- Author: Christian Jordan
Early one morning this fall, three National Park Service researchers from the Klamath Inventory and Monitoring Network (KLMN) scrambled over minivan-sized boulders on a remote butte in Lassen Volcanic National Park. Their goal -- to reach plot three, the most difficult to access site in the National Park Service's Whitebark Pine Monitoring Network at Lassen.
Since 2012, the KLMN has studied whitebark pine populations at Crater Lake and Lassen Volcanic National Parks to assess species health and long-term trends, specifically threats from blister rust and mountain pine beetle. At Lassen Volcanic, the Network has thirty 50m2 plots, with ten plots sampled each year. Dr. Lauren Youngblood, an Ecologist with the KLMN, is the lead scientist for the whitebark pine monitoring program at Crater Lake and Lassen Volcanic National Parks. When assessing whitebarks within each plot, Youngblood and her crew measure tree size (diameter at breast height), tree height, and percent of live canopy while also assessing for encroachment from other conifers and signs of white pine blister rust infection or mountain pine beetle attack.
Youngblood and her team did reach plot three that day, where signs of blister rust infection, mountain pine beetle attack, and associated mortality were detected on several whitebarks. Read on to learn more about whitebark pines, their uncertain future, and a conversation with Youngblood.
An Iconic Species
Whitebark pine is a long-lived, high elevation conifer found in the mountains of Western North America. In the Cascades, including at Lassen Volcanic National Park, the species is mostly found above 7000 feet. Despite the harsh summer and winter environments of their range, whitebarks can survive for hundreds of years, often living between 500 and 1000 years. The oldest known whitebark is over 1200 years old (National Park Service 2014).
Whitebark pine are recognized as both a foundation and keystone species, serving many critical roles in their ecosystems including increasing biodiversity, providing food and shelter for other species, capturing and retaining snowpack, reducing erosion, and improving water quality (National Park Service 2014; Schoettle et al. 2023; Ellison et al. 2005).
However, despite their longevity and capacity to endure harsh environmental conditions, whitebark pine are under threat. In recent years, white pine blister rust (a non-native and invasive fungus) and mountain pine beetle have led to a significant decline of whitebark pine across much its range. According to one study, approximately 54% of standing whitebark trees were dead as of 2019 (Goeking and Windmuller-Campione 2021). This high level of mortality represents a significant increase from 2009, when about 43% of standing whitebarks were dead, and 1999, when the figure was just 12% (Goeking and Windmuller-Campione 2021; Oswalt et al. 2019). The outlook for whitebark pine is bleak enough that it was listed as threatened with potential extinction under the Endangered Species Act in 2022 (whitebark pine is listed as an endangered species in Canada).
Despite these statistics, there is some reason for optimism. Recent research found high levels of resistance to white pine blister rust in certain whitebark pine populations (Sniezko et al. 2024). At Crater Lake, whitebarks have already been planted as part of a restoration planting and genetic trial. While young now, these trees may live hundreds of years.
A Conversation with Dr. Lauren Youngblood, Ecologist leading the Klamath Network's Whitebark Pine monitoring program
What are the objectives of the Klamath Inventory & Monitoring Network's Whitebark Pine Monitoring Network?
The objectives of our whitebark pine monitoring protocol are to quantify: 1) infection and death rates of whitebark pine from blister rust disease, mountain pine beetle, and other agents (e.g., fire, native diseases, etc.) over time, and 2) associated plant species composition. To meet our objectives, we monitor evidence of infection from blister rust and mountain pine beetles, as well as tree and seedling growth, at our 60 established plots in Crater Lake and Lassen Volcanic National Park.
What trends in whitebark pine health have been observed since the program began in 2012?
A recent report found that Whitebark pine in Crater Lake and Lassen Volcanic National Parks had higher rates of blister rust infestation and higher associated crown kill compared to other white pines in nearby western national parks (Reilly et al., 2022). Overall, we see lower incidence of blister rust at Lassen Volcanic as opposed to Crater Lake National Park -- and this is likely the result of environmental interactions, like elevation, temperature, and humidity shaping blister rust transmission. Analyses are currently underway to quantify how blister rust, mountain pine beetles, and abiotic factors – including novel thermal and hydric regimes due to climate change-- interact to shape whitebark pine populations in Crater Lake and Lassen Volcanic National Parks. As of today, we've completed four rounds of repeat sampling in our 2023 season, and we completed our 5th visit to panel 1 plots in the 2024 season. We're just now getting to the point where we have enough repeat sampling to facilitate exciting trend analyses, so stay tuned for future reports!
Any optimistic statements about the future of whitebark pines?
