Tongue River 2100: Future Tongue River Streamflow Estimates to Enable Northern Cheyenne Data-Driven Water Management and Planningn presentation given during the 2023 outreach trips to the following: Wyoming State Engineer’s Office, Sheridan, WY Tongue River Water Users Association, Tongue River Dam, MT Northern Cheyenne Tribe Citizens, Birney, MT & Ashland, MT Northern Cheyenne Tribal Historical Preservation Office, Lame Deer, MT Chief Dull Knife College, Lame Deer, MT Northern Cheyenne Tribe, Lame Deer, MT

Mountain ecosystems are prioritized by the North Central CASC due to the provided water resources, recreation opportunities, and endemic biodiversity. Mountain ecosystems are vulnerable to climate change due to elevation-dependent warming, loss of snowpack, reduction in physical area at higher elevations, and general sensitivity of alpine species to climate. Current climate adaptation strategies for this ecosystem include preservation of potential species refugia, connection of migratory pathways between habitat, management of recreation impacts, and modification of snow inputs. Many of these landscapes also fall within wilderness designation, constraining the range of options available for climate adaptation strategies. Further, at fine spatial and temporal scales applicable to management the patterns of climate change, subsequent biological responses, and success of climate adaptation strategies will likely be difficult to generalize across sites due to the idiosyncrasies of local geography (e.g., topography, soils).  This project’s overall objective is to produce a robust initiative for climate adaptation research in mountain ecosystems for the North Central CASC. This synthesis work aims to increase knowledge production and co-production of climate adaptation strategies for mountain ecosystems with federal, tribal, and academic partners in the North Central region. The research team investigate what are our knowledge gaps of mountain ecosystem responses to climate change that limit our ability to perform successful climate adaptation by: 1. Synthesizing literature on climate and biological trends in mountains across the study region; 2. Synthesizing literature on societal interests (e.g., water resources) and management actions (e.g., preservation) for this ecosystem in the context of changing climate; 3. Summarizing a prospective regional research agenda for climate adaptation in the mountain ecosystem for presentation to stake- and rights-holders; 4. Analyzing of publicly available biological datasets in mountains for temporal trends, regional patterns; 5. Documenting of climate adaptation case studies to address regional mountain management priorities, challenges, and opportunities; and 6. Creating a research and management initiative for climate adaptation in mountain ecosystems in the North Central region.

In this work we find that the future of fire in the U.S. will likely be characterized by more frequent and larger fires in most regions due to the changing climate and more people starting fires in new places. For the period 2020-2060, we project an average increase in the number of fires (+56%) and burned area (+59%) across the U.S. compared to the historical period (1984-2019). Our models indicate that there will be more fires in the Eastern U.S., which historically has had low fire activity, while the Western U.S. will see more fires that are larger than the largest fires on record. These changes have substantial implications for ecosystem and fire management, disaster response and mitigation, and wildland fire public policy. The work supported an early-career postdoc, provided mentoring and training opportunities, and helped to build a community of postdocs through the NCASC Climate Adaptation Postdoctoral (CAP) Fellows Program of Future of Fire.

Land surface phenology (LSP) products are currently of large uncertainties due to cloud contaminations and other impacts in temporal satellite observations and they have been poorly validated because of the lack of spatially comparable ground measurements. This study provided a reference dataset of gap-free time series and phenological dates by fusing the Harmonized Landsat 8 and Sentinel-2 (HLS) observations with near-surface PhenoCam time series for 78 regions of 10 × 10 km2 across ecosystems in North America during 2019 and 2020. The HLS-PhenoCam LSP (HP-LSP) reference dataset at 30 m pixels is composed of: (1) 3-day synthetic gap-free EVI2 (two-band Enhanced Vegetation Index) time series that are physically meaningful to monitor the vegetation development across heterogeneous levels, train models (e.g., machine learning) for land surface mapping, and extract phenometrics from various methods; and (2) four key phenological dates (accuracy ≤5 days) that are spatially continuous and scalable, which are applicable to validate various satellite-based phenology products (e.g., global MODIS/VIIRS LSP), develop phenological models, and analyze climate impacts on terrestrial ecosystems.

