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Fire History and Age Structure Analyses of Kipuka Forests in El Malpais National Monument, New Mexico D aniel B. Lewis Henri D. Grissino-Mayer Laboratory of Tree-Ring Science Department of Geography University of Tennessee Knoxville, Tennessee 37996. About El Malpais.
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Fire History and Age Structure Analyses of Kipuka Forests in El Malpais National Monument, New MexicoDaniel B. LewisHenri D. Grissino-MayerLaboratory of Tree-Ring ScienceDepartment of GeographyUniversity of TennesseeKnoxville, Tennessee 37996
About El Malpais • “el malpais” is Spanish for “badlands” or “bad country” • Established December 31, 1987 to protect a unique lava flow environment • Located in NW New Mexico • A patchwork of lava flows ranging from ca. 110,000-ca. 3200yrs • > 30 cinder cones found in and around the area
Research Questions • How interrelated are the fire regimes of the kipukas and the Hoya Flow? • Does the age structure of the kipukas indicate that forest composition has been altered due changes in their fire regimes? • What can the agencies managing the monument do to preserve these relict areas and reduce the impacts of human disturbances?
Fire History Methods
Fire History Results • Fire frequency increased in the mid-late 1700s, followed by a long, fire-free interval from 1782-1806. • Most fire-free intervals were between 2-10yrs, and more widespread fire-free intervals were between 3-16yrs (all sites combined). • Maximum hazard intervals were 20yrs (all scarred) and 93yrs (10% scarred) (all sites). • The seasonality of fire events changed ca. 1800 from predominantly late season occurrences to predominantly early season occurrences.
Age Structure Results • 64 trees were found on the lower slopes of Hidden Kipuka, 53 occurred as seedlings <20yrs, and only one was >180yrs old. • Seedling density was higher on the western side of Hidden Kipuka due to the more dense ponderosa pine forests on the Hoya Flow. • Lower slopes of Mesita Blanca dominated by trees <40yrs old. • Majority of trees in excess of 100yrs were located on the upper slopes. • Tree density on Mesita Blanca was not noticeably different from the eastern side to the western side.
Conclusions • From 1600-1799, 31% of all fires recorded on the Hoya Flow were synchronous with the kipukas. From 1800-2000, 47% of all fires were synchronous. • When analyzing widespread fire events (10% scarred), only 15% of the fires were synchronous from 1600-1799. From 1800-2000, 61% of the fires in this class were synchronous. • Fires became scarce on the Hoya Flow after 1933. Subsequently, fire frequency declined on the kipukas after 1933.
Conclusions • Inordinate numbers of ponderosa pine seedlings were found on the lower slopes of Hidden Kipuka. • Large numbers of trees <40yrs were found growing on the lower slopes of Mesita Blanca. • The lack of mature ponderosa pines on these lower kipuka slopes indicates these areas were not formerly in the natural range of ponderosa pine in the malpais area.
Recommendations • Allowing fires to burn as they once did prior to Euro-American settlement is problematic due to the proximity of human development. • Before these can be implemented, many areas of the monument will have to be thinned. • The trees growing on the lower slopes of the kipukas should be considered for removal (preferably by methods with low environmental impact).
Acknowledgements • Joint Fire Science Program • El Malpais National Monument • Laboratory of Tree-Ring Science • Committee members: Dr. Henri D. Grissino-Mayer, Dr. Sally P. Horn, Dr. Ken H. Orvis • Department of Geography • Beth Atchley, Michael Armbrister, David Mann, Jake Cseke, Kevin Anchukaitis, Damian Kolbay