Supervisor: Prof. Colin Prentice Cosupervisor: Dr César Terrer Dr Trevor Keenan Dr Oskar Franklin Huanyuan Zhang
2020 May EGU BG3.22
Huanyuan Zhang © . All rights reserved
Introduction
Based on Free Air Carbon Dioxide Enrichment (FACE) and other raised-CO
2experiments, new theory (Terrer et al. 2019) has been proposed to explain how the magnitude of the CO
2fertilization effect on biomass and biomass production depends on soil phosphorus (in ectomycorrhizal systems) and the soil carbon:nitrogen ratio (in arbuscular mycorrhizal systems). To test whether raised-CO
2experiments and Terrer et al.’s theory could explain the known characteristic of land carbon sink, in this study, we
converted biomass increase into land carbon sink.
Fig. 1: Soil C:N and soil P are key plant resources driving the CO
2fertilization effect on above-ground biomass. (Terrer et al. 2019)
Fig. 2: Potential above-ground biomass
enhancement in terrestrial ecosystems under
elevated CO2. (Terrer et al. 2019)
Method
So, for any grid of Fig.2 , we only know two points on the NPP enhancement vs CO
2plot (Fig.3). We used a saturation curve to fit them, and computed NPP since 1901 (Fig 4) for any grid.
At a given location:
Fig. 2: Potential above-ground biomass enhancement in terrestrial ecosystems under elevated CO2. (Terrer et al. 2019)
Fig. 3: Saturation curve: the relationship between CO
2and NPP enhancement (data shown are only for conceptual illustration).
Fig. 4: NPP calculated in this study, based on Terrer et al’s theory (about nutrient limitation) and experimental data from global eCO
2experiments
We constructed a simple first order kinetic model to convert NPP into land carbon sink
Method
Heterotrophic respiration
Land Carbon Sink (net ecosystem productivity) = NPP - Heterotrophic respiration
NPP calculated with consideration of nutrient limitation (eCO2_NPP in Fig 5) is way smaller than other independent estimates, so is the derived land carbon sink.
Result
Fig. 5: NPP calculated in this study, based on Terrer et al’s theory (about nutrient limitation) and experimental data from global eCO
2experiments, with comparison to Trendy (Sitch et al. 2008) and P_model (Stocker et al. 2019).
Fig. 6: Land carbon sink (NEP) calculated in this study and comparison with Trendy (Vege models) (Sitch et al.
2008) and the Global carbon project (residual land sink)
(Le Quéré et al. 2018).
Possible reason
A recent meta-analysis by showed that (Terrer et al. unpublished), at some elevated CO2 experiment sites, soil carbon pool is expanding while vegetation biomass remains unchanged. This was supported by several other studies (Bloom et al., 2010; Jiang et al., 2019; King et al., 2004).
These suggested that large amount of carbon might be exported to Csoil via Root exudates which were always neglected in field measurements.
Possible reason: The difference between
field measured “NPP” and actual NPP
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Photo Credits and Reference
Cover image: Aspen Face, provided by Photo: Rick Anderson/Skypixs Aerials, Lake Linden, Michigan, USA
https://news.wisc.edu/munching-bugs-thwart-eager-trees-reducing-the-carbon-sink/.
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Le Quéré, C., Andrew, R.M., Friedlingstein, P., Sitch, S., Hauck, J., Pongratz, J., et al. (2018). Global Carbon Budget 2018. Earth Syst. Sci. Data, 10, 2141–2194.
Stocker, B.D., Wang, H., Smith, N.G., Harrison, S.P., Keenan, T.F., Sandoval, D., et al. (2019). P-model v1.0: An optimality-based light use efficiency model for simulating ecosystem gross primary production. Geosci. Model Dev. Discuss., 2019, 1–59.
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https://www.researchgate.net/publication/335131249_Nitrogen_and_phosphorus_constrain_the_CO2_fertilization_of_globa l_plant_biomass