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Percent change in grassland soil carbon sequestration potential. These maps display the percent change in the potential for grassland soil carbon sequestration for each watershed under three IPCC-SRES scenarios – A1B, A2 and B1. Watershed boundaries are from the 8-digit Watershed Boundary Dataset (http://water.usgs.gov/GIS/huc.html). Here soil carbon represents soil organic carbon (up to 20 cm in depth). Future change in soil carbon was modeled by the U.S. Geological Survey’s General Ensemble Biogeochemical Modeling System (GEMS) (http://www.usgs.gov/climate_landuse/land_carbon/BGM.asp). Carbon model outputs were produced through the U.S. Geological Survey’s (USGS) national carbon sequestration assessment of ecosystem...
These interactive maps display results from a scenario analysis on the integrated effects of future land use and climate change on rangeland ecosystem services within the California Rangeland Conservation Coalition focus area (the California Central Valley and surrounding foothills). A three-map viewer allows users to view and compare results at the watershed scale across three scenarios simultaneously. Maps are available for the following metrics: 1) Change in the percentage of watershed area with critical habitat, 2) Percent change in grassland soil carbon sequestration potential, 3) Percent change in climatic water deficit relative to the 1981-2010 climate period, 4) Ratio of recharge to runoff for three 30-year...
These maps display the magnitude of projected future climate change in relation to the interannual variability in late 20th century CA climate. The maps show the standardized Euclidean distance between the late 20th century climate at each pixel and the future climate at each pixel. The standardization puts all of the climate variables included on the same scale and down weights changes in future climate which have had large year to year variation historically. Warmer colors indicate greater climate change and cooler colors indicate less extreme climate change.
Bird community turnover for current and future climate (GFDL) based on maxent models for 198 land bird species.
Understanding the environmental contributors to population structure is of paramount importance for conservation in urbanized environments. We used spatially explicit models to determine genetic population structure under current and future environmental conditions across a highly fragmented, human-dominated environment in Southern California to assess the effects of natural ecological variation and urbanization. We focused on 7 common species with diverse habitat requirements, home-range sizes, and dispersal abilities. We quantified the relative roles of potential barriers, including natural environmental characteristics and an anthropogenic barrier created by a major highway, in shaping genetic variation. The...
This dataset includes Climatic Water Deficit (CWD) change, average winter (Dec, Jan, Feb) and average spring (Mar, Apr, May) snowpack change, recharge change, and runoff change from Basin Characterization Model (BCM) output using the GFDL and PCM A2 Scenarios in Sierra Nevada California, for 2010-2039, 2040-2069 and 2070-2099. The data was processed using historic (1979-2000) and future (2010-2039; 2040-2069; 2070-2099) values to calculate change. CWD: The term climatic water deficit defined by Stephenson (1998) is quantified as the amount of water by which potential evapotranspiration (PET) exceeds actual evapotranspiration (AET). This term effectively integrates the combined effects of solar radiation, evapotranspiration,...
Average percent change in multiple ecosystem services from 2010 to 2040 These maps display the average percent change in three rangeland ecosystem services – total ecosystem carbon, critical habitat and water availability – from 2010 to 2040 for three IPCC-SRES scenarios (A1B, A2 and B1) and two climate projections (warm, wet future and hot, dry future). Total ecosystem carbon is total carbon stored in vegetation and soils (up to 20 cm in depth), and was estimated annually from 2006 to 2050 by the U.S. Geological Survey’s General Ensemble Biogeochemical Modeling System (GEMS) (http://www.usgs.gov/climate_landuse/land_carbon/BGM.asp). See Percent change in total ecosystem carbon dataset page for model details. Critical...
Significant efforts are underway to translate improved understanding of how climate change is altering ecosystems into practical actions for sustaining ecosystem functions and benefits. We explore this transition in California, where adaptation and mitigation are advancing relatively rapidly, through four case studies that span large spatial domains and encompass diverse ecological systems, institutions, ownerships, and policies. The case studies demonstrate the context specificity of societal efforts to adapt ecosystems to climate change and involve applications of diverse scientific tools (e.g., scenario analyses, downscaled climate projections, ecological and connectivity models) tailored to specific planning...
When: May 29, 2014 1:00 - 3:30 PMWhere: Department of Water Resources, Large Conference Room, 2nd Floor, Bonderson Building, 901 P Street, Sacramento, CA 95814The project evaluates the effects of different climate change and land use change scenarios on ecosystem services (water availability, wildlife habitat and carbon sequestration) provided by rangelands in California. The project is a partnership between the USGS and Defenders of Wildlife and it is funded by the California Landscape Conservation Cooperative.More information, an online tool and associated data are available at http://climate.calcommons.org/aux/rangeland/index.html.A fact sheet with information about the project can be found at http://pubs.usgs.gov/fs/2014/3019/.
The CA LCC-funded project “A Climate Change Adaptation Strategy for Sierra Nevada Birds “ applied the NatureServe Climate Change Vulnerability Index tool to assess vulnerability of 168 bird species that breed in the Sierra Nevada and developed a peer-reviewed Climate Change Adaptation Strategy for Sierra Nevada bird species that are most vulnerable to climate change. “Sierra Nevada Bird Vulnerability Assessment Matrix” provides the individual vulnerability factor scores upon which the vulnerability rankings are based.
