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1.
中国湿地土壤碳库保护与气候变化问题   总被引:10,自引:0,他引:10  
 中国湿地分布广, 类型丰富, 但存在着垦殖率高、碳密度较低、围垦损失严重等问题。估计我国湿地土壤碳库达8~10 Pg, 占全国陆地土壤总有机碳库的约1/10~1/8, 过去50 a间的损失可能达1.5 Pg。围垦和过度放牧是我国湿地土壤退化和碳库损失的主要驱动因子。目前,湿地土壤碳库保护面临严峻的挑战,从应对气候变化和保护人类生存环境的战略高度切实加强湿地资源保护,可以为增强陆地生态系统碳汇、探寻温室气体减排的潜在途径提供技术支持。  相似文献   

2.
中国土壤有机碳库及其演变与应对气候变化   总被引:33,自引:0,他引:33  
 通过综述和评价中国土壤,特别是农田土壤有机碳库(以下简称碳库)的现状与演变态势, 讨论其对我国应对气候变化的意义, 提出了我国土壤碳库及其演变与应对气候变化的基本国情是:1) 我国土壤背景碳储量较低且区域分布不均衡;2) 我国土壤固碳效应明显,未来固碳减排潜力显著;3) 技术和政策是实现和提高我国土壤碳汇、促进我国应对气候变化能力建设的重要途径。建议进一步加强对我国农田土壤固碳减排的研发投入, 完善农业应对气候变化的相关政策和鼓励措施体系,研究构建气候友好的新型农业,以期在提高和稳定农业生产力与应对气候变化能力上获得双赢。  相似文献   

3.
中国土壤有机碳库及其演变与应对气候变化   总被引:1,自引:0,他引:1  
通过综述和评价中国土壤,特别是农田土壤有机碳库(以下简称碳库)的现状与演变态势, 讨论其对我国应对气候变化的意义, 提出了我国土壤碳库及其演变与应对气候变化的基本国情是:1) 我国土壤背景碳储量较低且区域分布不均衡;2) 我国土壤固碳效应明显,未来固碳减排潜力显著;3) 技术和政策是实现和提高我国土壤碳汇、促进我国应对气候变化能力建设的重要途径。建议进一步加强对我国农田土壤固碳减排的研发投入, 完善农业应对气候变化的相关政策和鼓励措施体系,研究构建气候友好的新型农业,以期在提高和稳定农业生产力与应对气候变化能力上获得双赢。  相似文献   

4.
基于2005年4~10月盘锦湿地芦苇群落土壤不同土层土壤碱解氮及溶解性有机碳的观测资料,分析了盘锦湿地芦苇群落土壤碱解氮与溶解性有机碳(DOC)的季节动态。结果表明:不同土层碱解氮、溶解性有机碳的季节动态并不相同。0~10 cm土层碱解氮与DOC季节动态相似,6月土壤碱解氮与DOC含量均最高,分别为244.86 mg/kg和13.16 mg/L。8月碱解氮含量最低,为139.18 mg/kg;9月DOC含量最低。10~20 cm土层DOC的季节性动态变化与表土具有相似性,峰值均出现在6月,谷值出现在9月;10~20 cm土层碱解氮最低值出现在6月,与0~10 cm土层不同。20~30 cm土层内,4~7月DOC几乎无变化,8月DOC含量最低,9月增加;4~5月碱解氮波动较大,5月降到102 mg/kg,6月增加到151 mg/kg。研究表明,盘锦湿地芦苇群落土壤微生物活性与凋落物分解对DOC及碱解氮的季节动态有很大的影响,同时温度、降水量及冻融也影响着DOC及碱解氮的季节动态。  相似文献   

5.
6kaBP中国陆地生态系统净初级生产力的模拟   总被引:1,自引:0,他引:1       下载免费PDF全文
利用植被与大气相互作用模式(AVIM)模拟了全新世中期(6 kaBP)及现代中国陆地植被净初级生产力(NPP)的大小与分布特征,计算了以上两个时期我国陆地植被NPP的碳总量。结果表明:全新世中期以来气候的变化是影响我国陆地植被NPP变化的主要原因,6 kaBP时期NPP平均值为409 g/(m2·a), NPP碳总量为3.89 Pg/a,分别比现在高15%和19%。全新世中期至今,我国陆地植被NPP的变化特征与对应时期中国土壤碳储量的变化趋势具有很好的一致性,这表明了利用生态模式模拟长时间尺度下我国陆地植被NPP的变化特征是可行的。  相似文献   

