In semiarid rangelands, continuous grazing may decrease vegetation cover, accelerating soil erosion and eventually causing a transition to an alternative, degraded state. State-and-transition models invoke process-based explanations of alternative states, but there are few examples that use empirical data on key factors and processes. We used rainfall simulation to determine 1) the relationships between soil surface characteristics and interrill erosion in 3 spatially related plant communities: stable grass with scattered shrubs (GS), degraded grass with scattered shrubs (DGS), and degraded shrub steppes (DSS), and 2) the site conservation threshold (SCT) of this rangeland. We also analyzed the effect of past erosion on soil and vegetation characteristics. In the GS, sediment production and sediment concentration were significantly lower (p , 0.05) than in the DGS and the DSS. The main soil protection factors in the GS and in the DGS were perennial grass and litter cover, while in the DSS, gravel cover became the main soil protection factor. The SCT, the point at which the rate of soil erosion increases markedly, corresponded to a plant-and-litter cover close to 90% and occurred within the DGS. Although this plant community may reverse back to the conserved GS, long-term accelerated erosion may result in enough soil loss to trigger irreversible changes and prompt the transition to the DSS. The threshold underlying this transition would be reached when the A horizon is severely reduced by erosion. Under these conditions, the soil hydrological properties are affected irreversibly, preventing perennial grass establishment. While the GS represents a resource conserving plant community, desirable for both forage production and soil protection, the DSS represents a dysfunctional state with a minimum forage value. The DGS represents an unstable and transitional community that, without management intervention to halt soil erosion, will likely change into the DSS.
ResumenEn los pastizales naturales semi谩 ridos, el pastoreo continuo puede disminuir significativamente la cobertura de la vegetaci贸 n, acelerar la erosi贸 n del suelo y eventualmente causar una transici贸 n hacia estados alternativos degradados. Los modelos de estados y transiciones generalmente explican estados alternativos en funci贸 n de distintos procesos, sin embargo hay pocos ejemplos que usen datos emp铆ricos. Nosotros empleamos lluvia simulada a los fines de determinar 1) las relaciones entre las caracter铆sticas superficiales del suelo y la vegetaci贸 n y la erosi贸 n laminar en 3 comunidades vegetales espacialmente relacionadas: una estepa herb谩 cea con arbustos (EH), una estepa herb谩cea degradada con arbustos (EHD), y una estepa arbustiva degradada (EAD), y 2) el umbral de conservaci贸 n del sitio (UCS) en 茅ste pastizal. Tambi茅n analizamos el efecto de la erosi贸 n hist贸 rica sobre las caracter铆sticas superficiales del suelo y la vegetaci贸 n. En la EH la producci贸 n y la concentraci贸 n de sedimentos fueron significativamente m谩 s bajos (p , 0.05) que...