Response of net ecosystem gas exchange to a simulated precipitation pulse in a semi-arid grassland: the role of native versus non-native grasses and soil texture

Physiological activity and structural dynamics in arid and semi-arid ecosystems are driven by discrete inputs or “pulses” of growing season precipitation. Here we describe the short-term dynamics of ecosystem physiology in experimental stands of native (Heteropogon contortus) and invasive (Eragrostis lehmanniana) grasses to an irrigation pulse across two geomorphic surfaces with distinctly different soils: a Pleistocene-aged surface with high clay content in a strongly horizonated soil, and a Holocene-aged surface with low clay content in homogenously structured soils. We evaluated whole-ecosystem and leaf-level CO2 and H2O exchange, soil CO2 efflux, along with plant and soil water status to understand potential constraints on whole-ecosystem carbon exchange during the initiation of the summer monsoon season. Prior to the irrigation pulse, both invasive and native grasses had less negative pre-dawn water potentials (Ψpd), greater leaf photosynthetic rates (Anet) and stomatal conductance (gs), and greater rates of net ecosystem carbon exchange (NEE) on the Pleistocene surface than on the Holocene. Twenty-four hours following the experimental application of a 39 mm irrigation pulse, soil CO2 efflux increased leading to all plots losing CO2 to the atmosphere over the course of a day. Invasive species stands had greater evapotranspiration rates (ET) immediately following the precipitation pulse than did native stands, while maximum instantaneous NEE increased for both species and surfaces at roughly the same rate. The differential ET patterns through time were correlated with an earlier decline in NEE in the invasive species as compared to the native species plots. Plots with invasive species accumulated between 5% and 33% of the carbon that plots with the native species accumulated over the 15-day pulse period. Taken together, these results indicate that system CO2 efflux (both the physical displacement of soil CO2 by water along with plant and microbial respiration) strongly controls whole-ecosystem carbon exchange during precipitation pulses. Since CO2 and H2O loss to the atmosphere was partially driven by species effects on soil microclimate, understanding the mechanistic relationships between the soil characteristics, plant ecophysiological responses, and canopy structural dynamics will be important for understanding the effects of shifting precipitation and vegetation patterns in semi-arid environments.

[1]  W. Oechel,et al.  Environmental controls over carbon dioxide and water vapor exchange of terrestrial vegetation , 2002 .

[2]  J. Arnone,et al.  A large daylight geodesic dome for quantification of whole-ecosystem CO2 and water vapour fluxes in arid shrublands , 2003 .

[3]  J. Ehleringer,et al.  Canopy dynamics and carbon gain in response to soil water availability in Encelia frutescens gray, a drought-deciduous shrub , 2004, Oecologia.

[4]  D. Williams,et al.  Drought response of a native and introduced Hawaiian grass , 1994, Oecologia.

[5]  Evan P. Economo,et al.  Scaling metabolism from organisms to ecosystems , 2003, Nature.

[6]  W. Parton,et al.  Primary Production of the Central Grassland Region of the United States , 1988 .

[7]  John Wainwright,et al.  Hydrology–vegetation interactions in areas of discontinuous flow on a semi-arid bajada, Southern New Mexico , 2002 .

[8]  L. Walker,et al.  Impacts of Invasive Plants on Community and Ecosystem Properties , 1997 .

[9]  R. Monson,et al.  Carbon sequestration in a high‐elevation, subalpine forest , 2001 .

[10]  J. Dukes Will the increasing atmospheric CO2 concentration affect the success of invasive species , 2000 .

[11]  J. McAuliffe Landscape Evolution, Soil Formation, and Ecological Patterns and Processes in Sonoran Desert Bajadas , 1994 .

[12]  G. McPherson,et al.  Changing precipitation regimes and terrestrial ecosystems : a North American perspective , 2003 .

[13]  M. Loik,et al.  Photosynthetic responses of Mojave Desert shrubs to free air CO2 enrichment are greatest during wet years , 2003 .

[14]  K. Parker Effects of complex geomorphic history on soil and vegetation patterns on arid alluvial fans , 1995 .

