Progress 05/01/18 to 04/30/19
Outputs Target Audience:Our objectives stem from needs jointly identified by a diverse target audience: university and agency researchers, public and private land managers and producers, and non-governmental organizations. We expect our work to develop strategic guidance for ranchers and land managers so that they can identify effective adaptation strategies to climate variability given their geographic, ecological, and social situation. Extension work in each of five rangeland regions in the Western US (California annual grasslands, cold deserts, northern mixed prairie, shortgrass steppe, and hot deserts) will allow for the development of targeted, local guidance tailored to specific climates, vegetation, and social needs for ranchers. For policy makers and nongovernmental organizations, we will produce a white paper on the integration of regional and local exposure to guide diverse adaptive strategies in the western US. For university and agency researchers, we will produce peer-reviewed publications describing the outcomes of each of our objectives as well as their integration. Changes/Problems:There are no major changes to report. What opportunities for training and professional development has the project provided?This project has trained three postdoctoral researchers. Robert Shriver(USGS) has been active in the EXPOSURE group objectives, actively participates our bi-weekly meetings and our group meeting November 2018. He is primarily mentored by John Bradford. Andrew Felton (Utah State) has been active in the SENSITIVITY group objectives, actively participates our bi-weekly meetings and our group meeting November 2018.He is primarily mentored by Peter Adler. Christine Greene (UnivArizona)has been active in the ADAPTIVE CAPCITY group objectives, actively participates our bi-weekly meetings and our group meeting November 2018. She is primarily mentored by Mitch McClaran and Dan Ferguson. How have the results been disseminated to communities of interest?We are just completing the first year of this project, and so results have not been disseminated to communities of interest. We are planning our initial stakeholder meetings to begin May 2019. What do you plan to do during the next reporting period to accomplish the goals?1. EXPOSURE We will incorporate climate exposure into the co-development process in two ways. For the first workshop with producers and managers, we will develop information about exposure in a focal area over the previous 20 years. These data will inform initial interactions with producers and managers to discover what the innovators and early adopters have already done. For the second workshop, we will develop information about future climate scenarios that describe a gradient in business-as-usual (no change), increased variability representative of the focal region in 20 years, increased variability in the region with greatest exposure, and an extreme end of the 21st C scenario. 2. SENSITIVTY We haveinitiated our collaboration with Dr. Jay Angerer (Texas A&M) to analyze the response of forage quality to climate variability. That is the first step in our analysis of the sensitivity of livestock production to climate variability, which is a major goal during the next reporting period. 3. ADAPTIVE CAPACITY We are in the process of planning the first workshop with producers and managers, we will develop information about exposure in a focal area over the previous 20 years. We will be travelling to each of the 8 focal areas for these meetings in the next few months.
Impacts What was accomplished under these goals?
1. EXPOSURE. We applied an ecosystem water balance model (SOILWAT2) to estimate detailed historical and expected future patterns of soil moisture and plant water availability. We simulated these conditions on a ~7km grid from for three time periods: 1915 to 2015 (using gridded datasets based on weather observations), 2020-2059, and 2060-2099 (based on downscaled climate projections from general circulation models.) SOILWAT2 is a daily time-step, multiple soil layer, mechanistic model of ecosystem water balance that accounts for plot-specific interactions between climate, soil conditions, and vegetation, to estimate water pools and fluxes. Soil texture data was gathered from ISRIC WISE 30 arc second database (Batjes 2016). Potential plant biomass at each plot was estimated using algorithms within SOILWAT2 that account for the relationships between long-term climate patterns and vegetation structure (Bradford et al. 2014). Historical daily temperature and precipitation data was derived from the Livneh gridded dataset across the western US (Livneh et al 2013). Multi-model ensembles of future conditions were developed using 2 representative concentration pathways (RCPs 4.5 and 8.5) to represent uncertainty in future CO2 emissions and 11 different GCMs that were strategically selected to both perform well for the western United States and represent variability in the entire suite of available GCMs. We analyzed these results to quantify the exposure of western U.S. rangelands to changes in climate (figure E1) and ecological drought (figure E2), including changes already observed and those expected in coming decades (figure E3). We are evaluating a broad array of potential drought metrics, including precipitation: total water year precipitation; soil water availability: average available water (i.e. above -3MPa) in each season; simultaneous hot and dry conditions: water-year cumulative degree when soil water potential is <-3mpa; and growing season timing: days on which 50% and 90% of water year transpiration is reached. These results will provide ecologically relevant metrics of drought for evaluating rangeland climate sensitivity, and will provide useful perspective for stakeholders in our outreach efforts. 