Linda B. Phillips
Montana State University
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Featured researches published by Linda B. Phillips.
Ecological Applications | 2010
Linda B. Phillips; Andrew J. Hansen; Curtis H. Flather; Jim Robison-Cox
Ecosystem energy is now recognized as a primary correlate and potential driver of global patterns of species richness. The increasingly well-tested species-energy relationship is now ripe for application to conservation, and recent advances in satellite technology make this more feasible. While the correlates for the species-energy relationship have been addressed many times previously, this study is among the first to apply species-energy theory to conservation. Our objectives were to: (1) determine the strongest model of bird richness across North America; (2) determine whether the slope of the best species-energy model varied with varying energy levels; and (3) identify the spatial patterns with similar or dissimilar slopes to draw inference for conservation. Model selection techniques were used to evaluate relationships between Moderate Resolution Imaging Spectroradiometer (MODIS) measures of ecosystem energy and species richness of native land birds using the USGS Breeding Bird Survey (BBS) data. Linear, polynomial, and break point regression techniques were used to evaluate the shape of the relationships with correction for spatial autocorrelation. Spatial analyses were used to determine regions where slopes of the relationship differed. We found that annual gross primary production (GPP) was the strongest correlate of richness (adjusted R2 = 0.55), with a quadratic model being the strongest model. The negative slope of the model was confirmed significantly negative at the highest energy levels. This finding demonstrates that there are three different slopes to the species-energy relationship across the energy gradient of North America: positive, flat, and negative. If energy has a causal relationship with richness, then species-energy theory implies that energy causes richness to increase in low-energy areas, energy has little effect in intermediate-energy areas, and energy depresses richness in the highest-energy areas. This information provides a basis for potential applications for more effective conservation. For example, in low-energy areas, increased nutrients could improve vegetation productivity and increase species richness. In high-energy areas where competitive dominance of vegetation might reduce species richness, vegetation manipulation could increase species richness. These strategies will likely be most effective if tailored to the local energy gradient.
Archive | 2016
Andrew J. Hansen; Linda B. Phillips
An overarching question in natural resource management is, “How well are we sustaining entire ecosystems under climate and land use change?” The chapters of this book have dealt with understanding and managing landforms, tree species, and fish and vegetation communities in the face of changing climate. Application of the Climate-Smart Conservation framework is typically in the context of species, communities, or ecological processes deemed to be the most vulnerable to climate change. The effectiveness of adaptation options for vulnerable elements can be evaluated through adaptive management in which multiple treatments are implemented, monitored, and compared (chap. 13).
Archive | 2016
Andrew J. Hansen; Linda B. Phillips
If one stands on a peak on the eastern side of the Northern Rocky Mountains on a clear day and gazes across the surrounding landscape, striking patterns of vegetation are apparent. From valley bottoms to ridgetops, vegetation grades from grassland and shrublands to open savannas, from dense tall forest to scattered clumps of krumholtz trees in the alpine above the pronounced treeline (fig. 9-1). These recurrent patterns of climatically zoned vegetation suggest that plants are a logical starting point for understanding biodiversity response to climate change. Plants, once established, are sessile and unable to move to more favorable locations and thus are strongly limited by the local climate. The predictable variation in climate with elevation explains this striking pattern of vegetation in the Rockies. To the extent that climate changes in the future, vegetation is expected to change in establishment, growth, and death rates, in canopy structure, and in the distributions of species and thus to show major shifts upward in elevational distribution.
Remote Sensing of Environment | 2008
Linda B. Phillips; Andrew J. Hansen; Curtis H. Flather
Forest Ecology and Management | 2006
Richard H. Waring; Kelsey S. Milner; William M. Jolly; Linda B. Phillips; David B. McWethy
Forest Ecology and Management | 2015
Andrew J. Hansen; Linda B. Phillips
Forest Ecology and Management | 2014
Andrew J. Hansen; Linda B. Phillips; Ralph Dubayah; Scott J. Goetz; Michelle A. Hofton
Global Ecology and Biogeography | 2011
Andrew J. Hansen; Linda B. Phillips; Curtis H. Flather; Jim Robison-Cox
Ecosphere | 2018
Andrew J. Hansen; Linda B. Phillips
Remote Sensing of Environment | 2008
Linda B. Phillips; Andrew J. Hansen; Curtis H. Flather