6.
陆地生态系统碳汇显著降低大气CO2浓度上升和全球变暖的速率,受人类活动和气候变化的影响,陆地生态系统碳通量具有强烈的时空变化,其估算结果仍存在较大的不确定性,不同因子的贡献尚不清晰。为此,利用遥感驱动的陆地生态系统过程模型BEPS模拟分析了1981—2019年全球陆地生态系统碳通量的时空变化特征,评价了大气CO2浓度、叶面积指数(Leaf Area Index,LAI)、氮沉降、气候变化对全球陆地生态系统碳收支变化的贡献。1981—2019年全球陆地生态系统总初级生产力(Gross Primary Productivity,GPP)、净初级生产力(Net Primary Productivity,NPP)和净生态系统生产力(Net Ecosystem Productivity,NEP)的平均值分别为115.3、51.3和2.7 Pg·a-1(以碳质量计,下同),上升速率分别为0.47、0.21和0.06 Pg·a-1。全球大部分区域GPP和NPP显著增加,NEP显著上升(p<0.05)的区域明显少于GPP和NPP。1981—2019年,全球NEP累积为105.2 Pg,森林、稀树草原及灌木、农田和草地的贡献分别为76.4、15.8、9.4和3.6 Pg。CO2浓度、LAI、氮沉降和气候变化各自对NEP的累积贡献分别为58.4、20.6、0.7和-43.6 Pg,全部4个因子变化对NEP的累积贡献为39.8 Pg,其中CO2浓度上升是近40 a全球陆地生态系统NEP上升的主要贡献因子,其次为LAI。  相似文献   

7.
为了应对全球气候变化带来的挑战,2020年9月中国提出努力争取在2060年前实现碳中和。对此,生态系统固碳被寄予厚望;然而,生态学理论认为,成熟生态系统的碳输入输出趋于平衡,没有碳的净积累,也就没有碳汇功能,而未成熟的生态系统虽有碳的净积累并具有碳汇功能,但自然界任何未成熟生态系统从它建立的时候开始都在不断地向成熟生态系统演替,即任一生态系统演替的最终结果必然是碳输入输出达到平衡状态。由于森林生态系统碳库是陆地生态系统中最大的碳库,所以人们对其在碳中和上的贡献充满期待。本文以森林生态系统为例,分别考虑森林生态系统碳库的生物量碳库和土壤有机碳库,并基于全球最新研究成果,论证了森林生态系统土壤碳库积累过程具有长久的固碳功能,且不违背成熟生态系统碳输入输出趋于平衡的生态学理论,它能为实现碳中和目标做出贡献。  相似文献   

8.
全新世中国陆地生态系统碳储量变化的估算   总被引:1,自引:0,他引:1  
 利用重建的中国全新世植被图和现代植被碳密度资料,初步估算了全新世期间中国及其分区每2 ka陆地生态系统碳储量的变化情况。结果表明:近10 ka期间,中国陆地生态系统碳储量在6 ka BP前后达到最大,此后开始降低,尤其是近2 ka降幅明显。新石器时期,特别是农业文明开始以后,人类活动对陆地植被的持续干预可能是造成陆地生态系统碳储量长期减少的主要原因。  相似文献   

9.
利用重建的中国全新世植被图和现代植被碳密度资料,初步估算了全新世期间中国及其分区每2 ka陆地生态系统碳储量的变化情况。结果表明:近10 ka期间,中国陆地生态系统碳储量在6 ka BP前后达到最大,此后开始降低,尤其是近2 ka降幅明显。新石器时期,特别是农业文明开始以后,人类活动对陆地植被的持续干预可能是造成陆地生态系统碳储量长期减少的主要原因。  相似文献   

