Additionally important characteristics for the warming of QTP

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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
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terrestrial ecosystem processes within a single, physically consistent modeling framework
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(Coe et al., 2002). It represents land surface processes, canopy physiology, vegetation
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phenology, long-term vegetation dynamics, and carbon cycling (Coe et al., 2002, Foley et
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al., 1996, Kucharik et al., 2000). The hydrological module of IBIS is based on a land-
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surface-transfer scheme (Thompson & Pollard, 1995a, Thompson & Pollard, 1995b).
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Two canopy layers, three snow layers, and six soil layers are considered in each cell of
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the landscape grid. IBIS represents natural vegetation using plant functional types (PFTs),
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each of which is characterized in terms of its biomass and leaf area index. For each PFT,
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IBIS adopts a mechanistic treatment of canopy photosynthesis based on the methods of
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Farquhar et al. (1980) and Farquhar and Sharkey (1982), and uses a semi-mechanistic
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model of stomatal conductance (Ball et al., 1986, Foley et al., 1996, Kucharik et al., 2000)
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to quantify the gross primary productivity. A dynamic vegetation mechanism is adopted
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to simulate changes in the vegetation structure on an annual time step as a result of
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competition among PFTs for light and water from common resource pools (Kucharik et
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al., 2006). The competition between PFTs depends on differences in resource availability,
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carbon allocation, vegetation phenology, leaf form, and photosynthetic pathway (Foley et
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al., 1996, Kucharik et al., 2000).
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The variations of net primary production, soil respiration, and net ecosystem
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production on the Qinghai-Tibetan Plateau that were simulated in this study were
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extracted from a country-scale simulation of China created using IBIS (Zhu et al., 2012).
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A 0.085°resolution land mask map of China was used in the IBIS simulations. The map
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excluded bodies of water and some areas for which soil information was unavailable. A
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hole-filled version of the Shuttle Radar Topography Mission digital elevation model
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dataset (Jarvis et al., 2006) for China was re-sampled to 0.085° resolution and used as the
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input topographic data. A 1:1 000 000 China soil map provided the fractions of sand, clay,
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and silt particles for each soil layer and each cell (Shi et al., 2004). The 1:4 000 000
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China vegetation map was reclassified into IBIS-specific vegetation types to initialize the
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simulation (Hou et al., 1979). A 1-km-resolution land cover map of China from 2000
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(Data Center for Resources and Environmental Sciences Chinese Academy of Sciences
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(RESDC), 2001) was used to construct a vegetation cover layer for each cell in the grid,
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allowing a detailed representation of the current land use and land cover conditions in the
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simulation. These data are resampled to the resolution of 0.085°.
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Two projected future climate datasets under the IPCC SRES scenarios (A2 and B1)
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(IPCC, 2007) were selected from the third version of the Canadian Centre for Climate
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Modeling and Analysis Coupled Global Climate Model (CGCM3.1). Emission scenarios
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SRES A2 and SRES B1 represent high and low greenhouse gas emission levels,
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respectively, in this study. Averaged observed meteorological data based on more than
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650 stations obtained from Meteorological Bureau of China (precipitation, air
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temperature, relative humidity, and cloudiness fraction) from 1950 to 2006 were used as
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the baseline climate conditions. The relative climate forcing data were resampled to
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resolution of 0.085° using thin spline interpolation methods. The CO2 concentration was
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defined for each year of the simulation using the values in the SRES A2 and SRES B1
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scenarios. In 2100, the CO2 concentration is projected to increase to 836 ppmv under
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scenario SRES A2 and to 540 ppmv under scenario SRES B1 (IPCC, 2001). Simulations
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were performed using the abovementioned soil texture data, initial vegetation conditions,
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and projected climate data. The simulation results from 1960 to 2100 were then selected
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for analysis.
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Validation of IBIS in China and on the Qinghai-Tibetan Plateau
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From our previous studies using IBIS in China, simulated runoff captured the
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quantity pattern quite well; the simulated ET matched reasonably with estimated ET that
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is calculated as the residual of observed precipitation and runoff (Zhu et al., 2010b).
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Comparison between the observed and simulated soil moisture showed that mean errors
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are within 10% for all the months and root mean squared errors are within 10% for most
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of the seasons (Zhu et al., 2009). Validation for soil temperature simulation based on 650
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stations observed data (from 1955 to 2000) shows that IBIS model performs well in
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capturing spatial and temporal patterns of soil temperature (Zhu et al., 2010a). Validation
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and comparison showed reasonable agreement for variables related to carbon exchange
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processes using forestry inventory data (for net primary productivity and biomass
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validation), flux site data (for gross primary productivity validation), and literature
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reported data (for net primary productivity and biomass validation) at regional (Zhu et al.,
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2011a) and national (Zhu et al., 2011b) scales.
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The simulated annual NPP of QTP was compared with the MODIS NPP product,
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based on the multi-year average from 2000 to 2010. The 1 km MODIS NPP (MOD17A3;
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collection 5) was obtained from the Numerical Terradynamic Simulation Group
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(www.ntsg.umt.edu) (Zhao & Running, 2010, Zhao et al., 2005). Nearly 2000 random
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points were generated on QTP to extract the corresponding values from the NPP layers of
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simulated and MODIS product. The compared scatter plot is shown as Appendix Figure 1,
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which indicates quite reasonable modeled NPP using IBIS on QTP. The points marked by
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dashed circle, with the percentage of 7.5% of all the points, showed the NPP was
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underestimated by the model. However, most of the comparing scattered points (92.5%,
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marked by solid circle) were close to the 1:1 line, which indicted the model performed
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well.
