Large‐scale restoration of species‐rich dry grasslands on arable land: Environmental filtering drives successful species establishment over a period of 10 years

[1]  N. Hölzel,et al.  Grassland restoration on former arable land: fine‐scale grass accumulation and damaged soil conditions limit species establishment , 2022, Applied Vegetation Science.

[2]  N. Hölzel,et al.  Nitrogen limitation reduces the performance of target plant species in restored meadows , 2021, Restoration Ecology.

[3]  W. Durka,et al.  Populations restored using regional seed are genetically diverse and similar to natural populations in the region , 2021, Journal of Applied Ecology.

[4]  Ryan C. Blackburn,et al.  Grassland restoration characteristics influence phylogenetic and taxonomic structure of plant communities and suggest assembly mechanisms , 2019, Journal of Ecology.

[5]  M. Sevcíková,et al.  Grassland restoration on ex-arable land by transfer of brush-harvested propagules and green hay , 2019, Agriculture, Ecosystems & Environment.

[6]  J. Lepš,et al.  Variation in plant functional traits is best explained by the species identity: Stability of trait‐based species ranking across meadow management regimes , 2019, Functional Ecology.

[7]  Heidi K. Mod,et al.  Disentangling the processes driving plant assemblages in mountain grasslands across spatial scales and environmental gradients , 2018, Journal of Ecology.

[8]  K. Prach,et al.  Mass effects, clonality, and phenology but not seed traits predict species success in colonizing restored grasslands , 2018 .

[9]  H. Bruelheide,et al.  Predicting the establishment success of introduced target species in grassland restoration by functional traits , 2017, Ecology and evolution.

[10]  Tomáš Herben,et al.  CLO-PLA: a database of clonal and bud-bank traits of the Central European flora. , 2017, Ecology.

[11]  M. Hájek,et al.  Long-lasting Imprint of Former Glassworks on Vegetation Pattern in an Extremely Species-rich Grassland: A Battle of Species Pools on Mesic Soils , 2017, Ecosystems.

[12]  H. Bruelheide,et al.  Functional community ecology meets restoration ecology: Assessing the restoration success of alluvial floodplain meadows with functional traits , 2016 .

[13]  O. Tackenberg,et al.  Herbs are different: clonal and bud bank traits can matter more than leaf-height-seed traits. , 2016, The New phytologist.

[14]  F. Bello,et al.  Fine-scale coexistence patterns along a productivity gradient in wet meadows: shifts from trait convergence to divergence , 2016 .

[15]  T. Fukami Historical Contingency in Community Assembly: Integrating Niches, Species Pools, and Priority Effects , 2015 .

[16]  K. Prach,et al.  Spontaneous colonization of restored dry grasslands by target species: restoration proceeds beyond sowing regional seed mixtures , 2015 .

[17]  K. Prach,et al.  Landscape context in colonization of restored dry grasslands by target species , 2015 .

[18]  Thierry Dutoit,et al.  Can ecological engineering restore Mediterranean rangeland after intensive cultivation? A large-scale experiment in southern France , 2014 .

[19]  R. Callaway,et al.  A functional comparative approach to facilitation and its context dependence , 2013 .

[20]  Sarah Cunze,et al.  D3: The Dispersal and Diaspore Database – Baseline data and statistics on seed dispersal , 2013 .

[21]  Karel Prach,et al.  Large‐Scale Restoration of Dry Grasslands on Ex‐Arable Land Using a Regional Seed Mixture: Establishment of Target Species , 2013 .

[22]  M. Pärtel,et al.  Plant species richness: the world records , 2012 .

[23]  D. Wardle,et al.  Changes in coexistence mechanisms along a long‐term soil chronosequence revealed by functional trait diversity , 2012 .

[24]  M. Pärtel,et al.  Ecological assembly rules in plant communities—approaches, patterns and prospects , 2012, Biological reviews of the Cambridge Philosophical Society.

[25]  Balázs Deák,et al.  Lucerne‐dominated fields recover native grass diversity without intensive management actions , 2011 .

[26]  Sara A. O. Cousins,et al.  Dispersal and establishment limitation reduces the potential for successful restoration of semi‐natural grassland communities on former arable fields , 2009 .

[27]  Martin Hermy,et al.  The LEDA Traitbase: a database of life‐history traits of the Northwest European flora , 2008 .

[28]  R. Marrs,et al.  Do restored calcareous grasslands on former arable fields resemble ancient targets? The effect of time, methods and environment on outcomes , 2008 .

[29]  K. Kiehl,et al.  Establishment and persistence of target species in newly created calcareous grasslands on former arable fields , 2007, Plant Ecology.

[30]  K. Walker,et al.  Long‐term enhancement of agricultural production by restoration of biodiversity , 2006 .

[31]  J. P. Grime,et al.  Trait convergence and trait divergence in herbaceous plant communities: Mechanisms and consequences , 2006 .

[32]  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 .

[33]  Peter Rothery,et al.  Plant traits as predictors of performance in ecological restoration , 2003 .

[34]  Mark Westoby,et al.  A leaf-height-seed (LHS) plant ecology strategy scheme , 1998, Plant and Soil.

[35]  J. Doležal,et al.  Restoring species‐rich meadow by means of turf transplantation: long‐term colonization of ex‐arable land , 2017 .

[36]  K. Prach,et al.  Restoration of grasslands on ex-arable land using regional and commercial seed mixtures and spontaneous succession: Successional trajectories and changes in species richness , 2014 .