10.
陆地生态系统氮循环对碳循环过程及其对气候变化的反馈具有重要的影响,但当前陆面模式多数都没有考虑氮循环过程对碳循环过程的限制。本研究基于氮在土壤-植被-大气中的传输交换过程,将氮循环过程引入到陆面模式AVIM(Atmosphere-Vegetation Interaction Model)中,发展形成包含碳氮耦合过程的新版模式AVIM-CN。与2004-05年当雄生态系统定位站通量观测数据相对比,模式中引入氮循环过程后,高寒草甸的总初级生产力模拟值从1.1403 gC m-2d-1降到了0.7073 gC m-2d-1,前者更接近通量站的观测值0.5407 gC m-2d-1。生态系统呼吸的模拟值也从1.7695 gC m-2d-1降到了1.0572 gC m-2d-1,更接近对应的通量观测值0.8034 gC m-2d-1。整体而言,在模式中考虑氮的限制作用后,当雄站的热量通量和碳通量的模拟值更接近实测值。不考虑氮过程对碳过程的限制,模式高估了约40%的陆地生态系统碳通量。  相似文献   

11.
The interest in the national levels of the terrestrial carbon sink and its spatial and temporal variability with the climate and CO2 concentrations has been increasing. How the climate and the increasing atmospheric CO2 concentrations in the last century affect the carbon storage in continental China was investigated in this study by using the Modified Sheffield Dynamic Global Vegetation Model (M-SDGVM). The estimates of the M-SDGVM indicated that during the past 100 years a combination of increasing CO2 with historical temperature and precipitation variability in continental China have caused the total vegetation carbon storage to increase by 2.04 Pg C, with 2.07 Pg C gained in the vegetation biomass but 0.03 Pg C lost from the organic soil carbon matter. The increasing CO2 concentration in the 20th century is primarily responsible for the increase of the total potential vegetation carbon. These factorial experiments show that temperature variability alone decreases the total carbon storage by 1.36 Pg C and precipitation variability alone causes a loss of 1.99 Pg C. The effect of the increasing CO2 concentration alone increased the total carbon storage in the potential vegetation of China by 3.22 Pg C over the past 100 years. With the changing of the climate, the CO2 fertilization on China's ecosystems is the result of the enhanced net biome production (NBP), which is caused by a greater stimulation of the gross primary production (GPP) than the total soil-vegetation respiration. Our study also shows notable interannual and decadal variations in the net carbon exchange between the atmosphere and terrestrial ecosystems in China due to the historical climate variability.  相似文献   

12.
Activities to reduce net greenhouse gas emissions by biological soil or forest carbon sequestration predominantly utilize currently known, readily implementable technologies. Many other greenhouse gas emission reduction options require future technological development or must wait for turnover of capital stock. Carbon sequestration options in soils and forests, while ready to go now, generally have a finite life, allowing use until other strategies are developed. This paper reports on an investigation of the competitiveness of biological carbon sequestration from a dynamic and multiple strategy viewpoint. Key factors affecting the competitiveness of terrestrial mitigation options are land availability and cost effectiveness relative to other options including CO2 capture and storage, energy efficiency improvements, fuel switching, and non-CO2 greenhouse gas emission reductions. The analysis results show that, at lower CO2 prices and in the near term, soil carbon and other agricultural/forestry options can be important bridges to the future, initially providing a substantial portion of attainable reductions in net greenhouse gas emissions, but with a limited role in later years. At higher CO2 prices, afforestation and biofuels are more dominant among terrestrial options to offset greenhouse gas emissions. But in the longer run, allowing for capital stock turnover, options to reduce greenhouse gas emissions from the energy system and biofuels provide an increasing share of potential reductions in total US greenhouse gas emissions.  相似文献   

13.
Soil Carbon Sequestration in India   总被引:4,自引:0,他引:4  
R. Lal 《Climatic change》2004,65(3):277-296
With a large land area and diverse ecoregions, there is a considerable potential of terrestrial/soil carbon sequestration in India. Of the total land area of 329 million hectares (Mha), 297 Mha is the land area comprising 162 Mha of arable land, 69 Mha of forest and woodland, 11 Mha of permanent pasture, 8 Mha of permanent crops and 58 Mha is other land uses. Thesoil organic carbon (SOC) pool is estimated at 21 Pg (petagram = Pg = 1 ×1015 g= billion ton) to 30-cm depth and 63 Pg to 150-cm depth. The soil inorganic carbon (SIC) pool is estimated at 196 Pg to 1-m depth. The SOC concentration in most cultivated soils is less than 5 g/kg compared with 15 to 20 g/kg in uncultivated soils. Low SOC concentration is attributed to plowing, removal of crop residue and other biosolids, and mining of soil fertility. Accelerated soil erosion by water leads to emission of 6 Tg C/y. Important strategies of soil C sequestration include restoration of degraded soils, and adoption of recommended management practices (RMPs) of agricultural and forestry soils. Potential of soil C sequestration in India is estimated at 7 to 10 Tg C/y for restoration of degraded soils and ecosystems, 5 to 7 Tg C/y for erosion control, 6 to 7 Tg C/y for adoption of RMPs on agricultural soils, and 22 to 26 Tg C/y for secondary carbonates. Thus, total potential of soil C sequestration is 39 to 49 (44± 5) Tg C/y.  相似文献   