[15]  E. DeLucia,et al.  Consequences of wildfire on ecosystem CO2 and water vapour fluxes in the Great Basin , 2003 .

[16]  F. Giorgi,et al.  Regional Nested Model Simulations of Present Day and 2 × CO2 Climate over the Central Plains of the U.S. , 1998 .

[17]  Lawrence B. Flanagan,et al.  Seasonal and interannual variation in carbon dioxide exchange and carbon balance in a northern temperate grassland , 2002 .

[18]  G. Frasier,et al.  Water balance in pure stand of Lehmann lovegrass. , 1994 .

[19]  George B. Ruyle,et al.  Influence of climatic and edaphic factors on the distribution of Eragrostis lehmanniana Nees in Arizona, USA. , 1986 .

[20]  R. Monson,et al.  Temperature as a control over ecosystem CO2 fluxes in a high-elevation, subalpine forest , 2003, Oecologia.

[21]  M. McClaran,et al.  Spread of introduced Lehmann lovegrass Eragrostis lehmanniana Nees. in Southern Arizona, USA , 1992 .

[22]  F. Shreve,et al.  THE RELATION OF CALICHE TO DESERT PLANTS , 1933 .

[23]  P. Vitousek,et al.  Biological invasions by exotic grasses, the grass/fire cycle, and global change , 1992 .

[24]  Eric A. Davidson,et al.  Minimizing artifacts and biases in chamber-based measurements of soil respiration , 2002 .

[25]  P. D. J. Anderson,et al.  Physiological Ecology of North American Desert Plants , 1996, Adaptations of Desert Organisms.

[26]  J. Ehleringer Annuals and Perennials of warm deserts , 1985 .

[27]  R. Tausch,et al.  Soil water exploitation after fire: competition between Bromus tectorum (cheatgrass) and two native species , 1990, Oecologia.

[28]  A. Knapp,et al.  Fluxes of CO2, water vapor, and energy from a prairie ecosystem during the seasonal transition from carbon sink to carbon source , 1998 .

[29]  Stanley D. Smith,et al.  Soil-plant water relations in a Mojave Desert mixed shrubcommunity: a comparison of three geomorphic surfaces , 1995 .

[30]  A. Franzluebbers,et al.  Environmental Controls on Soil and Whole‐ecosystem Respiration from a Tallgrass Prairie , 2002 .

[31]  I. Noy-Meir,et al.  Desert Ecosystems: Environment and Producers , 1973 .

[32]  J. Harte,et al.  The effect of experimental ecosystem warming on CO2 fluxes in a montane meadow , 1999 .

[33]  Stanley D. Smith,et al.  Water Use by Tamarix Ramosissima and Associated Phreatophytes in a Mojave Desert Floodplain , 1996 .

[34]  Ü. Rannik,et al.  Respiration as the main determinant of carbon balance in European forests , 2000, Nature.

[35]  R. Neilson A Model for Predicting Continental‐Scale Vegetation Distribution and Water Balance , 1995 .

[36]  Stanley D. Smith,et al.  Effects of surface and sub‐surface soil horizons on the seasonal performance of Larrea tridentata (creosotebush) , 2000 .

[37]  G. Cunningham,et al.  The Effect of Carbonate Deposition Layers ("Caliche") on the Water Status of Larrea divaricata , 1973 .

[38]  A. Knapp,et al.  Variation among biomes in temporal dynamics of aboveground primary production. , 2001, Science.

[39]  C. Schwalbe,et al.  Alien annual grasses and their relationships to fire and biotic change in Sonoran desertscrub. , 2002 .

[40]  W. James Shuttleworth,et al.  Modeling multiyear observations of soil moisture recharge in the semiarid American Southwest , 2000 .

[41]  S. Wofsy,et al.  Physiological responses of a black spruce forest to weather , 1997 .

[42]  Tilden P. Meyers,et al.  A comparison of summertime water and CO2 fluxes over rangeland for well watered and drought conditions , 2001 .

[43]  E. McDonald,et al.  ECOLOGICAL RESPONSES OF TWO MOJAVE DESERT SHRUBS TO SOIL HORIZON DEVELOPMENT AND SOIL WATER DYNAMICS , 2002 .