While some of what I've said above may sound pessimistic, I do feel hopeful about the future of whitebark pine populations in our Klamath Network parks. Through our analyses, we've been able to identify a handful of whitebark pine trees that are potentially resistant to blister rust. Crater Lake has a strong conservation program that works with the Dorena Genetic Resource Center to study the genetic underpinning of blister rust resistance and has been replanting rust resistant seedlings in the park with great success. This work was largely led by Jen Hooke, who was a vegetation Ecologist at CRLA for many years before moving to a position with the USFS last year. You can read more about that program here. In addition to long-term monitoring, conservation programs like these will be key to preserving whitebark pine populations in our parks in the future.
RESOURCES AND FURTHER READING:
Ellison A. M., Bank, M., Clinton B., Colburn E., Elliott K., Ford, C., Foster D., Kloeppel B., Knoepp J., Lovett G., Mohan J., Orwig D., Rodenhouse N.; Sobczak W, Stinson K., Stone J., Swan C., Thompson V., Von Holle B., and Webster J. 2005. Loss of foundation species: Consequences for the structure and dynamics of forested ecosystems. Frontiersin Ecology and the Environment 3, 479–486. Doi: 10.1890/1540-9295(2005)003[0479:LO-FSCF]2.0.CO;2.
Goeking S.A. and Windmuller-Campione M.A. 2021. Comparative species assessments of five-needle pines throughout the western United States. Forest Ecology and Management. 496(2021)119438. https://doi.org/10.1016/j.foreco.2021.119438.
National Park Service, U.S. Department of the Interior. 2014. “Resource Brief: Whitebark Pine (Pinus abicaulis).” Crown of the Continent Research Learning Center. April 2014. Whitebark Pine Resource Brief.
National Park Service, U.S. Department of the Interior. 2022. “Status of White Pines Across Five Western National Park Units – Initial Assessment of Stand Structure and Condition, Revised October 2021.” National Resource Stewardship and Science Natural Resource Report NPS/KLMN/NRR—2022/2342.
Oswalt S.N., Smith W.B., Miles P.D., and Pugh S.A., 2019. Forest Resources of the United States, 2017: A Technical Document Supporting the Forest Service 2020 RPA Assessment. Gen Tech Rep WO-97 Wash. DC US Dep. Agric. For. Serv. Wash. Off., pp. 97. https://doi.org/10.2737/WO-GTR-97.
Reilly M.J., Nesmith J.C.B., Smith S.B., Stucki D.S., and Jules E.S. 2022. Status of white pines across five western national park units: Initial assessment of stand structure and condition, revised October 2021. Natural Resource Report NPS/KLMN/NRR—2022/2342. National Park Service, Fort Collins, Colorado. https://doi.org/10.36967/nrr-2288668.
Schoettle A.W., Keane II R.E., Bentz B.J., and Goeking S.A. 2023. “Not on Our Watch: Scientists and Managers Rush to Save High-Elevation, Five-Needle Pines.” United States Department of Agriculture Rocky Mountain Research Station, Science You Can Use Bulletin. July/August 2023. Issue 61.
Sniezko R.A., Johnson J.S., Kegley A., and Danchok R. 2024. Disease resistance in whitebark pine and potential for restoration of a threatened species. Plants, People, Planet, 6(2), 341-361. https://doi.org/10.1002/ppp3.10443.
Tomback D.F. and Achuff P. 2010. Blister rust and western forest biodiversity: ecology, values and outlook for white pines. Forest Pathology 40(2010) 186-225. https://doi.org/10.1111/j.1439-0329.2010.00655.x.
- Author: Christian Jordan
The Siskiyou County Prescribed Burn Association (PBA) will host a California Certified Prescribed Fire Burn Boss (CARX) training in Yreka, California from January 13th-17th, 2025. "After having spent since January working with the Siskiyou PBA, one of the limitations I've seen to increasing the pace and scale of private property burning in Siskiyou County is the lack of CARX burn boss capacity," said Patricia Grantham, Coordinator of the Siskiyou PBA. "Having the Fire Marshall's course hosted in Yreka is a tremendous opportunity to address this limitation. We need to fill the seats!"
Below is some additional information regarding the CARX training. Please contact Patricia Grantham with any questions: pgrantham@svrcd.org.
From the Office of the State Fire Marshall's website: The CAL FIRE-Office of the State Fire Marshal (OSFM) State-Certified Prescribed-Fire Burn Boss is for persons seeking Certification to plan and manage prescribed fire on State or private lands. A State-Certified Prescribed-Fire Burn Boss may possess authority to engage in a prescribed burning operation and to enter into the necessary contracts with the Department of Forestry and Fire Protection. The qualifications are documented in the State Certified Prescribed-Fire Burn Boss Certification Training Standards (CTS).
A State-Certified Prescribed-Fire Burn Boss performs prescribed-fire planning, obtains state or local approval and permits, develops and implements a burn plan, monitors fire effects, maintains prescriptive requirements, and conducts an After-Action Review.