14.
Terrestrial carbon pools in southeast and south-central United States   总被引:1,自引:0,他引:1  
Analyses of regional carbon sources and sinks are essential to assess the economical feasibility of various carbon sequestration technologies for mitigating atmospheric CO2 accumulation and for preventing global warming. Such an inventory is a prerequisite for regional trading of CO2 emissions. As a U.S. Department of Energy Southeast Regional Carbon Sequestration Partner, we have estimated the state-level terrestrial carbon pools in the southeast and south-central US. This region includes: Alabama, Arkansas, Florida, Georgia, Louisiana, Mississippi, North Carolina, South Carolina, Tennessee, Texas, and Virginia. We have also projected the potential for terrestrial carbon sequestration in the region. Texas is the largest contributor (34%) to greenhouse gas emission in the region. The total terrestrial carbon storage (forest biomass and soils) in the southeast and south-central US is estimated to be 130 Tg C/year. An annual forest carbon sink (estimated as 76 Tg C/year) could compensate for 13% of the regional total annual greenhouse gas emission (505 Tg C, 1990 estimate). Through proper policies and the best land management practices, 54 Tg C/year could be sequestered in soils. Thus, terrestrial sinks can capture 23% of the regional total greenhouse emission and hence are one of the most cost-effective options for mitigating greenhouse emission in the region.  相似文献   

15.
Mitigating the potential large negative impacts of a change in the earth's climate will require strong and definite actions in the different economic sectors, particularly within agriculture and forestry. Specifically, soils deserve a close examination due to their large carbon mitigation potential. The Kyoto protocol establishes the possibility for crediting greenhouse gas emission reductions from forestry and agriculture activities. In most circumstances, particularly those regarding developing countries, greenhouse gas mitigation activities will be carried out through projects. These projects will have to meet a series of criteria, for the carbon benefits to be measurable, transparent, verifiable and certified. These criteria include: establishing credible baselines (without-project or reference scenario), additionality, permanence, quantifying and reducing potential leakage of greenhouse gases across project borders, coping with natural or human induced risks, accurately measuring changes in carbon stocks using carbon accounting techniques, and – in the case of the Clean DevelopmentMechanism – resulting in sustainable development benefits. In this paper we describe the methods and approaches that have been developed to cope with the different criteria and discuss their implications for carbon sequestration in soils. Soil carbon represents the largest carbon pool of terrestrial ecosystems, and has been estimated to have one of the largest potentials to sequester carbon worldwide. However, getting credits from soil carbon sequestration through project activities presents several challenges: the need to monitor small incremental changes in soil carbon content relative to large carbon pools, long-time periods to accrue the full carbon benefits, high local variability of soil carbon content, and relatively costly soil carbon measurement procedures. Also, the responses of soil C stocks to forestry and agriculture activities are complex and need careful attention. Specifically, the time dynamics of soil C responses to land use changes, the diversity of soil types, soil-plant interactions, and the availability of accurate soil C inventories, should be considered to successfully implement LULUCF projects.  相似文献   

16.
Principles and substantiation of a system of monitoring anthropogenic greenhouse gas emissions and sinks are considered. The basic task of the system is to estimate the anthropogenic contribution to the atmospheric greenhouse gas concentrations and possible climate effect. The major attention is paid to the system of indirect or “computational” monitoring of anthropogenic greenhouse gases. A multifunctional information system is described in the context of its application for solving a number of other ecological problems. It can be used as an instrumental basis for estimating ecological efficiency of measures aimed at reducing emissions and increasing greenhouse gas uptake. The effect should be considered in totality for all greenhouse gases and most hazardous pollutants. Monitoring of anthropogenic greenhouse gas emissions and sinks includes observations (using modeling) of integral indicators of ecosystems and can be used as part of ecological monitoring (for example, dynamics of soil carbon balance of agroecosystems and forest cenoses). The connection of the monitoring of anthropogenic greenhouse gas emissions and sinks with the satellite monitoring enlarges the possible applications of this information system.  相似文献   