Priority areas for conservation of tidal marsh birds given current and future environmental conditions. Maps were created using Zonation, a spatial conservation planning software tool that can take into account multiple species and scenarios to create a hierarchical prioritization of the landscape.The current (2010) and future (2030-2110) prioritization is based upon distribution and abundance models for five tidal marsh bird species which utilized avian observation data (2000 - 2009), a marsh accretion model, and physical variables (e.g. salinity, distance to nearest channel, slope, etc). Values represent the rank in which pixels were removed from the landscape using Zonation Conservation Planning software with...
Marsh accretion was modeled by ESA PWA using the Marsh-98 model, described here. The model assumes that rates of marsh plain elevation change depend on the availability of suspended sediment and organic material, water depth, and duration of inundation periods. If enough suspended sediment is available, then tidal marsh elevations can keep pace with increased inundation. Model outputs were linearly interpolated in 10-cm increments for starting elevations ranging from -3.7 to 1.7 m (relative to mean higher high water, or MHHW), and applied to a composite 5-m elevation grid (see below) for SF Bay. Results for each possible combination of projected sea level rise, sediment and organic material availability, and target...
In California, the near-shore area where the ocean meets the land is a highly productive yet sensitive region that supports a wealth of wildlife, including several native bird species. These saltmarshes, mudflats, and shallow bays are not only critical for wildlife, but they also provide economic and recreational benefits to local communities. Today, sea-level rise, more frequent and stronger storms, saltwater intrusion, and warming water temperatures are among the threats that are altering these important habitats.To support future planning and conservation of California’s near-shore habitats, researchers examined current weather patterns, elevations, tides, and sediments at these sites to see how they affect plants...
Salt marsh elevation and geomorphic stability depends on mineral sedimentation. Many Mediterranean-climate salt marshes along southern California, USA coast import sediment during El Niño storm events, but sediment fluxes and mechanisms during dry weather are potentially important for marsh stability. We calculated tidal creek sediment fluxes within a highly modified, sediment-starved, 1.5-km2 salt marsh (Seal Beach) and a less modified 1-km2 marsh (Mugu) with fluvial sediment supply. We measured salt marsh plain suspended sediment concentration and vertical accretion using single stage samplers and marker horizons. At Seal Beach, a 2014 storm yielded 39 and 28 g/s mean sediment fluxes and imported 12,000 and 8800...
This data collection is the product of the CA LCC-funded project “Climate Change/Land Use Change Scenarios for Habitat Threat Assessments on California Rangelands”.The project aids conservation of California rangelands by identifying future integrated threats of climate change and land use change, and quantifying two main co-benefits of rangeland conservation – water supply and carbon sequestration. Through a multi-stakeholder partnership, the project proponents developed integrated climate change/land use change scenarios for the Central Valley and Chaparral and Oak Woodland eco-regions, and disseminated information about future potential threats to high priority conservation areas within the California Rangeland...
Percent change in climatic water deficit relative to the 1981-2010 climate period These maps display the average percent change in climatic water deficit (CWD) from the 1981-2010 climate period to a future climate period for each watershed. Percent change in CWD is provided for two climate projections for each of the three IPCC-SRES scenarios – A1B, A2 and B1. Future time periods displayed include 2010-2039, 2040-2069 and 2070-2099. Watershed boundaries are from the 8-digit Watershed Boundary Dataset (http://water.usgs.gov/GIS/huc.html). CWD is defined as potential evapotranspiration minus actual evapotranspiration. This term effectively integrates the combined effects of solar radiation, evapotranspiration, and...
Full Title: Environmental Change Network: Current and Projected VegetationThe current vegetation layer is derived from the vegetation map developed as part of the California Gap Analysis project. The derivation takes the California Wildlife Habitat Relationships (CWHR) habitat classification provided in the California Gap Analysis layer, generalizes the classes to a set of broader habitat types, and rasterizes it at 800 meter resolution.The future vegetation layers for both the GFDL and CCSM GCM models are derived using a random forest model of the vegetation classification. The original CWHR classification has been generalized to 12 classes for ease in modeling. Inputs to the model include eight bioclimatic variables...
Water-Wildlife Hotspots: Areas where changes in water availability (recharge plus runoff) and loss of critical habitat coincide. These maps display percent change in water availability relative to the 1981-2010 climate period where 5% or more of watershed area has lost critical habitat. Water availability is defined as recharge plus runoff. Critical habitat is defined as critical priority conservation areas mapped in the California Rangeland Conservation Coalition’s focus area map (http://www.carangeland.org/focusarea.html) (TNC, 2007). Percent change in water availability is provided for two climate projections for each of the three IPCC-SRES scenarios – A1B, A2 and B1. Scenarios of critical habitat loss for years...
The goal of the North-central California Coast and Ocean Climate-Smart Adaptation Project is to collaboratively develop and implement adaptation actions in response to, and in preparation for, climate change impacts on habitats, species and ecosystem services (termed focal resources). Vulnerability to climate and non-climate stressors was assessed for select focal resources in the region during Phase 1 of the project through two decision-support workshops. Climate-smart adaptive management actions will be developed and prioritized by the Climate-Smart Adaptation Working Group in Phase 2 of the project.
A collection of spatial data resources assembled to support the CVLCP partnership efforts, including scenario planning, assessing vulnerabilities, and developing adaptation strategies.