	46.67 ± 7.56	4.36 ± 0.97	1.78 ± 0.29	2.83 ± 0.45	5.67 ± 1.03	61.32 ± 7.99	4.67 ± 1.21	6.87 ± 1.27	3.47 ± 0.79	76.33 ± 9.45
	近熟林 Near mature forest	91.27 ± 11.39	7.12 ± 1.46	2.64 ± 0.64	4.16 ± 0.67	8.33 ± 2.18	113.52 ± 12.56	10.11 ± 2.16	9.57 ± 1.61	9.29 ± 1.64	142.49 ± 14.00
	成熟林 Mature forest	134.09 ± 16.96	9.43 ± 2.01	3.31 ± 0.54	5.18 ± 1.56	10.39 ± 0.29	162.40 ± 17.85	12.61 ± 2.57	2.14 ± 0.53	10.57 ± 1.57	187.72 ± 19.56
蒙古栎林 Quercus mongolica forest	幼龄林 Young forest	6.82 ± 0.75	1.52 ± 0.34	0.77 ± 0.13	1.01 ± 0.18	1.35 ± 0.27	11.46 ± 1.03	8.17 ± 1.89	19.33 ± 3.59	15.78 ± 3.59	54.74 ± 11.52
	中龄林 Middle-aged forest	20.53 ± 2.14	3.75 ± 0.84	1.77 ± 0.49	2.30 ± 0.41	3.13 ± 0.26	31.48 ± 2.75	7.64 ± 1.67	0.58 ± 0.09	2.67 ± 0.44	42.37 ± 5.16
	近熟林 Near mature forest	66.63 ± 16.48	9.83 ± 1.29	4.32 ± 1.04	5.54 ± 0.86	7.71 ± 1.08	94.04 ± 17.59	2.54 ± 0.49	0.47 ± 0.06	1.33 ± 0.22	98.38 ± 18.23
	成熟林 Mature forest	100.15 ± 17.56	13.72 ± 2.18	5.89 ± 1.15	7.52 ± 1.34	10.53 ± 2.19	137.80 ± 19.75	1.37 ± 0.35	0.51 ± 0.05	1.64 ± 0.34	141.32 ± 24.56
山杨林 Populus davidiana forest	幼龄林 Young forest	18.47 ± 1.75	1.77 ± 0.19	0.78 ± 0.13	1.32 ± 0.25	2.19 ± 0.52	24.54 ± 1.86	10.21 ± 2.57	8.28 ± 2.11	1.14 ± 0.12	44.17 ± 2.31
	中龄林 Middle-aged forest	35.81 ± 5.14	3.46 ± 0.61	1.52 ± 0.27	2.16 ± 0.37	3.38 ± 0.49	46.33 ± 6.15	8.46 ± 1.84	5.37 ± 1.35	3.47 ± 0.68	63.63 ± 6.87
	近熟林 Near mature forest	63.32 ± 8.79	6.15 ± 0.91	2.69 ± 0.61	3.30 ± 0.86	4.91 ± 0.84	80.36 ± 9.42	4.96 ± 0.78	6.57 ± 1.64	4.75 ± 0.93	96.64 ± 10.34
	成熟林 Mature forest	113.41 ± 16.34	11.08 ± 1.93	4.82 ± 0.49	5.08 ± 1.24	7.20 ± 1.42	141.59 ± 17.52	9.34 ± 2.47	8.39 ± 2.02	6.34 ± 1.24	165.66 ± 19.46

林型 Forest type	龄组 Age	乔木层Tree layer						灌木层 Shrub layer	草本层 Herbaceous layer	凋落物层 Litter layer	林分碳密度 Forest stand carbon density
林型 Forest type	龄组 Age	干 Trunk	枝 Branch	叶 Leaf	皮 Bark	根 Root	小计 Total	灌木层 Shrub layer	草本层 Herbaceous layer	凋落物层 Litter layer	林分碳密度 Forest stand carbon density
