Periodic Reporting for period 4 - TUVOLU (Tundra biogenic volatile emissions in the 21st century)
Periodo di rendicontazione: 2022-10-01 al 2024-03-31
In WP2, focused on insect herbivory, field work was conducted in Abisko, Tromsø, and Narsarsuaq. An experiment using methyl jasmonate (MeJA) to mimic insect herbivory on dwarf birch showed increased BVOC emissions and altered compound profiles, with climate warming amplifying this response (Li et al. 2019, Nat. Plants). The effects of herbivory on dwarf birch BVOC emissions varied under different environments (Rieksta et al. 2021, Glob. Change Biol.; Rieksta et al. 2023, Plant Environ. Interact.). Experiments indicated a positive relationship between the number of feeding larvae and BVOC emissions from mountain birch (Rieksta et al. 2020, Front. Plant Sci.). Gall-infestation caused less changes in BVOC emissions from Arctic willows (Swanson et al. 2021, Sci. Total Environ.).
In WP3, focused on permafrost thaw emissions, we showed that thawing permafrost releases BVOCs, especially ethanol and methanol, with lower atmospheric emissions due to microbial uptake during passage through the active layer (Kramshøj et al. 2018, Nat. Commun.). Microbial uptake is efficient for all BVOCs in all soils (Albers et al. 2018, Biogeosciences; Rinnan & Albers 2020, JGR Biogeosci.). The uptake rate increases with higher BVOC availability (Jiao et al. 2023, Soil Biol. Biochem.). Soil water content, affecting oxygen levels, also influences BVOC emissions (Kramshøj et al. 2019, Glob. Change Biol.). Emissions vary over the growing season and between landscape types (Jiao et al. 2023, Geoderma).
WP4 assessed temperature sensitivity of BVOC emissions in Alpine ecosystems beyond the Arctic, with field measurements in Ecuador, Bolivia, and Costa Rica. Comparisons of BVOC emissions in control and warming treatments in local Alpine vegetation are under analysis (Chan et al., in preparation; Smart et al., in preparation).
WP5’s modelling work analyzed Pan-Arctic tundra BVOC emissions under different climate scenarios and their impacts on atmospheric chemistry (Tang et al. 2023, npj Clim. Atmos. Sci.). A review article summarized current knowledge and identified gaps in modelling soil BVOC processes (Tang et al. 2019, Rev. Geophys.). New leaf temperature algorithms were developed using data from WP1 (Simin et al. 2021, Environ. Exp. Bot.) and ecosystem data were used for model validation (Seco et al. 2020, Atmos. Chem. Phys.). Herbivory-BVOC emission relationships were assessed to develop algorithms for model improvement (Tang et al., in preparation).
Our pioneering work on BVOC emissions from permafrost thaw has led several process studies revealing that actual emissions depend on the balance between release and microbial uptake, influenced by environmental conditions (Kramshøj et al. 2018, Nat. Commun.; Rinnan & Albers 2020, JGR Biogeosci.; Kramshøj et al. 2019, Glob. Change Biol.). The work related to soil processes in ecosystem BVOC exchange is still at its infancy and will likely lead to important new understanding in the future.
We also highlighted insect herbivory's importance in affecting Arctic BVOC emissions. While rising temperatures strongly influence emissions, herbivory has even more drastic effects during active feeding periods, amplified by temperature (Li et al. 2019, Nat. Plants).
Overall, we improved BVOC emission models, enhancing estimates of their magnitudes and compositions under different climate scenarios and their impact on atmospheric composition and climate (Tang et al. 2023, npj Clim. Atmos. Sci.).