Whitebark Pine in Crater Lake and Lassen Volcanic National Parks: Assessment of Stand Structure and Condition in a Management and Conservation Perspective
by
Jenell I. Jackson 1, Sean B. Smith 2,*, Jonathan C.B. Nesmith 3, Leigh Ann Starcevich 4
, Jennifer S. Hooke 5, Steve Buckley 6 and Erik S. Jules 1
Jenell I. Jackson 1, Sean B. Smith 2,*, Jonathan C.B. Nesmith 3, Leigh Ann Starcevich 4, Jennifer S. Hooke 5, Steve Buckley 6 and Erik S. Jules 1
1
Humboldt State University, Department of Biological Sciences, 1 Harpst St. Arcata, CA 95521, USA
2
National Park Service, Klamath Network Inventory and Monitoring Program, 1250 Siskiyou Blvd, Ashland, OR 97520, USA
3
National Park Service, Sierra Nevada Network Inventory & Monitoring Program, 47050 Generals Highway, Three Rivers, CA 93271, USA
4
Western EcoSystems Technology, Inc., 2725 NW Walnut Blvd, Corvallis, OR 97333, USA
5
Crater Lake National Park, PO Box 7 Hwy 62 Sager Building, Crater Lake, OR, 97604, USA
6
Lassen Volcanic National Park, PO Box 100, Mineral, CA 96063, USA
*
Author to whom correspondence should be addressed.
Forests 2019, 10(10), 834; https://doi.org/10.3390/f10100834
Received: 25 June 2019 / Revised: 27 August 2019 / Accepted: 18 September 2019 / Published: 21 September 2019
(This article belongs to the Special Issue Ecology and Restoration of Whitebark Pine)
Whitebark pine (Pinus albicaulis. Engelm.) is vulnerable to a number of threats including an introduced pathogen (Cronartium ribicola J.C. Fisch.), epidemic levels of native mountain pine beetle (Dendroctonus ponderosae Hopkins), fire suppression, and climate change. To describe the structure of whitebark pine populations in two national parks in the southern Cascades (Crater Lake, Oregon, USA (CRLA) and Lassen Volcanic, California, USA (LAVO) National Parks), we surveyed trees in 30 × 50 × 50 m plots in both parks. We used these plots to describe the extent of white pine blister rust (the disease caused by Cronartium ribicola), mountain pine beetle occurrence, and to elucidate factors influencing the presence of pests and pathogens, cone production, and canopy kill. In each plot, we recorded data related to tree health, including symptoms of blister rust and mountain pine beetle, and reproductive vigor (cone production). In both parks, encroachment from other species, particularly mountain hemlock (Tsuga mertensiana (Bong.) Carrière), was negatively associated with cone production. In CRLA, water stress was a good predictor of blister rust infection and cone production. For CRLA and LAVO, the presence of mountain pine beetle and blister rust was associated with higher canopy kill for whitebark pine. Lastly, we found evidence for a pest-pathogen interaction, mountain pine beetle attack was greater for trees that showed symptoms of blister rust infection in CRLA. Our results indicate that whitebark pine populations in the southern Cascade Range are experiencing moderate levels of blister rust infection compared with other sites across the species range, and that competition from shade-tolerant species may result in an additional threat to whitebark pine in both parks. We present our findings in the context of park management and situate them in range-wide and regional conservation strategies aimed at the protection and restoration of a declining species.
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MDPI and ACS Style
Jackson, J.I.; Smith, S.B.; Nesmith, J.C.; Starcevich, L.A.; Hooke, J.S.; Buckley, S.; Jules, E.S. Whitebark Pine in Crater Lake and Lassen Volcanic National Parks: Assessment of Stand Structure and Condition in a Management and Conservation Perspective. Forests 2019, 10, 834.
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