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RESEARCH POSTER PRESENTATION DESIGN © 2012 www.PosterPresentations.com 1. Faster Climatic Change, Sensitive Response 2. Traditional Pasture, Vulnerable Ecosystem TEMPERATE EURASIAN STEPPE(TES): convergence of climatic change and human activities 1. Terrestrial Biogeochemical Model: Prototype Model: Boreal Ecosystem Productivity Simulator (BEPS) with photosynthesis, soil carbon and terrestrial hydrological and energy scheme; Model Scheme Modifications: NPP allocation, autotrophic respiration; Parameterization on Grassland Ecosystem: V c,max Spatial Distribution, Q 10 for autotrophic respiration et al. 2. Disturbance Model: Graze Module: Modified Shiyomi grassland management scheme Fire Module: Glob-FIRM MATHETICAL ASSESSMENT ON DIAGNOSTIC TERRESTRIAL MODEL: model decomposition on GESS 1 college of life science, Nanjing University, Nanjing, China 2 Department of Microbiology and Plant Biology, University of Oklahoma, OK, US 3 NOAA National Climatic Data Center, Asheville, NC, US 4. Department of Geography, University of Toronto, Toronto, Ontario, Canada Yizhao Chen 1 , Jianlong Li 1 , Jianyang Xia 2 , Yiqi Luo 2 , Pavel Groisman 3 and Jingming Chen 4 () () () dX t BU t A CX t dt PROPER MONITOR AND PREDICTION: find suitable regional model instruments for TES The regional warming is among the fastest in the past century Grassland ecosystem is sensitive to global change, especially in arid/semi-arid areas World’s important source of agriculture products, animal products and mineral resources. Grassland degradation and desertification has been identified during the recent decades Regional study gaps: LARGE RESEARCH DISCREPANCY EXISTS Most studies are mainly concentrated on Mongol Steppe, while other regions of TES were less investigated by the international research community. FROM FIELD MEASUREMENTS TO REGIONAL MONITOR Currently research of disturbance from husbandry industry generally based on field measurements, while we need a better regional understanding. TO FIND THE BEST WE HAVE NOW AND IMPROVE IT AGAIN We have many terrestrial biosphere models with similar contracture. We need to know which one works best, where is the major uncertainty and how to make further refinement FUTURE WORK AND PERSPECTIVES MODEL PERFORMACE: Evaluation against multi-source dataset GRASSLAND ECOSYSTEM SIMULATION SYSTEM (GESS Ver. 1.0) DESIGN Most of current terrestrial biosphere models could be decomposed into a few traceable components based on following matrix model (Luo et al, 2003, Xia et al, 2013): Schematic diagram of the traceable model framework (Xia et al, 2013) carbon storage at time t. potential turnover rates. environmental scalar on carbon decomposition carbon transfer matrix net carbon influx carbon allocation carbon storage change REGIONAL RESULTS PRESENTATION (PARTLY) Regional results of (a) NPP, (b) Evaportranspiration, (c) Water use efficiency from 1982 to 2008 Regional results of (a) NPP, (b) NEP from 1999 to 2008 Regional results of graze model output from 1999 to 2008 Further model evaluation, especially for Kazakhstan Steppe; Pixel-based graze model development; Regional Model inter-comparison and benchmark. Please feel free to contact us if you are interested or have any questions about (detail of) our study E-mail: [email protected] [email protected] Main references: Xia J, Luo Y, Wang Y P, et al. Traceable components of terrestrial carbon storage capacity in biogeochemical models[J]. Global change biology, 2013, 19(7): 2104-2116. Luo Y, White L W, Canadell J G, et al. Sustainability of terrestrial carbon sequestration: a case study in Duke Forest with inversion approach[J]. Global biogeochemical cycles, 2003, 17(1). Thonicke K, Venevsky S, Sitch S, et al. The role of fire disturbance for global vegetation dynamics: coupling fire into a Dynamic Global Vegetation Model[J]. Global Ecology and Biogeography, 2001, 10(6): 661-677. Ju W, Chen J M, Black T A, et al. Modelling multi-year coupled carbon and water fluxes in a boreal aspen forest[J]. Agricultural and Forest Meteorology, 2006, 140(1): 136-151. Regional carbon residence time and baseline residence time NPP results from GESS showed good agreements with field measurements in the three sites (R 2 =0.75); GESS model performed better than original BEPS to the three sets of field measurements. The correlation in KS shows the largest R 2 enhancement with 0.14 comparing with BEPS (0.79 versus 0.65). Uncertainty Evaluation and Benchmark System Model Simulations and Modifications NPP validation against field measurements Graze module validation against field measurements Fire module validation against remote sensing database 86% of the pixels are in agreement with the L3JRC dataset. The major disagreement is from the mountainous areas in north Kazakhstan and Kyrgyzstan. the model could catch the regional temporal pattern when fire starts to appear (R 2 = 0.52) The overall correlation R 2 between model and field results is 0.71; the model usually under- estimated production during strong growth period (often from July to August) while over- estimated production during weak growth period (May and September), especially at the end of growth season. Spatial distribution of global warming trend (IPCC 5 th report) Major Disturbances in TES Schematic diagram of Main Carbon Pool and Flux in GESS GESS model framework NEESPI Synthesis conference, April 9-12,2015, Prague, Czech Republic

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Page 1: THIS SIDEBAR DOES NOT PRINT QUICK START …neespi.org/web-content/meetings/Prague_2015/Chen_poster.pdfProductivity Simulator (BEPS) with photosynthesis, soil carbon and terrestrial

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[email protected]

1. Faster Climatic Change, Sensitive Response

2. Traditional Pasture, Vulnerable Ecosystem

TEMPERATE EURASIAN STEPPE(TES): convergence of climatic change and human activities

1. Terrestrial Biogeochemical Model:

• Prototype Model: Boreal Ecosystem

Productivity Simulator (BEPS) with

photosynthesis, soil carbon and terrestrial

hydrological and energy scheme;

• Model Scheme Modifications: NPP

allocation, autotrophic respiration;

• Parameterization on Grassland Ecosystem:

Vc,max Spatial Distribution, Q10 for

autotrophic respiration et al.

