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Using bioclimatic envelope modelling to incorporate spatial and temporal dynamics of climate change into conservation planning By Nancy-Anne Rose NRES MSc Candidate December 14, 2010
Introduction - Climate change impacts on biodiversity ,[object Object],[object Object],[object Object]
The problem for biodiversity conservation planning: ,[object Object],[object Object]
B.C. parks and protected areas network ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Nature Conservancy of Canada - Ecoregional Assessment of the Central Interior Ecoregion http://science.natureconservancy.ca/centralinterior/central.php
Research Objectives ,[object Object],[object Object]
Bioclimatic envelope modelling ,[object Object],[object Object],[object Object],[object Object],[object Object],Botrychium crenulatum Crenulate Moonwort
Developmental Tools ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Methods -  Development of bioclimatic envelopes ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Methods – Identify locations of a target’s  suitable climate space SUITABLE CLIMATE SPACE
Overlay-Intersection  ï‚ź  Suitable Climate Space  ï‚ź  Persistent Climate Corridors   Nephroma occultum  (Cryptic Paw)
Bioclimatic Envelope ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Suitable Climate Space (SCS) ,[object Object]
Persistent climate corridors (PCC) ,[object Object],[object Object],[object Object],Engelmann Spruce-Sub-alpine Fir  Wet Very Cold (ESSFwv)
Conservation target summary ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
B.C. Biogeoclimatic Variants:  Interior Cedar Hemlock Hazelton Moist Cold Current distribution: 5,343 km 2 SCS: 3,677 km 2   PCC: 203 km 2   Representation: 3.8%
Terrestrial Ecological Unit:  North Pacific Interior Lodgepole Pine-Douglas Fir Woodland and Forest ,[object Object]
Listed Plant Species ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Areas of overlapping PCCs have a higher conservation value NB: TEU is terrestrial ecological unit
Application to conservation planning ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Marxan Comparison – Suitability Index ,[object Object],[object Object],[object Object],[object Object],[object Object]
Conclusions ,[object Object],[object Object],[object Object],[object Object]
Thanks! ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Questions ??
Ecoregional assessment process ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Uncertainty ,[object Object],[object Object],[object Object],[object Object],[object Object]
Limiting Climate Variables
Species response according to habitat type
ClimateBC/PP Variables ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]

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Masters Thesis Defense Presentation

Editor's Notes

  1. I’d like to thank everybody for coming today to listen to my presentation today. Your support and encouragement is greatly appreciated. The title of my presentation is 

  2. As we are all aware climate change is impacting our environment in a variety of complicated and interacting processes. For my research, I focused on its impacts on biodiversity and the ability of resource managers to conserve and maintain native ecological communities in the face of climate change. More specifically, I focused on the impact of climate change on the distribution of listed plant species and ecological communities. In short, plants are expected to either
  3. These changes have serious implications for biodiversity conservation. As our climate changes species are likely to migrate outside static park boundaries. Standard practice is to place static boundaries
  4. This map illustrates the flaw in applying static boundaries to a dynamic system. The polygons outlined in dark blue represent B.C.’s protected areas and the coloured polygons represent the PCCs of the biogeoclimatic zones of B.C. Admittedly in is unrealistic to expect a complete restructuring of our current reserve networks but the purpose of this research is to a) demonstrate the need to improve how we manage our resources and b) provide a potential starting point towards the development of a new decision making tool.
  5. To address this issue, I used NCC’s Central Interior ERA has a case study to introduce the concept of persistent climate corridors and their applicability to conservation planning. The study area shown here is 246 000 km squared and represents approximately 26% of the province.
  6. The utility of this concept is demonstrated by identifying potential persistent climate corridors for each target which I will argue represent candidate areas for conservation.
  7. Modelling strategy used to predict future species distribution. The figure illustrated on your right describes the bioclimatic envelope of Botrychiuum crenulatum defined by mean annual temperature, mean annual precipitation and the number of frost free days. In this example, the maximum and minimum values represent the limitations of B. crenulatum’s envelope. The envelopes I developed for my research are based on the 5 th and 95 th percentiles.
  8. Other important tools I used were
  9. In order to develop bioclimatic envelopes
  10. The first step towards identifying a target’s suitable climate space is to determine the location of its bioclimatic envelope throughout the study for each of the four timeslices. To do this I used a 1km grid of the study area where each point represented a km in the study and was represented by a latitude and longitude coordinate and an elevation. This information was run through ClimateBC to generate climate data for ech timeslice. Using SAS, I wrote a program that would check the climate data of each point fell within the 5 th and 95 th percentile of each of the 4 climate variables. If these conditions were met, that point recweived a value of 1 indicated full agreement with the envelope’s conditions, otherwise that point received a zero. This procedure was performed for each timeslice as demonstrated here. Next, these 4 timeslices were intersected and overlaid using Arcmap GIS the locations which coincided were termed suitable climate space.
  11. The identification of a target’s suitable climate space and consequently its persistent climate corridor is illustrated in this figure using Neproma occultum as an example. The intersection of the locations of its bioclimatic envelope for the baseline, 2020s, 2050s and 2080s timeslices results in the identification of N. occultum’s SCS. The next step is to overlay a target’s current distribution with its SCS. The areas of coincidence between these two spatial coverages is defined as the target’s PCC and is arguably a candidate area for conservation.
  12. Before I present some results, in summary
  13. Current Distribution 5343 km2, SCS 36
  14. In general areas with the potential to conserve multiple targets have a higher conservation value. For this reason I create a layer of PCCs for each target group and overlaid them to identify areas with more than one PCC. The only target groups to overlap were the TEU and the BGC variants, none of the PCCs belonging to the species overlapped with other target groups.
  15. In summary, the ERA processes in a conservation planning exercise designed to identify priority areas for the protection of biological diversity. A system of ecoregional planning is used to create a conservation blueprint which attempts to incorporate natural processes and document a portflio of sites desired for protection. If conserved, a conservation portfolio should secure the long term survival of viable native species and community types. Conservation planners, terrestrial and aquatic ecologists, GIS analysts Government agencies, non-profit groups, industry, First Nations