红松林 Pinus koraiensis forest	幼龄林 Young forest	16.4 ± 3.59	1.3 ± 0.27	0.6 ± 0.23	0.9 ± 0.47	1.0 ± 0.45	20.2 ± 3.63	5.3 ± 2.19	1.5 ± 0.70	4.4 ± 2.07	31.4 ± 4.31
	中龄林 Middle-aged forest	52.8 ± 11.89	3.0 ± 1.11	1.5 ± 0.58	1.9 ± 0.91	2.6 ± 0.70	61.7 ± 13.94	6.2 ± 1.90	2.1 ± 0.96	4.7 ± 1.21	74.7 ± 15.75
	近熟林 Near mature forest	89.9 ± 23.48	4.2 ± 1.64	2.2 ± 1.38	2.6 ± 1.36	4.0 ± 1.27	102.9 ± 26.58	7.8 ± 2.02	2.4 ± 0.89	5.3 ± 1.75	118.4 ± 29.15
	成熟林 Mature forest	100.2 ± 20.26	4.5 ± 1.40	2.4 ± 0.80	2.8 ± 1.47	4.3 ± 1.71	114.2 ± 21.76	4.2 ± 1.71	2.6 ± 0.77	9.2 ± 2.89	130.2 ± 23.10
兴安落叶松林 Larix gmelinii forest	幼龄林 Young forest	6.7 ± 1.86	0.7 ± 0.19	0.4 ± 0.38	1.0 ± 0.35	2.1 ± 0.89	10.9 ± 2.54	9.3 ± 4.22	3.5 ± 1.49	5.1 ± 2.49	28.9 ± 2.98
	中龄林 Middle-aged forest	18.3 ± 4.67	2.0 ± 0.85	0.7 ± 0.59	1.8 ± 0.89	4.1 ± 1.30	27.0 ± 5.51	4.8 ± 1.56	5.2 ± 1.42	7.3 ± 3.48	44.3 ± 7.51
	近熟林 Near mature forest	43.4 ± 17.36	4.9 ± 1.74	1.3 ± 0.36	3.1 ± 1.30	7.4 ± 2.25	60.0 ± 18.87	2.2 ± 0.29	4.2 ± 1.77	7.8 ± 3.36	74.2 ± 20.69
	成熟林 Mature forest	76.5 ± 27.19	8.7 ± 3.89	1.8 ± 0.85	4.4 ± 1.81	10.9 ± 2.92	102.3 ± 25.97	1.2 ± 0.17	1.5 ± 0.69	8.3 ± 3.65	113.3 ± 27.86
樟子松林 Pinus sylvestris var. mongolica forest	幼龄林 Young forest	7.5 ± 2.56	0.9 ± 0.27	0.3 ± 0.20	0.5 ± 0.28	1.2 ± 0.41	10.4 ± 2.57	5.1 ± 1.53	5.8 ± 2.48	1.5 ± 0.61	22.8 ± 3.15
	中龄林 Middle-aged forest	34.5 ± 17.69	3.1 ± 1.08	0.8 ± 0.39	1.2 ± 0.60	4.1 ± 1.32	43.7 ± 17.36	2.2 ± 0.68	3.7 ± 1.12	2.4 ± 1.03	52.0 ± 20.37
	近熟林 Near mature forest	47.4 ± 14.68	4.0 ± 1.87	1.0 ± 0.41	1.3 ± 0.48	5.2 ± 2.22	58.9 ± 14.86	3.8 ± 1.29	3.6 ± 1.21	4.8 ± 1.62	71.1 ± 16.85
	成熟林 Mature forest	65.9 ± 20.45	5.2 ± 2.58	1.2 ± 0.55	1.6 ± 0.71	6.6 ± 2.29	80.5 ± 20.37	3.3 ± 1.70	3.3 ± 1.00	5.6 ± 2.48	92.6 ± 23.89
云冷杉林 Picea-Abies forest	幼龄林 Young forest	11.5 ± 1.63	0.6 ± 0.36	0.4 ± 0.28	0.4 ± 0.12	0.9 ± 0.28	13.9 ± 1.94	3.3 ± 1.69	0.2 ± 0.12	5.8 ± 2.18	23.1 ± 2.67
	中龄林 Middle-aged forest	27.6 ± 9.99	1.4 ± 0.36	1.0 ± 0.42	0.9 ± 0.41	2.7 ± 1.06	33.6 ± 10.96	2.6 ± 1.31	0.1 ± 0.06	7.9 ± 2.91	44.1 ± 12.86