2. Disturbance Model:

Graze Module: Modified Shiyomi

grassland management scheme

Fire Module: Glob-FIRM

MATHETICAL ASSESSMENT ON DIAGNOSTIC TERRESTRIAL MODEL: model decomposition on

GESS

1 college of life science, Nanjing University, Nanjing, China 2Department of Microbiology and Plant Biology, University of Oklahoma, OK, US 3NOAA National Climatic Data Center, Asheville, NC, US 4. Department of Geography, University of Toronto, Toronto, Ontario, Canada

Yizhao Chen1, Jianlong Li1, Jianyang Xia2, Yiqi Luo2, Pavel Groisman3 and Jingming Chen4

( )( ) ( )

dX tBU t A CX t

dt

PROPER MONITOR AND PREDICTION: find suitable regional model instruments for TES

• The regional warming is

among the fastest in the

past century

• Grassland ecosystem is

sensitive to global change,

especially in

arid/semi-arid areas

• World’s important source

of agriculture products,

animal products and

mineral resources.

• Grassland degradation

and desertification has

been identified during

the recent decades

Regional study gaps: • LARGE RESEARCH DISCREPANCY EXISTS

Most studies are mainly concentrated on Mongol

Steppe, while other regions of TES were less

investigated by the international research community.

• FROM FIELD MEASUREMENTS TO REGIONAL

MONITOR Currently research of disturbance from husbandry

industry generally based on field measurements, while

we need a better regional understanding.

• TO FIND THE BEST WE HAVE NOW AND

IMPROVE IT AGAIN We have many terrestrial biosphere models with

similar contracture. We need to know which one works

best, where is the major uncertainty and how to make

further refinement

FUTURE WORK AND PERSPECTIVES

MODEL PERFORMACE: Evaluation against multi-source dataset

GRASSLAND ECOSYSTEM SIMULATION SYSTEM (GESS Ver. 1.0) DESIGN

Most of current terrestrial biosphere models could be decomposed into a few traceable components based on following matrix model (Luo et al, 2003, Xia et al, 2013):

Schematic diagram of the traceable model framework (Xia et al, 2013)

carbon storage at time t.

potential turnover rates.

environmental scalar on carbon decomposition

carbon transfer matrix

net carbon influx

carbon allocation

carbon storage change

REGIONAL RESULTS PRESENTATION (PARTLY)

Regional results of (a) NPP, (b) Evaportranspiration, (c) Water use efficiency from 1982 to 2008

Regional results of (a) NPP, (b) NEP from 1999 to 2008

Regional results of graze model output from 1999 to 2008

• Further model evaluation, especially for

Kazakhstan Steppe;

• Pixel-based graze model development;

• Regional Model inter-comparison and

benchmark.

Please feel free to contact us if you are interested or have any questions about (detail of) our study

E-mail: [email protected]

[email protected]

Main references: Xia J, Luo Y, Wang Y P, et al. Traceable components of terrestrial carbon storage capacity in biogeochemical models[J]. Global change biology, 2013, 19(7): 2104-2116. Luo Y, White L W, Canadell J G, et al. Sustainability of terrestrial carbon sequestration: a case study in Duke Forest with inversion approach[J]. Global biogeochemical cycles, 2003, 17(1). Thonicke K, Venevsky S, Sitch S, et al. The role of fire disturbance for global vegetation dynamics: coupling fire into a Dynamic Global Vegetation Model[J]. Global Ecology and Biogeography, 2001, 10(6): 661-677. Ju W, Chen J M, Black T A, et al. Modelling multi-year coupled carbon and water fluxes in a boreal aspen forest[J]. Agricultural and Forest Meteorology, 2006, 140(1): 136-151.

Regional carbon residence time and baseline residence time

• NPP results from GESS showed good agreements with field measurements in the three sites (R2=0.75);

• GESS model performed better than original BEPS to the three sets of field measurements. The correlation in KS shows the largest R2 enhancement with 0.14 comparing with BEPS (0.79 versus 0.65).

Uncertainty Evaluation and

Benchmark System

Model Simulations and

Modifications

NPP validation against field measurements

Graze module validation against field measurements

Fire module validation against remote sensing database

• 86% of the pixels are in agreement with the L3JRC dataset. The major disagreement is from the mountainous areas in north Kazakhstan and Kyrgyzstan.

• the model could catch the regional temporal pattern when fire starts to appear (R2 = 0.52)

• The overall correlation R2 between model and field results is 0.71;

• the model usually under-estimated production during strong growth period (often from July to August) while over-estimated production during weak growth period (May and September), especially at the end of growth season.

Spatial distribution of global warming trend (IPCC 5th report)

Major Disturbances in TES

Schematic diagram of Main Carbon Pool and Flux in GESS

GESS model framework

NEESPI Synthesis conference, April 9-12,2015, Prague, Czech Republic