Over the last twenty years, phenology—the study of seasonal life cycle events—has emerged as a key subfield of global change biology. Phenology provides an integrated measure of the organismal response to climate change and is a key driver of the functional responses of ecosystems to climate change. Since I established the PhenoCam Network in 2008, over 200 papers have been published using Phenocam technology, and these papers have added to our understanding of phenology as both an indicator of climate variability and change and a key aspect of ecosystem function. This review examines: (1) the changing phenological research landscape, as represented by phenology-themed papers in Agricultural and Forest Meteorology (AFM), over the last 60 y; (2) the contributions of phenocams and the PhenoCam Network, as reported in the pages of AFM, to the study of phenology; and (3) the lessons I have learned from developing this grassroots effort, and how other researchers might benefit from the PhenoCam Network's successes and failures. Key conclusions to emerge from this review include: (1) the enormous, value-added power of research networks; (2) the importance of both interpersonal relationships and serendipity, in the metamorphosis of ideas into results; and (3) the potential for open, freely-available data to be transformative, in ways that cut across disciplinary, socioeconomic, and demographic barriers. Finally, the development of the PhenoCam Network has been a collaborative, multidisciplinary experiment in team science, and the commitment of my team members and the enthusiasm of my collaborators have been critical to the success of these efforts.

Managing resources under climate change is a high-stakes and daunting task, especially because climate change and associated complex biophysical responses engender sustained directional changes as well as abrupt transformations. This environmental non-stationarity challenges assumptions and expectations among scientists, managers, rights holders, and stakeholders. These challenges are anything but straightforward – a high degree of uncertainty impedes our ability to predict the environmental trajectory with confidence, and affected resources often span multiple governance jurisdictions or are subject to competing management objectives. Fortunately, tools exist to help grapple with such challenges. Two commonly used tools are scenario planning (SP) and structured decision making (SDM). SP is a well-established approach for assessing system response and facilitating decision making under a wide range of conditions that are uncertain and uncontrollable, such as those associated with adapting to climate change. However, SP lacks a defined structure for establishing objectives, quantifying tradeoffs, and evaluating the performance of candidate decisions to meet those objectives. SDM, on the other hand, is rooted in decision theory and focuses on explicit (often quantitative) assessment of the expected outcomes of choosing among a set of decision alternatives. SDM has been criticized for an inability to account for surprises and for imposing an overly narrow framing of problems to increase tractability. We discuss the strengths and limitations of SDM and SP as experienced through their application in various resource-management contexts, and then propose a new generalized framework – Scenario-Based Decision Analysis (SBDA) – that integrates these complementary approaches. SBDA structures resource management problems and solutions while considering uncertainties and surprises to inform resource management decision making.

The escalating climate and wildfire crises have generated worldwide interest in using proactive forest management (e.g. forest thinning, prescribed fire, cultural burning) to mitigate the risk of wildfire-caused carbon loss in forests. To estimate the risk of wildfire-caused carbon loss in western United States (US) conifer forests, we used a generalizable framework to evaluate interactions among wildfire hazard and carbon exposure and vulnerability. By evaluating where high social adaptive capacity for proactive forest management overlaps with carbon most vulnerable to wildfire-caused carbon loss, we identified opportunity hot spots for reducing the risk of wildfire-caused carbon loss. We found that relative to their total forest area, California, New Mexico, and Arizona contained the greatest proportion of carbon highly vulnerable to wildfire-caused loss. We also observed widespread opportunities in the western US for using proactive forest management to reduce the risk of wildfire-caused carbon loss, with many areas containing opportunities for simultaneously mitigating the greatest risk from wildfire to carbon and human communities. Finally, we highlighted collaborative and equitable processes that provide pathways to achieving timely climate- and wildfire-mitigation goals at opportunity hot spots.

As climate change facilitates significant and persistent ecological transformations, managing ecosystems according to historical baseline conditions may no longer be feasible. The Resist-Accept-Direct (RAD) framework can guide climate-informed management interventions, but in its current implementations RAD has not yet fully accounted for potential tradeoffs between multiple – sometimes incompatible – ecological and societal goals. Key scientific challenges for informing climate-adapted ecosystem management include (i) advancing our predictive understanding of transformations and their socioecological impacts under novel climate conditions, and (ii) incorporating uncertainty around trajectories of ecological change and the potential success of RAD interventions into management decisions. To promote the implementation of RAD, practitioners can account for diverse objectives within just and equitable participatory decision-making processes.