Fire versus grazing as tools to restore serpentine grasslands under global change
Corresponding Author
Eliza Hernández
Environmental Studies Program, University of Oregon, Eugene, OR, 97403 U.S.A.
Address correspondence to E. Hernández, email [email protected], L. Hallett, email [email protected]
Search for more papers by this authorE. Ashley Shaw
Department of Biology, University of Oregon, Eugene, OR, 97403 U.S.A.
Search for more papers by this authorLina Aoyama
Environmental Studies Program, University of Oregon, Eugene, OR, 97403 U.S.A.
Department of Biology, University of Oregon, Eugene, OR, 97403 U.S.A.
Search for more papers by this authorAlejandro Brambila
Environmental Studies Program, University of Oregon, Eugene, OR, 97403 U.S.A.
Department of Biology, University of Oregon, Eugene, OR, 97403 U.S.A.
Search for more papers by this authorChristal Niederer
Creekside Center for Earth Observation, Menlo Park, CA, 94025 U.S.A.
Search for more papers by this authorStuart B. Weiss
Creekside Center for Earth Observation, Menlo Park, CA, 94025 U.S.A.
Search for more papers by this authorCorresponding Author
Lauren M. Hallett
Environmental Studies Program, University of Oregon, Eugene, OR, 97403 U.S.A.
Department of Biology, University of Oregon, Eugene, OR, 97403 U.S.A.
Address correspondence to E. Hernández, email [email protected], L. Hallett, email [email protected]
Search for more papers by this authorCorresponding Author
Eliza Hernández
Environmental Studies Program, University of Oregon, Eugene, OR, 97403 U.S.A.
Address correspondence to E. Hernández, email [email protected], L. Hallett, email [email protected]
Search for more papers by this authorE. Ashley Shaw
Department of Biology, University of Oregon, Eugene, OR, 97403 U.S.A.
Search for more papers by this authorLina Aoyama
Environmental Studies Program, University of Oregon, Eugene, OR, 97403 U.S.A.
Department of Biology, University of Oregon, Eugene, OR, 97403 U.S.A.
Search for more papers by this authorAlejandro Brambila
Environmental Studies Program, University of Oregon, Eugene, OR, 97403 U.S.A.
Department of Biology, University of Oregon, Eugene, OR, 97403 U.S.A.
Search for more papers by this authorChristal Niederer
Creekside Center for Earth Observation, Menlo Park, CA, 94025 U.S.A.
Search for more papers by this authorStuart B. Weiss
Creekside Center for Earth Observation, Menlo Park, CA, 94025 U.S.A.
Search for more papers by this authorCorresponding Author
Lauren M. Hallett
Environmental Studies Program, University of Oregon, Eugene, OR, 97403 U.S.A.
Department of Biology, University of Oregon, Eugene, OR, 97403 U.S.A.
Address correspondence to E. Hernández, email [email protected], L. Hallett, email [email protected]
Search for more papers by this authorAuthor contributions: SBW conceived and designed the research; SBW, CN conducted the study; EH, LMH cleaned the data; EAS, LA, AB, EH, LMH analyzed the data; EAS, LMH, EH, LA, AB wrote the manuscript; CN, SBW edited the manuscript.
Abstract
Grassland restoration in a world of change—including nitrogen deposition and invasion—requires solutions that can be sustained and effective in the face of novel drivers. This challenge is amplified in systems characterized by high spatiotemporal variability, as management to address novel drivers may affect a system differently across its range of variability. California serpentine grasslands epitomize this challenge: they host a high diversity of native species, are characterized by temporal and spatial variability, and are experiencing atmospheric nitrogen deposition that leads to a conversion from native annual forbs to non-native annual grasses. Here, we test the interactive effects of grazing and fire to restore native serpentine species following annual grass invasion and litter accumulation. We assess management outcomes (burned-grazed, burned-ungrazed, and unburned-ungrazed) using a long-term (2004–2012) monitoring dataset. A 2004 wildfire led to a reduction in annual grasses and a transient increase in native species (forb) richness. In 2008, cattle grazing was reintroduced and crossed with the burn legacy, which sustained post-fire diversity and eventually led to native recovery in unburned areas, with a caveat that a period of high precipitation promoted the growth of annual grasses. Our study indicates that short-term management, such as fire, can promote native forb recovery in invaded serpentine grassland communities, but that ongoing treatments like grazing are necessary to maintain restoration outcomes. We speculate that this recovery may be due to the presence of a robust native seed bank, which may persist despite a period of annual grass conversion.
Supporting Information
| Filename | Description |
|---|---|
| rec13353-sup-0001-Supinfo.docxWord 2007 document , 1.5 MB | Table S1. Permutational multivariate analysis of variance (perMANOVA) tests. Table S2. Pairwise Least-Square Means post-hoc contrasts for linear mixed effects models Table S3. p-values for pairwise comparisons between burned-grazed, unburned-grazed, and burned-ungrazed treatments. Table S4. Multilevel pattern analysis results listing significant indicator species within group and combination of groups by year. Figure S1. Map of experimental transects at our study site, Tulare Hill, California. Figure S2. Native forb relative percent cover (A), richness (B), and non-native grass relative percent cover (C), and richness (D) by transect from 2005–2012. Figure S3. Cover and richness response of native grasses and non-native forbs. Figure S4. Time series of absolute cover (%) of Plantago erecta from 2001 to 2018. Figure S5. Litter and precipitation lag effects on native forb richness and cover + correlation between prior year precipitation and litter cover. |
Please note: The publisher is not responsible for the content or functionality of any supporting information supplied by the authors. Any queries (other than missing content) should be directed to the corresponding author for the article.
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