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Climate Change and Biome Shifts in Alaska and Western Canada Current Results and Modeling Options December 2010.

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Presentation on theme: "Climate Change and Biome Shifts in Alaska and Western Canada Current Results and Modeling Options December 2010."— Presentation transcript:

1 Climate Change and Biome Shifts in Alaska and Western Canada Current Results and Modeling Options December 2010

2 Participants Scenarios Network for Alaska Planning (SNAP), University of Alaska Fairbanks EWHALE lab, Institute of Arctic Biology, University of Alaska Fairbanks US Fish and Wildlife Service The Nature Conservancy Ducks Unlimited Canada Government of the Northwest Territories Government of Canada Other invited experts

3 Goals of this meeting Summary of project background Explanation of modeling methods Update on progress thus far Discussion and decisions from group: ◦ Confirm clustering inputs (24 data points) ◦ Confirm resolution for clustering and re-projection (CRU vs PRISM) ◦ Select number of clusters (15-20) ◦ Select land cover comparisons and methods ◦ Choose future decades to model ◦ Confirm emissions scenarios (A1B, A2, B1) ◦ Other issues?

4 Overview This project is intended to: ◦ a) develop climate and vegetation based biomes for Alaska, the Yukon and the Northwest Territories, and ◦ b) based on climate data, identify areas that are least likely to change and those that are most likely to change over the next 100 years. This project builds on and makes use of work previously conducted by SNAP, EWHALE, USFWS, TNC, and other partners. The completed analysis will be used by partners involved in protected areas, land use, and sustainable land use planning.

5 Overall objectives Develop climate and vegetation based biomes (based on cluster analysis) for AK, Yukon, NWT, and areas to the south that may represent future climatic conditions for AK,Yukon or NWT. Model potential climate-induced biome shift. Based on model results, identify areas that are least or most likely to change over the next 90 years. Provide maps, data, and a written report summarizing, supporting, and displaying these findings.

6 The Scenarios Network for Alaska and Arctic Planning (SNAP) SNAP is a collaborative network of the University of Alaska, state, federal, and local agencies, NGOs, and industry partners. SNAP is a collaborative network of the University of Alaska, state, federal, and local agencies, NGOs, and industry partners. Its mission is to provide timely access to scenarios of future conditions in Alaska for more effective planning by decision-makers, communities, and industry. Its mission is to provide timely access to scenarios of future conditions in Alaska for more effective planning by decision-makers, communities, and industry.

7 SNAP uses data for 5 of 15 models that performed best for Alaska and northern latitudes PRISM downscaled to 2 km resolution OR CRU downscaled to 10 minutes (18.4 km) Monthly temp and precip from 1900 to 2100 (historical CRU + projected) 5 models x 3 emission scenarios Available as maps, graphs, charts, raw data On line, downloadable, in Google Earth, or in printable formats No data yet: ◦ Extreme events ◦ Snowpack ◦ Coastal/Oceans SNAP Projections: based on IPCC models

8 Phase I: Alaska model Mapped shifts in potential biomes based on current climate envelopes for six Alaskan biomes and six Canadian Ecozones http://geogratis.cgdi.gc.ca/geogratis/en/collection/detail.do?id=4361 8

9 Phase I Results:Potential Change: Current - 2100 (Noting that actual species shifts lag behind climate shifts)

10 Improvements over Phase I Extend scope to northwestern Canada Use all 12 months of data, not just 2 Eliminate pre-defined biome/ecozone categories in favor of model-defined groupings (clusters) ◦ Eliminates false line at US/Canada border ◦ Creates groups with greatest degree of intra- group and inter-group dissimilarity ◦ Gets around the problem of imperfect mapping of vegetation and ecosystem types ◦ Allows for comparison and/or validation against existing maps of vegetation and ecosystems

11 Sampling Extent

12 Cluster analysis Cluster analysis is the assignment of a set of observations into subsets so that observations in the same cluster are similar in some sense. Clustering is a method of “unsupervised learning” (the model teaches itself) Clustering is common for statistical data analysis used in many fields The choice of which clusters to merge or split is determined by a linkage criterion, which is a function of the pairwise distances between observations. Cutting the tree at a given height will give a clustering at a selected precision.

