Abstract
Graminoids and forbs are important entities in grassland community assembly, differing in their functional properties. In our study, we asked 1. Do graminoids and forbs differ in the speed of root proliferation into soil patches established under field conditions? 2. Is the patch occupation dynamics affected by the nutrient concentration in the patch? 3. What is the temporal dynamics of available macronutrients in an experimental patch and does it provide comparative advantage to any of these two categories in connection with their root proliferation dynamics? We used ingrowth core technique. Proliferated roots were sampled after 1, 2, 4, 8, or 15 weeks, with forb and graminoid categories distinguished on anatomical basis. We measured root length and root dry weight, concentration of NH4+, NO3−, and of exchangeable phosphorus in the soil. Roots of both functional groups proliferated more intensively in enriched soil patches than in the control ones, but graminoids entered experimental patches more rapidly. Soil concetration of available N fell down to the background level in four weeks. The initial head start by graminoids seems to be crucial for the overall patch exploitation, because the concentration of available nutrient forms, namely nitrate and ammonium, decreases rapidly.
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Abbreviations
- SRL:
-
specific root length; root length divided by their dry weight
- GFR-W:
-
graminoid to forb ratio based on dry weight of their roots
- GFR-L:
-
graminoid to forb ratio based on their root length
- NTOT, PTOT :
-
total amount of N and P in the aboveground parts of graminoids and forbs growing in the close patch neighbourhood
- RGR:
-
relative growth rate of roots
References
Berendse F (1982) Competition between plant populations with different rooting depths. III. Field experiments. Oecologia 53:50–55
Bret-Harte MS, Mack MC, Goldsmith GR et al (2008) Plant functional types do not predict biomass responses to removal and fertilization in Alaskan tussock tundra. J Ecol 96:713–726
Butler JD, Rieke PE, Minner DD (1985) Influence of water quality on turfgrass. In: Gibeault VA, Cockerham ST (eds) Turfgrass, water conservation. University of California, Oakland, pp 71–84
Campbell BD, Grime JP, Mackey JML (1991) A trade-off between scale and precision in resource foraging. Oecologia 87:532–538
Cornelissen JHC, Aerts R, Cerabolini B et al (2001) Carbon cycling traits of plant species are linked with mycorrhizal strategy. Oecologia 129:611–619
Craine JM, Froehle J, Tilman DG et al (2001) The relationships among root and leaf traits of 76 grassland species and relative abundance along fertility and disturbance gradients. Oikos 93:274–285
Crick JC, Grime JP (1987) Morphological plasticity and mineral nutrient capture in two herbaceous species of contrasted ecology. New Phytol 107:403–414
Diaz S, Cabido M (2001) Vive la difference: plant functional diversity matters to ecosystem processes. Trends Ecol Evol 16:646–655
Einsmann JC, Jones RH, Pu M et al (1999) Nutrient foraging traits in 10 co-occurring plant species of contrasting life forms. J Ecol 87:609–619
Farley RA, Fitter AH (1999) Temporal and spatial variation in soil resources in a deciduous woodland. J Ecol 87:688–696
Fitter AH (1986) Spatial and temporal patterns of root activity in a species-rich alluvial grassland. Oecologia 69:594–599
Fransen B, Blijjenberg J, de Kroon H (1999) Root morphological and physiological plasticity of perennial grass species and the exploitation of spatial and temporal heterogeneous nutrient patches. Plant Soil 211:179–189
Gross KL, Maruca D, Pregitzer KS (1992) Seedling growth and root morphology of plants with different life-histories. New Phytol 120:535–542
Hodge A, Robinson D, Griffiths BS et al (1999) Why plants bother: root proliferation results in increased nitrogen capture from an organic patch when two grasses compete. Plant Cell Environ 22:811–820
Kubát K et al (2002) Klíč ke květeně České republiky [Key to the Flora of the Czech Republic]. Academia, Praha
Kull O, Aan A (1997) The relative share of graminoid and forb life-forms in a natural gradient of herb layer productivity. Ecography 20:146–154
Lepik M, Liira J, Zobel K (2004) The space-use strategy of plants with different growth forms, in a field experiment with manipulated nutrients and light. Folia Geobot 39:113–127
Levang-Brilz N, Biondini ME (2003) Growth rate, root development and nutrient uptake of 55 plant species from the Great Plains Grasslands, USA. Plant Ecol 165:117–144
Neill C (1992) Comparison of soil coring and ingrowth methods for measuring below-ground production. Ecology 73:1918–1921
Newsham KK, Fitter AH, Watkinson AR (1995) Multi-functionality and biodiversity in arbuscular mycorrhizas. Trends Ecol Evol 10:407–411
Nippert JB, Knapp AK (2007) Soil water partitioning contributes to species coexistence in tallgrass prairie. Oikos 116:1017–1029
Olsen SR, Sommers LE (1982) Phosphorus. In: Page AL, Miller RH, Keeney DR (eds) Methods of soil analysis, part 2. Agronomy, 9. ASA, Madison, Wisconsin, pp 403–430
Pokorny ML, Sheley RL, Svejcar TJ et al (2004) Plant species diversity in a grassland plant community: evidence for forbs as a critical management consideration. West N Am Nat 64:219–230
R Development Core Team (2008) R: A language and environment for statistical computing. R Foundation for Statistical Computing, Vienna, Austria
Robinson D, van Vuuren MMI (1998) Responses of wild plants to nutrient patches in relation to growth rate and life-form. In: Lambers H, Poorter H, van Vuuren MMI (eds) Inherent variation in plant growth. Physiological mechanisms and ecological consequences. Backhuys Publishers, The Netherlands, pp 237–257
Roumet C, Lafont F, Sari M et al (2008) Root traits and taxonomic affiliation of nine herbaceous species grown in glasshouse conditions. Plant Soil 312:69–83
Shaw A, Karlsson C, Möller J (1988) An introduction to the use of flow injection analysis, Tecator AB.