	近熟林 Near mature forest	50.5 ± 10.54	2.4 ± 0.91	2.1 ± 0.88	1.5 ± 0.98	5.5 ± 2.32	62.1 ± 11.51	4.9 ± 2.97	1.2 ± 0.37	9.5 ± 2.67	77.6 ± 11.97
	成熟林 Mature forest	92.8 ± 30.87	4.2 ± 1.42	4.3 ± 0.67	2.5 ± 1.09	11.3 ± 3.52	115.1 ± 31.49	1.9 ± 0.36	1.1 ± 0.48	12.3 ± 3.98	130.3 ± 33.56
白桦林 Betula platyphylla forest	幼龄林 Young forest	10.4 ± 1.58	1.2 ± 0.92	0.5 ± 0.20	0.8 ± 0.60	1.7 ± 0.48	14.5 ± 2.33	1.1 ± 0.44	2.4 ± 0.79	0.8 ± 0.23	18.8 ± 2.88
	中龄林 Middle-aged forest	21.9 ± 7.88	2.0 ± 0.99	0.8 ± 0.32	1.3 ± 0.47	2.6 ± 1.05	28.5 ± 8.49	2.2 ± 1.27	3.1 ± 1.30	1.6 ± 0.83	35.3 ± 10.47
	近熟林 Near mature forest	43.2 ± 11.54	3.3 ± 1.50	1.2 ± 0.66	1.9 ± 0.69	3.8 ± 2.19	53.3 ± 12.87	4.7 ± 2.18	4.3 ± 1.64	4.3 ± 1.69	66.6 ± 14.85
	成熟林 Mature forest	63.8 ± 17.25	4.4 ± 2.06	1.5 ± 0.57	2.3 ± 1.58	4.8 ± 0.31	76.8 ± 18.16	6.0 ± 2.59	1.0 ± 0.58	4.9 ± 1.59	88.5 ± 20.37
蒙古栎林 Quercus mongolica forest	幼龄林 Young forest	3.2 ± 0.84	0.7 ± 0.40	0.4 ± 0.16	0.5 ± 0.20	0.6 ± 0.30	5.4 ± 1.34	3.9 ± 1.92	8.7 ± 3.62	7.0 ± 3.62	25.0 ± 12.69
	中龄林 Middle-aged forest	9.8 ± 2.19	1.8 ± 0.88	0.8 ± 0.52	1.1 ± 0.44	1.5 ± 0.27	14.9 ± 2.87	3.6 ± 1.69	0.3 ± 0.10	1.2 ± 0.47	20.0 ± 6.16
	近熟林 Near mature forest	32.5 ± 16.87	4.7 ± 1.31	2.0 ± 1.07	2.6 ± 0.88	3.6 ± 1.11	45.4 ± 17.76	1.2 ± 0.52	0.2 ± 0.07	0.6 ± 0.25	47.5 ± 19.42
	成熟林 Mature forest	49.4 ± 17.94	6.5 ± 2.22	2.8 ± 1.18	3.6 ± 1.36	5.0 ± 2.24	67.2 ± 19.86	0.7 ± 0.38	0.2 ± 0.07	0.8 ± 0.38	68.9 ± 25.26
山杨林 Populus davidiana forest	幼龄林 Young forest	8.3 ± 1.76	0.8 ± 0.20	0.3 ± 0.16	0.6 ± 0.26	1.0 ± 0.55	11.0 ± 1.99	4.6 ± 2.59	3.7 ± 2.14	0.5 ± 0.15	19.8 ± 2.58
	中龄林 Middle-aged forest	16.2 ± 5.19	1.6 ± 0.67	0.7 ± 0.30	1.0 ± 0.38	1.6 ± 0.52	20.9 ± 6.58	3.9 ± 1.87	2.4 ± 1.37	1.5 ± 0.70	28.7 ± 7.19
	近熟林 Near mature forest	28.7 ± 9.42	2.8 ± 0.94	1.2 ± 0.63	1.5 ± 0.91	2.2 ± 0.88	36.3 ± 9.64	2.3 ± 0.82	3.0 ± 1.68	2.1 ± 0.95	43.7 ± 11.75
	成熟林Mature forest	52.8 ± 16.83	5.1 ± 1.98	2.2 ± 0.51	2.3 ± 1.25	3.3 ± 1.46	65.7 ± 17.87	4.3 ± 2.51	3.8 ± 2.05	2.9 ± 1.26	76.6 ± 20.45

[1]	宋语涵, 张鹏, 金光泽. 阔叶红松林不同演替阶段灌木叶片碳氮磷化学计量特征及其影响因素[J]. 植物生态学报, 2021, 45(9): 952-960.