13 Step 1: Create a Dissimilarity Matrix Distance measure determines how the similarity of two elements is calculated. Some elements may be close to one another according to one distance and farther away according to another. In our modeling efforts, all 24 variables are given equal weight, and all distances are calculated in “24-dimensional space” using RandomForest (similarity matrix proximity matrix, distance matrix) Taxicab geometry versus Euclidean distance: The red, blue, and yellow lines have the same length in taxicab geometry for the same route. In Euclidean geometry, the green line has length 6×√2 ≈ 8.48, and is the unique shortest path.

14 Methods: Partitioning Around Medoids (PAM) The dissimilarity matrix describes pairwise distinction between objects. The algorithm PAM computes representative objects, called medoids whose average dissimilarity to all the objects in the cluster is minimal Each object of the data set is assigned to the nearest medoid. PAM is more robust than the well-known kmeans algorithm, because it minimizes a sum of dissimilarities instead of a sum of squared Euclidean distances, thereby reducing the influence of outliers.

15 Clustering limitations PAM must compare every data point to every other data point in order to create a dissimilarity matrix and create medoids Adding additional data points affects processing requirements exponentially Thus, in creating clusters, we were limited to approximately 20,000 data points Total area is approximately 19 million square kilometers This meant selecting one data point for every 20 km by 20 km

16 Resolution limitations Data are not available at the same resolution for the entire area ◦ for Alaska, Yukon, and BC, SNAP uses 1961-1990 climatologies from PRISM, at 2 km, ◦ for all other regions of Canada SNAP uses climatologies for the same time period from CRU, at 10 minutes lat/long (~18.4 km) ◦ In clustering these data, both the difference in scale and the difference in gridding algorithms led to artificial incongruities across boundaries. ◦ One solution to both resolution and clustering limitaitons is to cluster across the whole region using CRU data, which is available for the entire area.

17 PRISM data Unlike other statistical methods in use today, PRISM was written by a meteorologist specifically to address climate Moving-window regression of climate vs. elevation for each grid cell Uses nearby station observations Spatial climate knowledge base weights stations in the regression function by their physiographic similarity to the target grid cell PRISM is well-suited to mountainous regions, because the effects of terrain on climate play a central role in the model's conceptual framework The primary effect of orography on a given mountain slope is to cause precipitation to vary strongly with elevation. The topographic facet is an important climatic unit and elevation is a primary driver of climate patterns

18 CRU data The station climate statistics were interpolated using thin- plate smoothing splines (ANUSPLIN) Trivariate thin-plate spline surfaces were fitted as functions of latitude, longitude and elevation to the station data The inclusion of elevation as a co-predictor adds considerable skill to the interpolation, enabling topographic controls on climate Local topographic effects such as rain shadows cannot be resolved unless: (1) a predictor that is a proxy for this influence is incorporated in the interpolation, and/or (2) there are sufficient stations to capture this local dependency as a function of latitude, longitude and elevation. In regions with sparse data, the station networks used to create these data sets are clearly unable to capture this sort of detail

19 Re-projecting CRU clusters to PRISM CRU is available for entire study area, and offers a good fit at a broader scale PRISM offers a better fit at fine scales, with better accuracy re altitude Best of both: ◦ Cluster results from CRU data were used to train an RF classification model. ◦ RF then classified the full PRISM datasets (where available)according to these clusters

20 Comparison of results using various methods Results were derived from the following train/down-model groups: ◦ Trained to 15km sample of 2km data and down-modeled to the 2km resolution over AK, YT, BC. ◦ Trained to 20km sample of 10min data down- modeled to the 2km resolution over AK, YT, BC. ◦ Trained to 15km sample of 2km data and down-modeled to the 10min resolution over full study region.

21 Comparison of results: 5 clusters Trained to PRISM data Trained to CRU, re- projected to PRISM data

22 Comparison of results: 10 clusters Trained to PRISM data Trained to CRU, re- projected to PRISM data

23 Comparison of results: 15 clusters Trained to PRISM data Trained to CRU, re- projected to PRISM data

24 Comparison of results: 20 clusters Trained to PRISM data Trained to CRU, re- projected to PRISM data

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