Contribution of the soil seed bank to the restoration of temperate grasslands by mechanical sward disturbance

The restoration of grasslands is one of the primary targets of nature conservation. An easy tool to stimulate the growth of plant species currently absent from the aboveground vegetation but hidden in the “dark”, is to make use of the soil seed bank. Here, seeds of rare and endangered species may still be present. However, the potential contribution of soil seed banks to effective grasslands restoration still remains unclear, as some but not many valuable species built up a persistent seed bank. To evaluate the potential of the soil seed bank for grassland restoration, we installed an experiment in 73 differently managed grasslands in Germany, where the seed bank was activated by mechanical sward disturbance. We also determined the species richness, the density of viable seeds, and the functional composition of seed banks and monitored the regeneration of the aboveground vegetation over two seasons. Our results show that sward disturbance led to an activation of the soil seed banks, which, however, contributed only little to the revegetation after sward disturbance. In addition, the severe impoverishment of the soil seed bank indicated a restricted potential for the restoration of temperate grasslands. Nevertheless, the activation of the soil seed bank increased not only the richness of arable weeds but also slightly the richness of typical grassland species. We conclude that only in recently improved and strongly species‐impoverished grasslands, sward disturbance alone might be able to slightly increase plant species richness. To achieve a distinct increase in species richness, additional diaspore transfer is needed.

[1]  P. Macek,et al.  Disentangling the interplay of generative and vegetative propagation among different functional groups during gap colonization in meadows , 2017 .

[2]  Anette Reenberg,et al.  Hotspots of land use change in Europe , 2016 .

[3]  M. Fischer,et al.  Enriching plant diversity in grasslands by large-scale experimental sward disturbance and seed addition along gradients of land-use intensity , 2016 .

[4]  E. Meineri,et al.  Seed banks are biodiversity reservoirs: species–area relationships above versus below ground , 2016 .

[5]  A. Otte,et al.  Negative and positive interactions among plants: effects of competitors and litter on seedling emergence and growth of forest and grassland species. , 2015, Plant biology.

[6]  S. Boch,et al.  Influence of experimental soil disturbances on the diversity of plants in agricultural grasslands , 2014 .

[7]  R Core Team,et al.  R: A language and environment for statistical computing. , 2014 .

[8]  K. Rydgren,et al.  Management history affects grassland seed bank build-up , 2013, Plant Ecology.

[9]  P. Macek,et al.  Establishment and spatial associations of recruits in meadow gaps , 2013 .

[10]  M. Hermy,et al.  Consistent seed bank spatial structure across semi‐natural habitats determines plot sampling , 2012 .

[11]  C. Leuschner,et al.  Fifty years of change in Central European grassland vegetation: Large losses in species richness and animal-pollinated plants , 2012 .

[12]  Carsten F. Dormann,et al.  A quantitative index of land-use intensity in grasslands: Integrating mowing, grazing and fertilization , 2012 .

[13]  A. Otte,et al.  Enhancing plant biodiversity in species‐poor grassland through plant material transfer – the impact of sward disturbance , 2012 .

[14]  N. Blüthgen,et al.  Nutrient concentrations and fibre contents of plant community biomass reflect species richness patterns along a broad range of land-use intensities among agricultural grasslands , 2011 .

[15]  Jens Nieschulze,et al.  Implementing large-scale and long-term functional biodiversity research: The Biodiversity Exploratories , 2010 .

[16]  N. Hölzel,et al.  Species introduction in restoration projects-Evaluation of different techniques for the establishment of semi-natural grasslands in Central and Northwestern Europe , 2010 .

[17]  H. Ellenberg Vegetation Mitteleuropas mit den Alpen : in ökologischer ,dynamischer und historischer Sicht , 2010 .

[18]  Wolfgang Schmidt,et al.  The relationship between soil seed bank, above‐ground vegetation and disturbance intensity on old‐field successional permanent plots , 2009 .

[19]  O. Honnay,et al.  Can the seed bank be used for ecological restoration? An overview of seed bank characteristics in European communities , 2008 .

[20]  A. Otte,et al.  Large scale application of diaspore transfer with plant material in restoration practice - Impact of seed and microsite limitation , 2007 .

[21]  A. Otte,et al.  Seed bank diversity in mesic grasslands in relation to vegetation type, management and site conditions , 2007 .

[22]  A. Otte,et al.  Seed bank diversity in mesic grasslands and their relation to vegetation, management and site conditions , 2007 .

[23]  N. Hölzel Seedling recruitment in flood-meadow species: The effects of gaps, litter and vegetation matrix , 2005 .

[24]  Carsten Thies,et al.  REVIEWS AND SYNTHESES Landscape perspectives on agricultural intensification and biodiversity - ecosystem service management , 2005 .

[25]  Robin J. Pakeman,et al.  The role of the seed bank, seed rain and the timing of disturbance in gap regeneration , 2005 .

[26]  A. Escudero,et al.  Regenerative role of seed banks following an intense soil disturbance , 2005 .

[27]  P. A. Stevens,et al.  The restoration and re-creation of species-rich lowland grassland on land formerly managed for intensive agriculture in the UK , 2004 .

[28]  A. Otte,et al.  Assessing soil seed bank persistence in flood-meadows: The search for reliable traits , 2004 .

[29]  A. Otte,et al.  Ecological significance of seed germination characteristics in flood-meadow species , 2004 .

[30]  A. Otte,et al.  Restoration of a species-rich flood meadow by topsoil removal and diaspore transfer with plant material , 2003 .

[31]  B. McCune,et al.  Analysis of Ecological Communities , 2002 .

[32]  J. Grace,et al.  Effects of disturbance on germination and seedling establishment in a coastal prairie grassland: a test of the competitive release hypothesis , 2002 .

[33]  A. Otte,et al.  The impact of flooding regime on the soil seed bank of flood-meadows , 2001 .

[34]  M. Crawley,et al.  Herbivores, seed banks and seedling recruitment in mesic grassland , 1999 .

[35]  J. Bakker,et al.  Constraints in the restoration of ecological diversity in grassland and heathland communities. , 1999, Trends in ecology & evolution.

[36]  J. P. Grime,et al.  Benefits of plant diversity to ecosystems: immediate, filter and founder effects , 1998 .

[37]  P. Poschlod,et al.  Seed size, shape and vertical distribution in the soil: indicators of seed longevity , 1998 .

[38]  Thierry Dutoit,et al.  Restoration and Rehabilitation of Species‐Rich Grassland Ecosystems in France: a Review , 1998 .

[39]  J. Bakker,et al.  Ecological correlates of seed persistence in soil in the north‐west European flora , 1998 .

[40]  J. Bakker,et al.  Soil seed banks in European grasslands: does land use affect regeneration perspectives? , 1997 .

[41]  P. Poschlod,et al.  Seed banks and seed dispersal: Important topics in restoration ecology , 1996 .

[42]  M. Hutchings,et al.  Studies on the feasibility of re-creating chalk grassland vegetation on ex-arable land. I. The potential roles of the seed bank and the seed rain , 1996 .

[43]  J. Silvertown,et al.  An experimental study of the effects of sheep grazing on vegetation change in a species-poor grassland and the role of seedling recruitment into gaps , 1994 .

[44]  Ruprecht Düll,et al.  Zeigerwerte von Pflanzen in Mitteleuropa , 1992 .

[45]  M. Hutchings,et al.  A field investigation of germination from the seed bank of a chalk grassland ley on former arable land , 1988 .