Ecosystems, Sustainability and Global Change Study Notes

  • Current Fluxes (2006-2015):
      - Fossil fuels & industry: 34.1extGtCO2/extyrext(Carbondioxideemittedfromburningfossilfuelsandrelatedindustrialprocesses)34.1 ext{ Gt CO}_2/ ext{yr} ext{ (Carbon dioxide emitted from burning fossil fuels and related industrial processes)}
      - Land-use change: 3.5extGtCO2/extyrext(Emissionsresultingfromdeforestation,theconversionofforeststoagriculture,andotherlandusechanges)3.5 ext{ Gt CO}_2/ ext{yr} ext{ (Emissions resulting from deforestation, the conversion of forests to agriculture, and other land-use changes)}
      - Atmospheric growth: 16.4extGtCO2/extyrext(NetincreaseofCO2extintheatmosphere)16.4 ext{ Gt CO}_2/ ext{yr} ext{ (Net increase of CO}_2 ext{ in the atmosphere)}
      - Land sink: 11.5extGtCO2/extyrext(Carbonabsorbedbyterrestrialecosystems,suchasforestsandsoils)11.5 ext{ Gt CO}_2/ ext{yr} ext{ (Carbon absorbed by terrestrial ecosystems, such as forests and soils)}
      - Ocean sink: 9.7extGtCO2/extyrext(Carbondioxideabsorbedbytheoceans)9.7 ext{ Gt CO}_2/ ext{yr} ext{ (Carbon dioxide absorbed by the oceans)}

  • Anthropogenic Trends (2020 projection):
      - Fossil fuel combustion source: 9.6imes1015extgCyr1ext(Carbonemissionsfromfossilfueluse)9.6 imes 10^{15} ext{ gCyr}^{-1} ext{ (Carbon emissions from fossil fuel use)}
      - Deforestation/land use source: 1.3imes1015extgCyr1ext(Carbonemissionsduetodeforestation)1.3 imes 10^{15} ext{ gCyr}^{-1} ext{ (Carbon emissions due to deforestation)}
      - Net balance (sources-uptake): 3.1imes1015extgCyr1ext(Netcarbonuptakebyecosystems,indicatingasinkdespitesignificantemissions)-3.1 imes 10^{15} ext{ gCyr}^{-1} ext{ (Net carbon uptake by ecosystems, indicating a sink despite significant emissions)}

  • Photosynthetic Pathways and Adaptive Values:
      - C3 Photosynthesis:
        - Incorporates CO2CO_2 into a 3-carbon compound, primarily using the enzyme RUBISCO (ribulose biphosphate carboxylase/oxygenase).
        - Most efficient under cool, moist conditions ( < 30^ ext{C}), as high temperatures can promote photorespiration, reducing efficiency.   - C4 Photosynthesis:     - Incorporates CO2CO_2 into a 4-carbon compound via the enzyme PEP Carboxylase (phosphoenol pyruvate), allowing plants to thrive in high-temperature environments.     - Kranz Anatomy: Features specialized bundle sheath cells where Calvin cycle takes place, enhancing efficiency.     - Adaptive Value: Higher water-use efficiency and faster rates under high light/temperature ( > 30^ ext{C}) by minimizing photorespiration.
        - Disadvantage: More energetically costly due to additional ATP required to regenerate PEP.
      - CAM (Crassulacean Acid Metabolism):
        - Stomata open at night to store CO2CO_2 as an acid, conserving water by closing during the day.
        - CAM-idling: In extreme aridity, plants may close stomata all day and night, relying on internal stores of oxygen from photosynthesis for respiration and vice versa.

  • Stomatal Density and Transpiration:
      - Stomatal Function: Essential for balancing CO2CO_2 assimilation with water loss via evapotranspiration. Notably, 99 ext{%} of absorbed water is lost through transpiration.
      - Woodward (1987): Significant research indicating an inverse correlation between atmospheric CO2CO_2 concentration and stomatal frequency, suggesting plants adjust stomatal opening to varying environmental CO_2 levels.
      - Historical Evidence: Comparisons of modern and fossil Ginkgo biloba demonstrate significant stomatal shifts corresponding to CO2CO_2 levels from the Upper Triassic to the present. Changes in stomatal density provide insights into past climate conditions and plant responses to atmospheric changes.

  • Climate Change Impacts on Distributions and Biomes:
      - Biome Shifts: Changes in mean annual temperature and precipitation patterns driven by climate change can significantly alter biomes. Doubling atmospheric CO2CO_2 levels are expected to shift Canadian ecozones (e.g., Tundra transforming into Boreal forest areas).
      - Cyclamen Case Study: Projections for 2050 suggest a total habitat loss of 53 ext{%} for various Cyclamen species (e.g., C. colchicum, C. creticum, C. cyprium), which may face 100 ext{%} range loss due to habitat incompatibility with shifting climates.
      - Direct Impacts: Changes in distributions, typically moving toward higher latitudes or altitudes, alongside phenological shifts such as earlier flowering, resulting from warming temperatures.
      - Indirect Impacts: Altered ecological interactions, including invasive species spreading into new regions, changes in fire frequency and intensity, and modified interactions between herbivores and pathogens with their hosts due to altered environments.

  • Biological Responses and Species Interactions:
      - Phenology Mismatches:
        - Visser and Hollemann (2001): Documented timing differences between the winter moth (Operophtera brumata) hatching and the synchronization with host plant bud burst, impacting their survival and reproductive success.
        - Butterfly species (e.g., Euchloe tagis) could lose suitable habitat if their migration routes don't coincide with host plants in shifting climates, leading to population declines.
      - Range Shifts:
        - Parmesan et al. (1999): Approximately 63 ext{%} of 35 studied non-migratory European butterflies have exhibited northward shifts in range as they respond to changing temperatures.
        - Significant range expansion of Thaumetopoea pityocampa (Pine Processionary) correlates with increased mean night temperatures, affecting forest ecosystems where they thrive.
      - Atmospheric Interactions: Moderate levels of O3O_3 (Ozone) can counteract some of the elevated CO2CO_2 responses observed in various ecosystems, suggesting potential overestimations in carbon sequestration capabilities when only observing CO2CO_2 levels.
      - Insect Development: Temperature remains the primary abiotic factor influencing development rates in invertebrates. Higher temperatures typically accelerate development and survival; however, populations may decline if critical temperature thresholds are surpassed, as observed in species such as Arctia caja.