2. SENSITIVTY The majority of progress to date has concerned processing the remotely sensed annual net primary productivity (rangeland plant growth) data in preparation for climate sensitivity analyses. We processed these data to assure our sensitivity analyses reflect responses of rangeland ecosystems, and not irrigated agricultural regions, based on satellite imagery. Processing occurred within Google Earth Engine and R software. We now have produced a 30-year (1986-2015) annual net primary productivity dataset of the western United States rangeland sector (at 7 km spatial scales). We have combined these data climate and soil moisture covariates produced by the Exposure group to produce a spatially referenced dataset ready for our analysis of forage production sensitivity. This dataset and the associated R computer code will be made publicly available to the research community. Currently, the data are stored on Google Drive and the computer code is stored on local hard drives and synced to Github, consistent with our data management plan. Our first analyses have focused on understanding how sensitivity of forage production to annual precipitation varies across distinct rangeland regions (i.e., vegetation types) of the western US. When we map the sensitivity of production to precipitation in individual locations (pixels), we see a general trend of decreasing sensitivity from east to west trend, with a notable exception in California annual grasslands. More generally, we are finding that locations that are more productive on average are less sensitive to interannual variation in precipitation, though the slope of this relationship varies markedly among vegetation types. Our next analyses will focus on how responses of production to our soil moisture covariates compare across vegetation types. This provide a more mechanistic understanding of how and why rangelands may differ in their sensitivity to future changes in the amount and timing of water availability expected under future climate changes. We have also worked with theoretical population models to test our intuition about how evolutionary strategies for coping with variability depend on both the magnitude and the predictability of environmental variation. The results mostly support the arguments we made in the proposal, with conservative bet-hedging strategies favored where variability is large in magnitude but unpredictable, and plasticity favored where cues provide some degree of predictability. However, we learned that these results depend on the form of density-dependence. We are now gathering empirical data sets to locate natural plant communities in this parameter space. 3. ADAPTIVE CAPACITY. The overarching goal for this objectiveis to inform the development of science that can increase rangeland adaptive capacity. To meet this goal, the HD team developed a strategy for engaging with ranchers, rangeland managers, cooperative extension agents and similar conveners to better understand how the social and biophysical systems on rangelands have been changing over the past 20 years as a benchmark for understanding recent adaptive capacity and how that may be manifest in the near future. During the reporting period, we conducted a literature review of the climate vulnerability of ranching across the Western United States as well as adaptive capacity, including both short-term and long-term drought adaptation strategies. We also worked with the research team to identify 8 focal landscapes for a comparative analysis of local knowledge and rangeland adaptive capacity. The identified focal landscapes include Central Arizona (Gila County), Southwest New Mexico (Luna, Sierra, Grant, and Hidalgo Counties), Northeast Colorado (Weld, Logan, and Morgan Counties), Central Nebraska (Cherry and Grant Counties), Southern Utah (Garfield and Kane Counties), Northwest Nevada (Humboldt County), and Northeast Utah (Rich County). These landscapes were selected as they represent a range of climates, forage ecology, and ranching on both public and private land. We developed the research protocols for the focus group discussions and surveys and applied for Institutional Review Board (IRB) approval of human subjects research. The protocol for the upcoming focus group discussions was developed to identify: 1. local knowledge of the rangeland context, 2. activity and decision calendars, including how climate variability changes activities and decisions in ranching and rangeland management, and 3. ranking of threats, both environmental and social, to ranching and rangeland management.
Publications
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