2. Select a feature or set of features in the map .
3. Explore results generated for the selected area.
(Results will appear here)
Projected Change (Model Averages, Annual) | |
---|---|
|
The average max temperature in the selected area is projected to exceed the historical average by
1.8 °C over the next 30 years2.9°C over the 30 years after that |
|
The average min temperature in the selected area is projected to exceed the historical average by
1.8 °C over the next 30 years2.9°C over the 30 years after that |
|
The average precipitation in the selected area is projected to the historical average by
1.8 mm over the next 30 years2.9mm over the 30 years after that (Note that precipitation projections vary widely among models) |
|
The average aridity in the selected area is projected to the historical average by
% over the next 30 years % over the 30 years after that
|
|
The average potential evapotranspiration in the selected area is projected to the historical average by
% over the next 30 years % over the 30 years after that
|
The zonal mean for several climate projection datasets is calculated for each of the reporting units and stored in a spatial database which can then be queried against using the tools provided on the left hand side of the map or by simply clicking on a feature of interest. This allows the user to examine the future climate projections and potential for climate change impact within one or more administrative units or ecological boundaries of interest.
Climate is different from weather. A weather forecast refers to a prediction about the specific atmospheric conditions expected for a location in the short-term future (hours to days).2
A climate trend is a progressive change in the state of the climate based on weather statistics evaluated over long periods, typically of at least 30 years.1
For information on climate models click the following link to view a presentation created by the Pacific Institute for Climate Solutions: http://pics.uvic.ca/insights/module1_lesson4/player.html
The time series climate data used to represent the historical period (1971-2000) were obtained from the LT71m PRISM 30 arc-second spatial climate dataset for the Conterminous United States (Daly et al., 2008). We selected a subset of the 34 CMIP5 General Circulation Models (GCMs) that have been shown to reproduce several observed climate metrics and that captured the full range of projected change for both annual average temperature and annual precipitation under the representative concentration pathway 8.5 (RCP8.5; Meinshausen et al., 2011; van Vuuren et al., 2011). We then obtained downscaled time series climate projections for the selected GCMs from the NASA Earth Exchange (NEX) U.S. Downscaled Climate Projections (NEX US-DCP30) dataset (Thrasher et al., 2013) for the entire spatial extent of the study area and for the period 2016-2075 time. The multi-model ensemble mean of the four downscaled climate models was calculated for each of the climate variables.
The data in these files represent probability of exceedance values. The field headers (98, 95, 90 ,80, 70, 60, 50, 40, 30, 20, 10, 5, 2) indicate the probability that the actual temperature or precipitation level during the three month period expressed by the LEAD time will be greater than the stated value within the specified climate division (CD). Click here for complete field descriptions and additional information on the forecast distribution files above.
The historical means and forecast means displayed in the climate console come directly from the values in the climatological mean field (C MEAN) and the forecast mean field (F MEAN), respectively. The forecast mean corresponds to the 50% probability of exceedance value. These data are automatically updated on the third Thursday of each month.
We used the Environmental Evaluation Modeling System (EEMS), a spatially explicit fuzzy logic modeling framework developed by Conservation Biology Institute (CBI), to evaluate the potential impact of climate change throughout the study area. We defined potential impact as a function of “site sensitivity” and the nature and degree to which a site may experience changes in climate, which we refer to as “climate exposure”. The EEMS logic model for each of the evaluated metrics, site sensitivity, climate exposure, and potential climate impacts are described in the sections below.
Overview of the EEMS Modeling Process
EEMS is based on the Ecosystem Management Decision Support System (EMDS; Reynolds, 2006). With fuzzy logic modeling (a quick introduction to fuzzy logic modeling can be found at: http://tinyurl.com/ox76lhb), input variables are first converted into a common numeric domain or range (also referred to as fuzzy space). Fuzzy values are assigned to the input variables based on the relationship to a true/false proposition. Values range between -1.0 (representing a fully false result) and +1.0 (representing a fully true result). For instance, input values of projected change in average minimum temperature can be tested against the proposition, “has high change from historical temperature” via a mathematical function with fuzzy values between +1.0 (the most true result) and -1.0 (the most false result), inclusive.
Fuzzy values are combined using logic operators in a hierarchical, tree-based logic structure to produce a result based on a single evaluation proposition (for instance “has a high degree of climate change”). Each cell in the study area is evaluated independently, and a map reflecting the value of each proposition across the landscape is produced.
This dataset provides an estimate of current terrestrial intactness, based on an EEMS fuzzy logic model that integrates multiple measures of landscape development and vegetation intactness.
This model integrates agriculture development (from LANDFIRE EVT v1.1), urban development (from LANDFIRE EVT v1.1 and NLCD Impervious Surfaces), linear development (from Tiger 2012 Roads, utility lines, and pipelines), OHV recreation areas, energy and mining development (from state mine and USGS national mines datasets as well as geothermal wells, oil/gas wells, wind turbines, and power plant footprints), vegetation departure (from LANDFIRE VDEP), invasive vegetation (multiple sources combined for invasives analyses), and measures of natural vegetation fragmentation calculated using FRAGSTATS. In this version, Maxent modeled Sahara Mustard was included in the Invasive's branch as well as in the Fragstats model run.
Caution is warranted in interpreting this dataset because it provides a single estimate of terrestrial intactness based on available data. The degree of terrestrial intactness likely varies for a particular species or conservation element, and may depend on additional factors or thresholds not included in this model. Instead, this model should be taken as a general measure of intactness that can serve as a template for evaluating across many species at the ecoregion scale, and provides a framework within which species-specific parameters can be incorporated for more detailed analyses.
View or Download this dataset on Data Basin
View or Download this dataset on Data Basin
View or Download this dataset on Data Basin (2016-2045)
View or Download this dataset on Data Basin (2046-2075)
View or Download this dataset on Data Basin (2016-2045)
View or Download this dataset on Data Basin (2046-2075)
2 National Oceanic and Atmospheric Administration (NOAA), Climate Program Office, Climate Literacy