Šmilauer P (1996) Modern approaches to analysis of ecological data. Ph.D thesis, Faculty of Biological Sciences, University of South Bohemia, České Budějovice. Msc.
Šmilauerová M (2001) Plant root response to heterogeneity of soil resources: effects of nutrient patches, am symbiosis, and species composition. Folia Geobot 36:337–351
Šmilauer P, Šmilauerová M (2000) Effect of AM symbiosis exclusion on grassland community composition. Folia Geobot 35:13–25
Šmilauerová M, Šmilauer P (2002) Morphological responses of plant roots to heterogeneity of soil resources. New Phytol 154:703–715
Šmilauerová M, Šmilauer P (2006) Co-occurring graminoid and forb species do not differ in their root morphological response to soil heterogeneity. Folia Geobot 41:121–135
Šmilauerová M, Šmilauer P (2007) What youngsters say about adults: seedling roots reflect clonal traits of adult plants. J Ecol 95:406–413
Symstad AJ, Tilman D (2001) Diversity loss, recruitment limitation, and ecosystem functioning: lessons learned from a removal experiment. Oikos 92:424–435
Taub DR, Goldberg D (1996) Root system topology of plants from habitats differing in soil resource availability. Funct Ecol 10:258–264
Wardle DA, Bonner KI, Barker GM et al (1999) Plant removals in perennial grassland: Vegetation dynamics, decomposers, soil biodiversity, and ecosystem properties. Ecol Monogr 69:535–568
Wijesinghe DK, John EA, Beurskens S et al (2001) Root system size and precision in nutrient foraging: responses to spatial pattern of nutrient supply in six herbaceous species. J Ecol 89:972–983
Wilson GWT, Hartnet DC (1997) Effects of mycorrhizae on plant growth and dynamics in experimental tallgrass prairie microcosms. Am J Bot 84:478–482
Wilson GWT, Hartnet DC (1998) Interspecific variation in plant responses to mycorrhizal colonization in tallgrass prairie. Am J Bot 85:1732–1738
Acknowledgements
We thank Jonathan Titus for important suggestions and language revisions, to anonymous reviewers of an earlier version for their valuable comments, and to Blanka Divišová for her assistance with the field and lab work. This work was funded by a grant from the Czech Ministry of Education, MSM-6007665801, and a grant from the Grant Agency of the Czech Republic, GAČR 206/06/0098.
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Appendix
Appendix
List of species growing in the close patch neighbourhood (in the rim surrounding each patch, with an external diameter 11 cm and projection area of 80 cm2) and their relative frequency (% of all sampled pathes). In addition, Festuca rubra, Alchemilla vulgaris agg., Betonica officinalis, Galium verum, Medicago lupulina and Ranunculus acris were noticed several times in the broader patch neighbourhood (40 × 40 cm squares). The plant species nomenclature follows Kubát et al. (2002)
Graminoids: | Forbs: | ||
Poa angustifolia | 97% | Veronica chamaedrys | 61% |
Alopecurus pratensis | 43% | Achillea millefolium | 29% |
Holcus lanatus | 33% | Plantago lanceolata | 29% |
Avenula pubescens | 22% | Campanula patula | 18% |
Agropyron repens | 12% | Rumex acetosa | 18% |
Luzula campestris | 12% | Carum carvi | 14% |
Festuca pratensis | 6% | Taraxacum sect. Ruderalia | 12% |
Dactylis glomerata | 4% | Centaurea jacea | 8% |
Trisetum flavescens | 4% | Veronica arvensis | 8% |
Cerastium holosteoides subsp. triviale | 6% | ||
Clinopodium vulgare | 6% | ||
Leontodon autumnalis | 6% | ||
Pimpinella major | 6% | ||
Hypericum perforatum | 4% | ||
Leontodon hispidus | 4% |
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Šmilauerová, M., Šmilauer, P. First come, first served: grasses have a head start on forbs with prompt nutrient patch occupation. Plant Soil 328, 327–336 (2010). https://doi.org/10.1007/s11104-009-0112-0
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DOI: https://doi.org/10.1007/s11104-009-0112-0