June Skeeter
UBC Geography Department
Presentation in defense of my PhD thesis
This work was conducted in Indigenous territories.
Chapter 1: Introduction
Chapter 2: Vegetation Influence and Environmental Controls on Greenhouse Gas Fluxes from a Drained Thermokarst Lake in the Western Canadian Arctic
Chapter 3: Controls on Carbon Dioxide and Methane Fluxes from a Low-Center Polygonal Peatland in the Mackenzie River Delta
Chapter 4: Modeling Interannual Variability of Carbon Fluxes at a Low-Center Polygon Ecosystem in the Mackenzie River Delta
Chapter 5: Conclusions
Arctic amplification is accelerating climate change in the northern high latitudes, leading to:
Eddy covariance (EC) is a method to measure carbon dioxide (CO2) and methane (CH4) fluxes.
Harsh conditions stunt vegetation.
Reindeer grazing at Illisarvik
Permafrost inhibits decomposition;
tundra soils are often C rich.
NEE of CO2 is the primary component of the C balance.
NME of CH4 is an important secondary component in tundra wetlands.
Algorithms that build predictive models from experience.
$f(X,w)= \sum_{h=1}^Hβ_hg(\sum_{m=0}^M\gamma_{hm}x_m)$
Two ecosystems in the Mackenzie Delta Region we studied.
Two ecosystems in the Mackenzie Delta Region we studied.
Advance our understanding of the growing season C exchange in the Mackenzie Delta Region.
EC system measured peak growing season CO2 and CH4 fluxes.
EC station at Illisarvik
Fish eye view of EC system
Kljun et al. (2015) flux footprints intersected with vegetation map.
Class | Dominant Species | Landscape Fraction | Median Fclim [min - max] |
---|---|---|---|
Shrub | Salix spp. & Alnus viridis | 48% | 36%[0–79] |
Sedge | Carex aquatilis & Arctophila fulva | 29% | 39%[1–78] |
Grass | Pocacea spp. & Eriophorum angustifolium | 12% | 11%[0–56] |
Sparse | Sparse veg. / bare ground | 8% | 2%[0–34] |
Water | Hippuris vulgaris | 3% | 0%[0–4] |
Upland | Salix spp. & Betula nana | 0% | 6%[0–15] |
Neural Network (NN) models were used to:
Conditions over the peak growing season in 2016.
NEE had four key drivers:
PPFD, VPD, VWC, and FShrub
NME had five key drivers:
FSedge, VWC, Ts, FShrub & U
Long-term observations are needed to better contextualize results.
Similar Setup as Illisarvik.
Kljun et al. (2015) flux footprints intersected with landscape classification.
Class | Dominant Species | Landscape Fraction | Median Fclim [min - max] |
---|---|---|---|
Polygon Centers | Sphagnum spp., Equisetum spp., & Carex spp. | 66% | 63% [33–78] |
Polygon Rims | Salix spp. | 29% | 22% [5–56] |
Polygon Troughs | Carex spp. & Eriophorum angustifolium | 5% | 3% [0–9] |
Similar approach to Chapter 2, but a more robust NN was used to identify flux drivers. Weights Method (Gevery et al. 2003):
Conditions over the 2017 growing season.
Net growing season C sink.
Net Ecosystem Exchange
Factor | RI | Sign | |
---|---|---|---|
1 | Photon Flux Density (PPFD) | 64% | - |
2 | Vapor Pressure Deficit (VPD) | 8% | - |
3 | Polygon Center Temp. 5cm (TCnt5) | 7% | + |
4 | Thaw Depth (TD) | 7% | - |
5 | Day/Night (Daytime) | 6% | - |
6 | Polygon Rim Temp. 5cm (TRim5) | 5% | - |
7 | Polygon Rim Temp. 15cm (TRim15) | 3% | + |
8 | Wind (U) | 1% | - |
Flux response functions
Net Methane Exchange
Factor | RI | Sign | |
---|---|---|---|
1 | Net Radiation (Rn) | 34% | + |
2 | Friction Velocity (u*) | 20% | + |
3 | Wind (U) | 17% | - |
4 | Thaw Depth (TD) | 12% | - |
5 | Polygon Center Temp. 15cm (TCnt15) | 6% | - |
6 | Water Table (WTD) | 5% | - |
7 | Rim Fraction (FRim) | 4% | + |
8 | Center Fraction (FCnt) | 2% | - |
Flux response functions
Long-term observations are needed.
Chapter 3 fills a knowledge gap, but more context is needed.
Fish Island Landscape Classification
Class | Coverage |
---|---|
Low Center Polygons | 53% |
Shrub Tundra | 42% |
Open Water | 5% |
A Flux Driver Time Series (FDTS) was created spanning 2009-2019 snow-free seasons.
Substantial inter-annual variability.
It is not clear whether Fish Island is a net carbon sink.
Spearman Correlation Analysis
Factor | NEE | NME | Net C |
---|---|---|---|
Snowmelt Date | -- | +0.65 | -- |
Flood Date | -- | +0.79 | -- |
Max NDVI | -0.71 | -- | -0.73 |
Snowfall | -0.57 | -- | -- |
Snow-free Season Length | +0.64 | -- | -- |
Mean July Ta | +0.68 | -- | +0.64 |
Temporal upscaling indicated significant interannual variability in growing season C exchange.
Illisarvik | Fish Island | |
---|---|---|
NEE | Greater uptake than DTLB studied elsewhere | Mixed finding |
NME | Lower emission than DTLB studied elsewhere | Higher emission than LCP ecosystems studied elsewhere |
Spatial Heterogeneity | Substantial variability, diverse vegetation communities | Small scale variability, repeating features ≈ heterogeneous at larger scale |
Long-term Outlook | Depends on trajectory (shrub/sedge) | Potentially reduced C uptake with climate warming |
Neural Networks are not "black-box" models when applied carefully.
If our priority is just extracting information, the research only serves to perpetuate colonialism (Liboiron 2021).
I would like to thank:
Extra content that could not be discussed in the time allotted.
Random Forests (RF):
Impact of sensor location bias at Fish Island.
Estimating ER by projecting to "nighttime" conditions:
NN | r2 = 0.58 | RMSE = 0.23 μmol m-2 s-1 |
Q10 | r2 = 0.32 | RMSE = 0.28 μmol m-2 s-1 |
Logistic | r2 = 0.45 | RMSE = 0.24 μmol m-2 s-1 |
Wide range of possible conditions.