Abstract:Abstract. Ecosystems can shift between alternative states characterized by persistent differences in structure, function, and capacity to provide ecosystem services valued by society. We examined empirical evidence for alternative states in a semiarid grassland ecosystem where topographic complexity and contrasting management regimes have led to spatial variations in levels of livestock grazing. Using an inventory data set, we found that plots (n ¼ 72) cluster into three groups corresponding to generalized alt… Show more
“…However, we propose that evaluating the longer-term effects of rehabilitation treatments on plant community cover and composition is needed given the increasing interest from society in the multiple ecosystem services public lands provide (e.g., wildlife, nativeness, forage, etc. ; Havstad et al 2007, Dodds et al 2008, Miller et al 2011.…”
Section: How Then To Decide If Active Rehabilitation Is Needed and Imentioning
Abstract. Uncontrolled wildfire in arid and semiarid ecosystems has become an increasing concern in recent decades. Active rehabilitation of fire-affected areas is often quickly initiated to minimize long-term ecosystem damage. However, the complex soil-geomorphic-vegetation patterns and low and variable moisture conditions in these regions makes restoration challenging. To further inform these post-fire management decisions, we present results from 5 years of vegetation and sediment flux monitoring following the Milford Flat Fire in west-central Utah, USA. Our sampling design includes monitoring plots in areas not burned, areas burned but where no rehabilitation was attempted, and burned areas where various rehabilitation approaches were implemented. At each of the 25 plots, vegetation cover and composition data were collected annually, and wind-driven sediment flux was measured using passive dust traps. To evaluate effectiveness of post-fire rehabilitation treatments in establishing desired species and limiting dominance of undesired species, we analyzed the temporal response of individual species and functional groups as well as community-level multivariate responses. The warm and dry conditions that persisted for approximately 12 months post-treatment, coupled with the surface disturbing rehabilitation approaches used, resulted in near-surface dust fluxes several orders of magnitude higher in treated areas than in unburned or burned areas where no rehabilitation occurred. These dry conditions and high surface sediment flux limited the establishment of seeded species in rehabilitation areas for nearly 3 years. Post-fire rehabilitation did not limit dominance by invasive annual species of concern. Perennial species composition in the areas burned but not subject to post-fire rehabilitation was relatively similar to unburned throughout the study period. In contrast, the burned plots where rehabilitation was attempted were characterized by no (,3%) perennial cover or, in response to moister conditions, seeded forage species. These results suggest the post-fire rehabilitation efforts conducted in the lower elevation regions affected by the Milford Flat Fire were not generally successful. Though dry conditions are likely to blame for the lack of success, the low and variable precipitation characteristic of these regions suggest future post-fire rehabilitation decisions must assume that precipitation is going to be insufficient and plan rehabilitation efforts that are resilient to dry conditions.
“…However, we propose that evaluating the longer-term effects of rehabilitation treatments on plant community cover and composition is needed given the increasing interest from society in the multiple ecosystem services public lands provide (e.g., wildlife, nativeness, forage, etc. ; Havstad et al 2007, Dodds et al 2008, Miller et al 2011.…”
Section: How Then To Decide If Active Rehabilitation Is Needed and Imentioning
Abstract. Uncontrolled wildfire in arid and semiarid ecosystems has become an increasing concern in recent decades. Active rehabilitation of fire-affected areas is often quickly initiated to minimize long-term ecosystem damage. However, the complex soil-geomorphic-vegetation patterns and low and variable moisture conditions in these regions makes restoration challenging. To further inform these post-fire management decisions, we present results from 5 years of vegetation and sediment flux monitoring following the Milford Flat Fire in west-central Utah, USA. Our sampling design includes monitoring plots in areas not burned, areas burned but where no rehabilitation was attempted, and burned areas where various rehabilitation approaches were implemented. At each of the 25 plots, vegetation cover and composition data were collected annually, and wind-driven sediment flux was measured using passive dust traps. To evaluate effectiveness of post-fire rehabilitation treatments in establishing desired species and limiting dominance of undesired species, we analyzed the temporal response of individual species and functional groups as well as community-level multivariate responses. The warm and dry conditions that persisted for approximately 12 months post-treatment, coupled with the surface disturbing rehabilitation approaches used, resulted in near-surface dust fluxes several orders of magnitude higher in treated areas than in unburned or burned areas where no rehabilitation occurred. These dry conditions and high surface sediment flux limited the establishment of seeded species in rehabilitation areas for nearly 3 years. Post-fire rehabilitation did not limit dominance by invasive annual species of concern. Perennial species composition in the areas burned but not subject to post-fire rehabilitation was relatively similar to unburned throughout the study period. In contrast, the burned plots where rehabilitation was attempted were characterized by no (,3%) perennial cover or, in response to moister conditions, seeded forage species. These results suggest the post-fire rehabilitation efforts conducted in the lower elevation regions affected by the Milford Flat Fire were not generally successful. Though dry conditions are likely to blame for the lack of success, the low and variable precipitation characteristic of these regions suggest future post-fire rehabilitation decisions must assume that precipitation is going to be insufficient and plan rehabilitation efforts that are resilient to dry conditions.
“…Los ecosistemas áridos y semiáridos ocupan casi un 40 % de la superficie terrestre , y son especialmente susceptibles a degradación de sus atributos estructurales y funcionales, y la CBS juega un papel crucial en el mantenimiento de su resiliencia (Miller et al 2011). Esto es debido a que por sus atributos fisiomorfológicos, las diferentes especies de CBS representan un conjunto de diferentes grupos funcionales de gran peso y carentes de redundancia funcional a nivel del ecosistema (Miller et al 2011).…”
Section: Aplicación Del Conocimiento De La Cbs a Nivel Específico En unclassified
“…Finalmente, la CBS interacciona con otros microorganismos y microfauna del suelo, ya que les proporciona recursos y un hábitat potencial (Neher et al 2003;Bamforth 2004;Castillo-Monroy et al 2011b). Es por ello, que la CBS ha sido considerada como un "ingeniero ecosistémico" y "elemento clave" en ambientes áridos y semiáridos (Eldridge et al 2010;Miller et al 2011). …”
“…Different authors have used different conventions to develop model diagrams and narratives. Models can be entirely qualitative/descriptive (Knapp and FernandezGimenez 2009;Kachergis et al 2013), quantify only properties of states Miller et al 2011), or quantify states and/or transitions (Jackson and Bartolome 2002;Czembor and Vesk 2009;Rumpff et al 2011). Across all model types, however, there are a set of common elements that define an STM.…”
Section: Development Of State and Transition Modelsmentioning
confidence: 99%
“…In some instances, plant communities linked via transient dynamics are represented as "states" in the broad sense (Jackson and Bartolome 2002;Bagchi et al 2012) and in other cases, alternative stable states in the narrow sense are emphasized and transient dynamics within states are described separately or ignored (Miller et al 2011).…”
State and transition models (STMs) are used to organize and communicate information regarding ecosystem change, especially the implications for management. The fundamental premise that rangelands can exhibit multiple states is now widely accepted and has deeply pervaded management thinking, even in the absence of formal STM development. The current application of STMs for management, however, has been limited by both the science and the ability of institutions to develop and use STMs. In this chapter, we provide a comprehensive and contemporary overview of STM concepts and applications at a global level. We first review the ecological concepts underlying STMs with the goal of bridging STMs to recent theoretical developments in ecology. We then provide a synthesis of the history of
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