[2]	魏红, 满秀玲. 中国寒温带不同林龄白桦林碳储量及分配特征[J]. 植物生态学报, 2019, 43(10): 843-852.
[3]	岑宇, 王成栋, 张震, 任侠, 刘美珍, 杨帆. 河北省天然草地生物量和碳密度空间分布格局[J]. 植物生态学报, 2018, 42(3): 265-276.
[4]	杨昊天, 王增如, 贾荣亮. 腾格里沙漠东南缘荒漠草地不同群落类型土壤有机碳分布及储量特征[J]. 植物生态学报, 2018, 42(3): 288-296.
[5]	闫宝龙, 王忠武, 屈志强, 王静, 韩国栋. 围封对内蒙古典型草原与荒漠草原植被-土壤系统碳密度的影响[J]. 植物生态学报, 2018, 42(3): 327-336.
[6]	李茜, 王芳, 曹扬, 彭守璋, 陈云明. 陕西省森林土壤固碳特征及其影响因素[J]. 植物生态学报, 2017, 41(9): 953-963.
[7]	崔光帅, 张林, 沈维, 刘新圣, 王媛韬. 西藏雅鲁藏布江流域中段砂生槐灌丛生物量分配及碳密度[J]. 植物生态学报, 2017, 41(1): 53-61.
[8]	杨路存, 李长斌, 宁祎, 聂秀青, 徐文华, 周国英. 青海高寒金露梅灌丛碳密度及其分配格局[J]. 植物生态学报, 2017, 41(1): 62-70.
[9]	赵玮, 胡中民, 杨浩, 张雷明, 郭群, 乌志颜, 刘德义, 李胜功. 浑善达克沙地榆树疏林和小叶杨人工林碳密度特征及其与林龄的关系[J]. 植物生态学报, 2016, 40(4): 318-326.
[10]	汲玉河, 郭柯, 倪健, 徐小牛, 王志高, 王树东. 安徽省森林碳储量现状及固碳潜力[J]. 植物生态学报, 2016, 40(4): 395-404.
[11]	李银, 陈国科, 林敦梅, 陈彬, 高雷明, 简兴, 杨波, 徐武兵, 苏宏新, 赖江山, 王希华, 杨海波, 马克平. 浙江省森林生态系统碳储量及其分布特征[J]. 植物生态学报, 2016, 40(4): 354-363.
[12]	许文强, 杨辽, 陈曦, 高亚琪, 王蕾. 天山森林生态系统碳储量格局及其影响因素[J]. 植物生态学报, 2016, 40(4): 364-373.
[13]	黄晓琼, 辛存林, 胡中民, 李钢铁, 张铜会, 赵玮, 杨浩, 张雷明, 郭群, 岳永杰, 高润宏, 乌志颜, 闫志刚, 刘新平, 李玉强, 李胜功. 内蒙古森林生态系统碳储量及其空间分布[J]. 植物生态学报, 2016, 40(4): 327-340.
[14]	杨怀, 李意德, 任海, 骆土寿, 陈仁利, 刘文杰, 陈德祥, 许涵, 周璋, 林明献, 杨秋, 姚海荣, 周国逸. 海南岛热带原始森林主要分布区土壤有机碳密度及影响因素[J]. 植物生态学报, 2016, 40(4): 292-303.
[15]	关晋宏, 杜盛, 程积民, 吴春荣, 李国庆, 邓磊, 张建国, 何秋月, 时伟宇. 甘肃省森林碳储量现状与固碳速率[J]. 植物生态学报, 2016, 40(4): 304-317.