Study on Carbon Budget for Ecosystems of China: Aspects and Progress Yao Huang ([email protected]) Institute of Atmospheric Physics Chinese Academy of Sciences SCIENTIFIC THEMES FOR CHINESE SCIENTISTS 1. How do C sources and sinks vary over time for different ecosystems? 2. How do patterns of C sources and sinks distribute regionally? 3. Key factors driving the processes of C cycling in different ecosystems? SCIENTIFIC THEMES FOR CHINESE SCIENTISTS 4. Responses of different ecosystems to the global change? 5. Options that can enhance the C storage and/or reduce the C emissions from different ecosystems? Projects • Study on Carbon Budget in Terrestrial and Marginal Sea Ecosystems of China, CBTSEC launched by the Chinese Academy of Sciences (2001~2005) • Carbon Cycle and Driving Mechanisms in China Terrestrial Ecosystems, CCDMCTE supported by the Ministry of Science and Technology of China (2003~2007) Objectives of the CBTSEC 1. To clarify the characteristics of C fluxes and reservoirs for different ecosystems 2. To address the role of climate, soil and human actions playing in the terrestrial C cycling processes 3. To compile an inventory of current C budget regarding to the terrestrial ecosystems of China 4. To evaluate the potential response of ecosystems to projected global change 5. To assess the contribution of land-use and land-cover change (LUCC) to C sink/source relationship during the last 100-year period 6. To develop techniques that can enhance the C storage and/or reduce C emissions I: Measurements of C fluxes and reservoirs (Eddy covariance, Static chamber/GC system, RS) Characteristics of C fluxes and reservoirs for typical ecosystems III: History of C cycling: LUCC II: Biogeochemical processes of C cycling: Responses of C cycling to climate, soil and human activities IV: C Model: Assimilation & Respiration V: Patterns of C sources/ sinks and options 1. Seasonal variation of C sources/sinks: Model output 2. Regional distribution of C sources/sinks: Model + GIS + RS output 3. Response of ecosystems to projected global change: C-model+GCM+GIS output 4. Potential in enhancing C storage 5. Options for mitigating C emissions and/or enhancing C storage Framework of the CBTSEC Topics and Progress of the CBTSEC 1 Carbon fluxes and reservoirs in typical Chinese terrestrial and marginal sea ecosystems Key aspects: Observations and measurements in situ Eddy covariance Static chamber/GC system Remote sensing Establishment of ChinaFlux network Eddy covariance, Static Chamber/GC, Remote Sensing Observations and measurements in situ (Eddy Covariance) 40 Higher NEE in forest 30 20 10 Temperate conifer-broadleaved forest (42°24’N, 128°28’E, 763m) 0 -10 -20 -30 Jul-02 Oct-02 Jan-03 May-03 Aug-03 Nov-03 Mar-04 Jun-04 Sep-04 30 Higher NEE in cropland 20 10 0 -10 -20 -30 -40 -50 Cropland (36°57’N, 116°36’E, 20m) Jan-03 May-03 Aug-03 Nov-03 Mar-04 -60 Oct-02 Jun-04 Sep-04 10 Lower NEE in high-frigid brush 5 0 -5 -10 -15 High-frigid brush (37°45’N, 101°12’E, 3200m) Jan-03 May-03 Aug-03 Nov-03 Mar-04 Jun-04 -20 Oct-02 Sep-04 Observations and measurements in situ Static chamber Soil respiration (mgCO 2/m 2/hr) Respiration from forest soil is higher than that from soils of cropland and grassland 900 Forest 800 Cropland 700 Grassland 600 500 400 300 200 100 0 07-03-02 10-01-02 12-30-02 03-30-03 06-28-03 Date (mm-dd-yy) 09-26-03 12-25-03 03-24-04 Increased atmospheric CO2 concentration enhanced CH4 emission from rice paddy FACE Ambient CO2 100 常绿针叶 50 落叶针叶 针阔混交 常绿阔叶 落叶阔叶 草地 0 灌丛 荒漠 农田 无植被 Percentage of land cover from RS 750 Identification of land cover from RS 375 0 Annual NPP from RS 2 Biogeochemical processes of C cycling in different ecosystems of China Key aspects: Decomposition and retention of the litter-C in forest ecosystems as influenced by climate Processes of C cycling in typical pasture ecosystems such as temperate grass and highfrigid meadow grass Key factors and mechanisms regulating organic C balance in agricultural soils Carbon released from litter decomposition accounted for ~30% of soil respiration in temperate conifer-broadleaved forest Partition of net photosynthesis (%) Some 17% of net photosynthesis of maize and soybean is released through rhizospheric respiration 100 80 60 40 20 0 Aboveground-C Root-C Soil-C Component Rhizospheric Resp-C 35 wheat rice 25 -1 -1 Rd (µmol kg s ) 30 20 15 10 R d = 4.74(0.36)N - 1.45 (R 2 = 0.83, n =152) 5 0 0 2 4 6 8 N (%) Crop dark respiration increased with tissue N concentration Plant root contributes greatly to soil carbon in grassland 3 Patterns of C sinks and sources and the response to global change Key aspects: Modeling C emission/assimilation Integration of C models with GCMs, GIS and RS Geographical and temporal patterns of C sources and sinks Response of different ecosystems to the global change Models are developed for the sections of forest, grassland, cropland and wetland, respectively. Upscaling: integration of models and GIS and RS Upscaling: daily weather (10km× 10km) Upscaling: soil parameter (10km× 10km) Upscaling: cropping system (10km×10km) 4 LUCC and mitigation options Key aspects: Contribution of LUCC to the C cycling Options for mitigating C emissions and/or enhancing C storage Arable land increased from 1661 to 1950 while decreased thereafter 110 Average CLAI 105 100 95 90 85 80 75 70 1650 1700 1750 1800 1850 1900 1950 2000 Year Contribution to SOC(%) There is a great potential for enhancing C storage in agricultural soils 60 50 40 30 20 10 0 synthetic fertilizer crop straw amendment no-tillage Agricultural practice 16 18 Fengqiu (after12-year) 12 10 16 14 SOM(g kg-1) SOM (g kg-1) 14 8 6 4 12 Yingtan (after14-year) 10 8 6 4 2 2 0 0 1/2OM CK NK NP Treatment NPK OM PK Original CK NK PK Treatment NP NPK Institutes are involved in the CBTSEC Institute of geography science and resource Institute of Atmospheric Physics Institute of Applied Ecology Institute of Soil Sciences Institute of Botany Sciences Institute of Remote Sensing Center of Ecology and Environment Sciences Chinese Ecosystem Research Network … Thank You
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