17.
Offsetting China's CO2 Emissions by Soil Carbon Sequestration   总被引:4,自引:0,他引:4  
R. Lal 《Climatic change》2004,65(3):263-275
Fossil fuel emissions of carbon (C) in China in 2000 was about 1 Pg/yr, which may surpass that of the U.S. (1.84 Pg C) by 2020. Terrestrial C pool of China comprises about 35 to 60 Pg in the forest and 120 to 186 Pg in soils. Soil degradation is a major issue affecting 145 Mha by different degradative processes, of which 126 Mha are prone to accelerated soil erosion. Similar to world soils, agricultural soils of China have also lost 30 to 50% or more of the antecedent soil organic carbon (SOC) pool.Some of the depleted SOC pool can be re-sequestered through restoration of degraded soils, and adoption of recommended management practices. The latter include conversion of upland crops to multiple cropping and rice paddies, adoption of integrated nutrient management (INM) strategies, incorporation of cover crops in the rotations cycle and adoption of conservation-effective systems including conservation tillage. A crude estimated potential of soil C sequestration in China is 119 to 226 Tg C/y of SOC and 7 to 138 Tg C/y for soil inorganic carbon (SIC) up to 50 years. The total potential of soil C sequestration is about 12 Pg, and this potential can offset about 25%of the annual fossil fuel emissions in China.  相似文献   

18.
This article reviews recent advances over the past 4 years in the study of the carbon-nitrogen cycling and their relationship to climate change in China. The net carbon sink in the Chinese terrestrial ecosystem was 0.19-0.26 Pg C yr-1 for the 1980s and 1990s. Both natural wetlands and the rice-paddy regions emitted 1.76 Tg and 6.62 Tg of CH 4 per year for the periods 1995-2004 and 2005-2009, respectively. China emitted~1.1 Tg N 2 O-N yr-1 to the atmosphere in 2004. Land soil contained~8.3 Pg N. The excess nitrogen stored in farmland of the Yangtze River basin reached 1.51 Tg N and 2.67 Tg N in 1980 and 1990, respectively. The outer Yangtze Estuary served as a moderate or significant sink of atmospheric CO 2 except in autumn. Phytoplankton could take up carbon at a rate of 6.4 ×10 11 kg yr-1 in the China Sea. The global ocean absorbed anthropogenic CO 2 at the rates of 1.64 and 1.73 Pg C yr-1 for two simulations in the 1990s. Land net ecosystem production in China would increase until the mid-21st century then would decrease gradually under future climate change scenarios. This research should be strengthened in the future, including collection of more observation data, measurement of the soil organic carbon (SOC) loss and sequestration, evaluation of changes in SOC in deep soil layers, and the impacts of grassland management, carbon-nitrogen coupled effects, and development and improvement of various component models and of the coupled carbon cycle-climate model.  相似文献   

19.
Science Needs and New Technology for Increasing Soil Carbon Sequestration   总被引:9,自引:0,他引:9  
Fossil fuel use and land use change that began over 200 years ago are driving the rapid increase in atmospheric content of CO2 and other greenhouse gases that may be impacting climatic change (Houghton et al., 1996). Enhanced terrestrial uptake of CO2 over the next 50 to 100 years has been suggested as a way to reclaim the 150 or more Pg carbon (C) lost to the atmosphere from vegetation and soil since 1850 as a consequence of land use change (Batjes, 1999; Lal et al., 1998a; Houghton, 1995), thus effectively `buying time' for the development and implementation of new longer term technical solutions, such as C-free fuels. The ultimate potential for terrestrial C sequestration is not known, however, because we lack adequate understanding of (1) the biogeochemical mechanisms responsible for C fluxes and storage potential on the molecular, landscape, regional, and global scales, and (2) the complex genetic and physiological processes controlling key biological and ecological phenomena. Specifically, the structure and dynamics of the belowground component of terrestrial carbon pools, which accounts for two-thirds of global terrestrial organic C stocks, is poorly understood. Focusing primarily on forests, croplands and grasslands, the purpose of this chapter is to consider innovative technology for enhancing C sequestration in terrestrial ecosystems and address the scientific issues related to better understanding of soil C sequestration potential through appropriate and effective approaches to ecosystem management.  相似文献   

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