From the California Wildfire and Forest Resilience Task Force Website: Obtaining the CARX qualification also allows access to the Prescribed Fire Liability Claims Fund, which provides up to $2 million in coverage for prescribed fire projects led by a qualified burn boss or cultural practitioner. (Note: Claims fund project enrollment is also available to those holding a current NWCG RXB1 or RXB2 qualification.)
Prerequisites for the CARX course:
Coursework Requirements
1. IS-100 Introduction to the Incident Command System
2. S-190 Introduction to Wildland Fire Behavior
3. S-130 Firefighter Training
4. S-290 Intermediate Wildland Fire Behavior (classroom only, online courses not accepted)
Firing Requirements
Qualified NWCG/CICCS Firing Boss (FIRB) or both equivalent firing experience and one of the following courses: S-219 Firing Operations, CA-219 Wildland Firefighting – Firing Operations, C-234 Ignition Operations, or S-234 Ignition Operations
Leadership Requirements
S-131 Advanced Firefighter or L-280 Followership to Leadership or Qualified NWCG/CICCS Firefighter Type 1 (FFT1) or Equivalent leadership experience
After successfully attending the CARX course, initiating and completing a task book is required prior to certification.
- Author: Christian Jordan
The Forestry Institute for Teachers (FIT) will be hosting two "FIT-Focus" sessions this Fall, including one in Plumas County. Please see the below message and attached flier for additional details:
- Author: Christian Jordan
Shasta College will host a Geographic Information Systems (GIS) for Forest Resilience workshop this October. The course has been developed with industry partners and will provide practical, applied experience in the use of GIS to support project management for forest and wildfire resilience. The workshop will take place on four consecutive Saturdays, beginning October 5th. The attached flier includes further details. For additional information or questions, please reach out to Dan Scollon: dscollon@shastacollege.edu.
- Author: Christian Jordan
On August 3rd, 2021, the Antelope Fire reached the Goosenest Adaptive Management Area (GAMA) on the Klamath National Forest in Siskiyou County. For six days, the fire burned through the predominately ponderosa pine and white fir forest, exhibiting mild, moderate, and extreme fire behavior. Fortunately for Pacific Southwest Research Station Scientists, the fire offered a unique opportunity to study the effectiveness of fuel treatments on wildfire behavior and severity.
Prior to the Antelope Fire's arrival, twenty-three study plots at GAMA had received four different fuel treatments: 1) Thin-only (emphasis on pine retention), 2) Thin-only (emphasis on big tree retention), 3) Thin (emphasis on pine retention) plus Prescribed Fire (two broadcast burns, nine years apart), and 4) Fire-only (two broadcast burns nine years apart). Untreated control plots provided a baseline for the study. “I think what's incredible about the Goosenest data set is that because of the number of replicated treatments that we had, and because they were laid out in a randomized experiment before the fire came through, we really had this incredible and to our knowledge unprecedented opportunity [to assess fuel treatment effectiveness],” said Emily Brodie, Forest Monitoring Scientist with CAL FIRE, Former Postdoctoral Scholar at the Pacific Southwest Research Station, and one of the paper's co-authors.
When researchers returned to the site post-fire, they found more than just a black forest. Overall, fuel treatments resulted in lower fire severity across all four metrics examined: tree mortality, average bole char-height, percent crown volume consumed (PCVC), and percent crown volume affected (PCVA). All treatments were found to lower fire severity, with thinning plus prescribed fire being the most effective.
“I was most excited about these areas where the road went through and on one side you had a treatment that had received thinning and burning and the trees were totally green,” said Brodie. “And on the other side, there was a control where no treatment action had occurred. Those trees were completely charred.”
The study also demonstrated that fuel treatments can be effective over a decadal or multi-decadal time period – it had been ten years since prescribed fire and twenty years since mechanical thinning had been implemented at the study plots. Importantly, treatments were still effective under extreme weather conditions.
“In a nutshell, what our study showed is that fuel treatments changed outcomes, even under the most extreme weather conditions,” said Eric Knapp, Research Ecologist at the Pacific Southwest Research Station and one of the paper's co-authors. “Fuels really do matter. When the winds were the strongest and the humidity was super low, only the trees in the treated areas really had a chance. Going forward in a time of increasing fire activity, if we want forests that are resilient to these types of fires, it's going to become increasingly important to keep both the canopy fuels and the ground fuels low and keep them managed.”
For more details and insights on the paper, please refer to the following resources:
Brodie, Emily G.; Knapp, Eric E.; Brooks, Wesley R.; Drury, Stacy A.; Ritchie, Martin W. 2024. Forest thinning and prescribed burning treatments reduce wildfire severity and buffer the impacts of severe fire weather. Fire Ecology. 20(1): 11770. https://doi.org/10.1186/s42408-023-00241-z.
An Interview with Emily Brodie and Eric Knapp: Through The Fire | US Forest Service Research and Development (usda.gov)