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References
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82
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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. Journal of Geophysical Research, 107(D20), 8044,
doi:8010.1029/2001JD000740.
Data Center for Resources and Environmental Sciences Chinese Academy of Sciences
(Resdc) (2001) National landuse dataset (1km resolution). pp Page,
http://www.geodata.cn.
Farquhar GD, Caemmerer S, Berry JA (1980) A biochemical model of photosynthetic
CO2 assimilation in leaves of C3 species. Planta, 149, 78-90.
Farquhar GD, Sharkey TD (1982) Stomatal Conductance and Photosynthesis. Annual
Review of Plant Physiology, 33, 317-345.
Foley JA, Colin PI, Ramankutty N, Levis S, Pollard D, Sitch S, Haxeltine A (1996) An
integrated biosphere model of land surface processes, terrestrial carbon balance,
and vegetation dynamics. Global Biogeochemical Cycles, 10, 603-628.
Hou X, Sun S, Zhang J (1979) The vegetation map of China (1:4,000,000) (in Chinese),
Beijing, SinoMaps Press.
3
95
96
97
98
99
100
101
102
103
104
105
106
107
108
109
110
111
112
113
114
115
116
117
118
119
120
121
122
123
124
125
126
127
128
129
130
131
132
133
134
135
136
137
138
Ipcc (2001) Climate Change 2001: The Scientific Basis. Contribution of Working Group
I to the Third Assessment Report of the Intergovernmental Panel on Climate
Change. (eds Houghton JT, Ding Y, Griggs DJ, Noguer M, Linden PJVD, Dai X,
Maskell K, Johnson CA) pp Page, Cambridge, United Kingdom and New York,
NY, USA.
Jarvis A, Reuter HI, Nelson A, Guevara E (2006) Hole-filled SRTM for the Globe
Version 3. available from the CGIAR-CSI SRTM 90m Database:
http://srtm.csi.cgiar.org.
Kucharik CJ, Barford CC, Maayar ME, Wofsy SC, Monson RK, Baldocchi DD (2006) A
multiyear evaluation of a Dynamic Global Vegetation Model at three AmeriFlux
forest sites: Vegetation structure, phenology, soil temperature, and CO2 and H2O
vapor exchange. Ecological Modelling, 196, 1-31.
Kucharik CJ, Foley JA, Delire C et al. (2000) Testing the performance of a Dynamic
Global Ecosystem Model: Water balance, carbon balance, and vegetation
structure. Global Biogeochemical Cycles, 14, 795-825.
Shi XZ, Yu DS, Warner ED, Pan XZ, Petersen GW, Gong ZG, Weindorf DC (2004) Soil
Database of 1:1,000,000 Digital Soil Survey and Reference System of the Chinese
Genetic Soil Classification System. Soil Survey Horizons, 45, 129-136.
Thompson SL, Pollard D (1995a) A Global Climate Model (GENESIS) with a LandSurface Transfer Scheme (LSX).1.Present climate simulation. Journal of Climate,
8, 732-761.
Thompson SL, Pollard D (1995b) A Global Climate Model (GENESIS) with a LandSurface Transfer Scheme (LSX).2.CO2 sensitivity. Journal of Climate, 8, 11041121.
Zhao M, Running SW (2010) Drought-Induced Reduction in Global Terrestrial Net
Primary Production from 2000 Through 2009. Science, 329, 940-943.
Zhao MS, Heinsch FA, Nemani RR, Running SW (2005) Improvements of the MODIS
terrestrial gross and net primary production global data set. Remote Sensing of
Environment, 95, 164-176.
Zhu QA, Jiang H, Liu J, Fang X, Yu S (2010a) Simulation and Trend Analysis of Soil
Temperature in China from 1955 to 2006 using IBIS Model. Scientia
Geographica Sinica (in Chinese , with English abstract), 30, 354-362.
Zhu QA, Jiang H, Liu J et al. (2011a) Forecasting carbon budget under climate change
and CO2 fertilization in Zhejiang Province of China using IBIS model. Polish
Journal of Ecology, 59, 3-23.
Zhu QA, Jiang H, Liu J et al. (2010b) Evaluating the spatiotemporal variations of water
budget across China over 1951-2006 using IBIS model. Hydrological Processes,
24, 429-445.
Zhu QA, Jiang H, Liu JX (2009) Effects of climate change on soil moisture over China
from 1960 to 2006. 2009 International Conference on Environmental Science and
Information Application Technology,Vol I, Proceedings, 140-143.
Zhu QA, Jiang H, Peng C et al. (2012) Effects of future climate change, CO2 enrichment,
and vegetation structure variation on hydrological processes in China. Global and
Planetary Change, 80-81, 123-135.
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139
140
141
Zhu QA, Jiang H, Peng CH et al. (2011b) Evaluating the effects of future climate change
and elevated CO2 on the water use efficiency in terrestrial ecosystems of China.
Ecological Modelling, 222, 2414-2429.
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