Abstract
Relationships between woody plants and grass are typically described at either the stand (≥100 m2) or plant (≤10 m2) spatial resolutions. Descriptions of the Prosopis velutina (mesquite)–grass relationships in the North American Desert Grassland differ between spatial scales: P. velutina often inhibits grass at the stand scale compared to facilitation or neutral relations at the plant scale. We use simultaneous measures of grass density at both spatial resolutions (made at 3 y intervals from 1997 to 2003) to evaluate the influence of the spatial resolution on detecting P. velutina–grass relationships. We confine our observations to the parsimonious conditions of (1) two distinct P. velutina age classes that are exclusive occupants of study sites and (2) total cover of P. velutina was not different between study sites in 2000 and 2003. Thus, total P. velutina cover is constant in those 2 years but P. velutina ages contributing to that cover differed between the study sites. We confirmed the importance of spatial scale because no grass species was related to P. velutina age at the stand scale, but 2 of 5 species were significantly related at the plant scale. Aristida spp. was greater under young than old P. velutina, and Muhlenbergia porteri was greater under old P. velutina. These results suggest that the influence of old P. velutina on grass abundance is restricted to the area under the canopy and does not extend into inter-canopy areas, and therefore the observations at the stand scale may not detect the P. velutina–grass relationships at the plant scale.
Similar content being viewed by others
References
Amundson RG, Ali AR, Belsky AJ (1995) Stomatal responsiveness to changing light intensity increases rain-use efficiency of below-crown vegetation in tropical savannas. J Arid Environ 29:139–153
Barth RC, Klemmedson JO (1982) Amount and distribution of dry matter, nitrogen, and orgnic carbon in soil–plant systems of mesquite and palo verde. J Range Manage 35:412–418
Breckenfeld DJ, Robinett D (2003) Soil and ecological sites on the Santa Rita Experimental Range. In: McClaran MP, Ffolliott PF, Edminster CB (tech. coords.) Santa Rita Experimental Range: 100 years (1903 to 2003) of accomplishments and contributions. Proceedings RMRS-P-30. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Ft. Collins, Colorado, USA, pp 157–165
Cable DR (1971) Lehmann lovegrass on the Santa Rita Experimental Range, 1937–1968. J Range Manage 24:17–21
Cable DR (1975) Influence of precipitation on perennial grass production in the semidesert Southwest. Ecology 56:981–986
Cable DR (1977) Seasonal use of soil water by native velvet mesquite. J Range Manage 30:4–11
Conover WJ, Iman RL (1981) Rank transformations as a bridge between parametric and nonparametric statistics. Am Statist 35:124–129
Drewa PB, Havstad KM (2001) Effects of fire, grazing, and the presence of shrubs on Chihuahuan desert grasslands. J Arid Environ 48:429–443
Franco AC, Nobel PS (1989) Effect of nurse plant on the microhabitat and growth of cacti. J Ecol 77:870–886
House JI, Archer S, Breshears DD, Scholes RJ, NCEAS Tree-Grass Interaction Participants (2003) Conundrums in mixed woody–herbaceous plant systems. J Biogeogr 30:1763–1777
Jameson DA (1967) The relationship of tree overstory and herbaceous understory vegetation. J Range Manage 20:247–249
Littell RC, Milliken GA, Stroup WW, Wolfinger RD, Schabenberger O (2006) SAS for mixed models, 2nd edn. SAS Institue Inc. Cary, North Carolina
Livingston M, Roundy BA, Smith SE (1997) Association of overstory plant canopies and native grasses in southern Arizona. J Arid Environ 35:441–449
Ludwig F, de Kroon H, Berendse F, Prins HHT (2004) The influence of savanna trees on nutrient, water, and light availability and the understory vegetation. Plant Ecol 170:93–105
Martin SC, Cable DR (1974) Managing semidesert grass–shrub ranges: vegetation responses to precipitation, grazing, soil texture, and mesquite control. Technical Bulletin (1480). U.S. Department of Agriculture, Forest Service, Washington DC, USA
Martin SC, Severson KE (1988) Vegetation response to the Santa Rita grazing system. J Range Manage 41:291–295
McClaran MP (2003) A century of vegetation change on the Santa Rita Experimental Range. In: McClaran MP, Ffolliott PF, Edminster CB (tech. coords.) Santa Rita Experimental Range: 100 years (1903 to 2003) of accomplishments and contributions. Proceedings RMRS-P-30. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Ft. Collins, Colorado, USA, pp 16–33
McClaran MP, Angell DL (2006) Long-term vegetation response to mesquite removal in desert grassland. J Arid Environ 66:686–697
McClaran MP, Angell DL, Wissler C (2002) Santa Rita Experimental Range digital database: user’s guide. General Technical Report RM GTR-100. U.S. Department of Agriculture, Forest Service, Rocky Mountain Experiment Station, Ft. Collins, Colorado, USA
Parker KW, Martin SC (1952) The mesquite problem on southern Arizona ranges. Circular 908. U.S. Department of Agriculture, Washington DC, USA
Scholes RJ, Archer S (1997) Tree–grass interactions in Savannas. Annu Rev Ecol System 28:517–544
Stuart-Hill GC, Tainton NM (1989) The competitive interaction between Acacia karroo and the herbaceous layer and how this is influenced by defoliation. J Appl Ecol 26:285–298
Tewksbury JJ, Lloyd JD (2001) Positive interactions under nurse-plants: spatial scale, stress gradients and benefactor size. Oecologia 127:425–434
Tiedemann AR, Klemmedson JO (1977) Effect of mesquite trees on vegetation and soils in the desert grassland. J Range Manage 30:361–367
Tiedemann AR, Klemmedson JO (1986) Long-term effects of mesquite removal on soil characteristics: I. Nutrients and bulk density. Soil Sci Soc Am J 50:472–475
Tiedemann AR, Klemmedson JO (2004) Responses of desert grassland vegetation to mesquite removal and regrowth. J Range Manage 57:455–465
Tiedemann AR, Klemmedson JO, Ogden PR (1971) Response of four perennial southwest grasses to shade. J Range Manage 24:442–447
Turner MG, Gardner RH, O’Neill RV (2001) Landscape ecology in theory and practice: pattern and process. Springer, New York
Warren A, Holechek J, Cardenas M (1996) Honey mesquite influences on Chihuahuan desert vegetation. J Range Manage 49:46–52
Williams PT (1976) Grass production changes with mesquite (Prosopis juliflora) reinvasion in southern Arizona. M.S. Thesis, University of Arizona: Tucson, Arizona, USA, 37 pp
Yavitt JB, Smith EL (1983) Spatial patterns of mesquite and associated herbaceous species in an Arizona desert grassland. Am Midland Nat 109:89–93
Acknowledgments
Data sets were provided by the Santa Rita Experimental Range Digital Database (http://ag.arizona.edu/srer). Funding for the digitization of these data and for their analysis in this paper was provided by the US Department of Agriculture Forest Service Rocky Mountain Research Station, University of Arizona Agricultural Experiment Station, and University of California Los Alamos National Laboratory. K. Van Deren, M. Livingston, and S. Jorstad assisted with field data collection, and S. Archer and three anonymous reviewers provided valuable comments on earlier versions of this manuscript.
Author information
Authors and Affiliations
Corresponding author
Rights and permissions
About this article
Cite this article
McClaran, M.P., Angell, D.L. Mesquite and grass relationships at two spatial resolutions. Plant Ecol 191, 119–126 (2007). https://doi.org/10.1007/s11258-006-9220-6
Received:
Accepted:
Published:
Issue Date:
DOI: https://doi.org/10.1007/s11258-006-9220-6