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Sifting through selective science and misinformation for collaborative forest management

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Land manager and public land partner-focused panel webinar dedicated to examining selective science use, some of the impacts to land management, and methods for reducing misinformation in collaborative forest management. The panel provides short talks on their perspectives, and address questions and issues provided by attendees. Discussion and Q&A during this session will facilitate information exchange between all attendees.

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Plant community resistance to invasion by Bromus species: The roles of community attributes, Bromus interactions with plant communities, and Bromus traits – Chapter 10

View Chapter 10 of the book, Exotic brome-grasses in arid and semiarid ecosystems of the western US: Causes, consequences, and management implications.

The factors that determine plant community resistance to exotic annual Bromus species are diverse and context specific. They are influenced by the environmental characteristics and attributes of the community, the traits of Bromus species, and the direct and indirect interactions of Bromus with the plant community. Environmental factors, in particular ambient and soil temperatures, have significant effects on the ability of Bromus to establish and spread.

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2017 Fire season in OR and WA

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The 2017 Fire Narrative and Timeline tells the story of successes and challenges, and also addresses emerging technology and science, such as Quantitative Risk Assessment, Risk Management Assistance Teams, and using Unmanned Aircraft Systems (drones) for infrared and reconnaissance flights.

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Seed use in the field: Delivering seeds for restoration success

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Seed delivery to site is a critical step in seed‐based restoration programs. Months or years of seed collection, conditioning, storage, and cultivation can be wasted if seeding operations are not carefully planned, well executed, and draw upon best available knowledge and experience. Although diverse restoration scenarios present different challenges and require different approaches, there are common elements that apply to most ecosystems and regions. A seeding plan sets the timeline and details all operations from site treatments through seed delivery and subsequent monitoring. The plan draws on site evaluation data (e.g. topography, hydrology, climate, soil types, weed pressure, reference site characteristics), the ecology and biology of the seed mix components (e.g. germination requirements, seed morphology) and seed quality information (e.g. seed purity, viability, and dormancy). Plan elements include: (1) Site treatments and seedbed preparation to remove undesirable vegetation, including sources in the soil seed bank; change hydrology and soil properties (e.g. stability, water holding capacity, nutrient status); and create favorable conditions for seed germination and establishment. (2) Seeding requirements to prepare seeds for sowing and determine appropriate seeding dates and rates. (3) Seed delivery techniques and equipment for precision seed delivery, including placement of seeds in germination‐promotive microsites at the optimal season for germination and establishment. (4) A monitoring program and adaptive management to document initial emergence, seedling establishment, and plant community development and conduct additional sowing or adaptive management interventions, if warranted. (5) Communication of results to inform future seeding decisions and share knowledge for seed‐based ecological restoration.

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Prioritizing limited resources in landscape-scale management projects

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Collaborating at the planning stage of restoration projects can be slow. It takes time to build relationships, and meeting people “where they are at” is often the accomplishment. Success in collaboration comes from gathering the local knowledge to move forward with implementing projects. Long-standing collaborative groups often face challenges with keeping stakeholders and partners involved particularly when tracking past projects. Finding continued funding to maintain the projects implemented years earlier takes effort usually on behalf of the convening organization.

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2021 North American forest and conservation nursery technology webinar series

Webinar recordings.

Webinars will be Wednesdays, August 4 through September 8, 2021. Each webinar will last approximately one hour and include a Q&A session.

Planned webinar topics are:

Lessons learned in nursery operations during the pandemic
Water management and its effects on pests, pathogens, and plant growth
Hot planting and fall/summer planting: operational tips and tricks for success
Current programs and resources regarding genetics and assisted migration
Innovative nursery technologies from other industries
Current reforestation pipeline goals and legislation: expected impacts on growers and land managers

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Ranch economics of using targeted grazing to create wildfire fuel breaks on public land

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Targeted grazing in the Great Basin has been used to reduce cheatgrass fuel loads and enhance wildfire control. In this project, we evaluate the economic impact of targeted grazing on cow-calf ranches across southeast Oregon, northeast Nevada, and southwest Idaho when practices such as fencing, water hauling, and herding are necessary for producers to accomplish desired grazing outcomes. Large and small representative ranch models were developed for major land resource areas 23, 24, and 25 where applicable. Typical targeted grazing costs and practices were obtained from producer and agency focus groups in each state and introduced into ranch economic models. Targeted grazing periods begin 1 mo before typical Bureau of Land Management turnout in the spring and again in the fall after typical public land grazing ends. In each year, targeted grazing would occur when the previous growing season (September to March and April to August) had more than 25% of median precipitation based on PRISM historical data. Hence, targeted grazing could occur in the spring, fall, or both depending on precipitation. In both seasons, targeted grazing continues until the desired animal unit months of forage are removed. One hundred precipitation data sets were randomly generated using Excel to mimic the actual number of drought years in the spring and fall. The model is a 40-yr recursive linear programming model using 100 cattle price sets and the 100 precipitation sets. Results are averaged over 10 000 model runs and compared with scenarios with no targeted grazing and targeted grazing based on the actual precipitation data set. Results show changes in cattle herd size, hay sales, and the economic impacts to the public land ranch operation for two ranch sizes in each of the three major land resource areas by state.

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Lessons learned from Learn-n-Burn events

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“Learn and Burn” workshops are an excellent way for private landowners and others to gain hands-on burning experience and knowledge from expert mentors. This webinar will provide some lessons learned from coordinating these events, and tips to putting one on in the future. Participants will be provided with a template checklist, examples of past agendas, ideas for potential partners and funding opportunities, suggestions on how to measure program impact, and successes from past events. Are you thinking of planning one of these events?

How will future climate change impact prescribed fire across the contiguous United States?

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In this study, we combine climate projections with information on prescribed burning windows for ecoregions across the contiguous United States (CONUS) to compute the number of days when meteorological conditions allow for the safe and effective application of prescribed fire under present-day (2006–2015) and future climate (2051–2060) conditions. The resulting projections, which cover 57% of all vegetated area across the CONUS, indicate fewer days with conditions suitable for prescribed burning across ecoregions of the eastern United States due to rising maximum daily temperatures, but opportunities increase in the northern and northwestern United States, driven primarily by rising minimum temperatures and declining wind speeds.

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Distinguishing disturbance from perturbations in fire-prone ecosystems

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Here, we provide a brief overview of examples where anthropogenically driven changes in fire frequency, fire pattern, fuels consumed and fire intensity constitute perturbations that greatly disrupt natural disturbance cycles and put ecosystems on a different trajectory resulting in type conversion. These changes are not due to fire per se but rather anthropogenic perturbations in the natural disturbance regime.

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