1 2 IBIS model and its use to simulate trends for the Qinghai-Tibetan Plateau The Integrated Biosphere Simulator (IBIS) is designed to integrate a variety of 3 terrestrial ecosystem processes within a single, physically consistent modeling framework 4 (Coe et al., 2002). It represents land surface processes, canopy physiology, vegetation 5 phenology, long-term vegetation dynamics, and carbon cycling (Coe et al., 2002, Foley et 6 al., 1996, Kucharik et al., 2000). The hydrological module of IBIS is based on a land- 7 surface-transfer scheme (Thompson & Pollard, 1995a, Thompson & Pollard, 1995b). 8 Two canopy layers, three snow layers, and six soil layers are considered in each cell of 9 the landscape grid. IBIS represents natural vegetation using plant functional types (PFTs), 10 each of which is characterized in terms of its biomass and leaf area index. For each PFT, 11 IBIS adopts a mechanistic treatment of canopy photosynthesis based on the methods of 12 Farquhar et al. (1980) and Farquhar and Sharkey (1982), and uses a semi-mechanistic 13 model of stomatal conductance (Ball et al., 1986, Foley et al., 1996, Kucharik et al., 2000) 14 to quantify the gross primary productivity. A dynamic vegetation mechanism is adopted 15 to simulate changes in the vegetation structure on an annual time step as a result of 16 competition among PFTs for light and water from common resource pools (Kucharik et 17 al., 2006). The competition between PFTs depends on differences in resource availability, 18 carbon allocation, vegetation phenology, leaf form, and photosynthetic pathway (Foley et 19 al., 1996, Kucharik et al., 2000). 20 The variations of net primary production, soil respiration, and net ecosystem 21 production on the Qinghai-Tibetan Plateau that were simulated in this study were 22 extracted from a country-scale simulation of China created using IBIS (Zhu et al., 2012). 23 A 0.085°resolution land mask map of China was used in the IBIS simulations. The map 24 excluded bodies of water and some areas for which soil information was unavailable. A 25 hole-filled version of the Shuttle Radar Topography Mission digital elevation model 26 dataset (Jarvis et al., 2006) for China was re-sampled to 0.085° resolution and used as the 27 input topographic data. A 1:1 000 000 China soil map provided the fractions of sand, clay, 28 and silt particles for each soil layer and each cell (Shi et al., 2004). The 1:4 000 000 29 China vegetation map was reclassified into IBIS-specific vegetation types to initialize the 30 simulation (Hou et al., 1979). A 1-km-resolution land cover map of China from 2000 1 31 (Data Center for Resources and Environmental Sciences Chinese Academy of Sciences 32 (RESDC), 2001) was used to construct a vegetation cover layer for each cell in the grid, 33 allowing a detailed representation of the current land use and land cover conditions in the 34 simulation. These data are resampled to the resolution of 0.085°. 35 Two projected future climate datasets under the IPCC SRES scenarios (A2 and B1) 36 (IPCC, 2007) were selected from the third version of the Canadian Centre for Climate 37 Modeling and Analysis Coupled Global Climate Model (CGCM3.1). Emission scenarios 38 SRES A2 and SRES B1 represent high and low greenhouse gas emission levels, 39 respectively, in this study. Averaged observed meteorological data based on more than 40 650 stations obtained from Meteorological Bureau of China (precipitation, air 41 temperature, relative humidity, and cloudiness fraction) from 1950 to 2006 were used as 42 the baseline climate conditions. The relative climate forcing data were resampled to 43 resolution of 0.085° using thin spline interpolation methods. The CO2 concentration was 44 defined for each year of the simulation using the values in the SRES A2 and SRES B1 45 scenarios. In 2100, the CO2 concentration is projected to increase to 836 ppmv under 46 scenario SRES A2 and to 540 ppmv under scenario SRES B1 (IPCC, 2001). Simulations 47 were performed using the abovementioned soil texture data, initial vegetation conditions, 48 and projected climate data. The simulation results from 1960 to 2100 were then selected 49 for analysis. 50 Validation of IBIS in China and on the Qinghai-Tibetan Plateau 51 From our previous studies using IBIS in China, simulated runoff captured the 52 quantity pattern quite well; the simulated ET matched reasonably with estimated ET that 53 is calculated as the residual of observed precipitation and runoff (Zhu et al., 2010b). 54 Comparison between the observed and simulated soil moisture showed that mean errors 55 are within 10% for all the months and root mean squared errors are within 10% for most 56 of the seasons (Zhu et al., 2009). Validation for soil temperature simulation based on 650 57 stations observed data (from 1955 to 2000) shows that IBIS model performs well in 58 capturing spatial and temporal patterns of soil temperature (Zhu et al., 2010a). Validation 59 and comparison showed reasonable agreement for variables related to carbon exchange 2 60 processes using forestry inventory data (for net primary productivity and biomass 61 validation), flux site data (for gross primary productivity validation), and literature 62 reported data (for net primary productivity and biomass validation) at regional (Zhu et al., 63 2011a) and national (Zhu et al., 2011b) scales. 64 The simulated annual NPP of QTP was compared with the MODIS NPP product, 65 based on the multi-year average from 2000 to 2010. The 1 km MODIS NPP (MOD17A3; 66 collection 5) was obtained from the Numerical Terradynamic Simulation Group 67 (www.ntsg.umt.edu) (Zhao & Running, 2010, Zhao et al., 2005). Nearly 2000 random 68 points were generated on QTP to extract the corresponding values from the NPP layers of 69 simulated and MODIS product. The compared scatter plot is shown as Appendix Figure 1, 70 which indicates quite reasonable modeled NPP using IBIS on QTP. The points marked by 71 dashed circle, with the percentage of 7.5% of all the points, showed the NPP was 72 underestimated by the model. However, most of the comparing scattered points (92.5%, 73 marked by solid circle) were close to the 1:1 line, which indicted the model performed 74 well. 75 References 76 77 78 79 80 81 82 83 84 85 86 87 88 89 90 91 92 93 94 Ball JT, Woodrow IE, Berry JA (1986) A model predicting stomatal conductance and its contribution to the control of photosynthesis under different environmental condition. In: Progress in Photosynthesis Research. (ed Biggings J) pp Page., Martinus Nijhoff. Coe MT, Costa MH, Botta AL, Birkett C (2002) Long-term simulations of discharge and floods in the Amazon Basin. 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