Rabbit (Oryctolagus cuniculus L.) impacts on vegetation and soils, and implications for management of wooded rangelands

Summary Rabbit warrens are a distinctive landscape feature in the semi-arid woodlands of eastern Australia. We examined the surface morphology and vegetation composition of ten rabbit warrens in central-western NSW in order to assess their roles as a harbor for weedy plants. In general, mounds were characterised by a degraded soil surface dominated by bare soil and coarse gravel, whilst adjacent non-mound (control) surfaces were characterised by an extensive cover of cryptogams (lichens and mosses). Mounds supported significantly more exotic plants than non-mounds, and there was a clear separation between the two microsites in terms of the cover-abundances of vascular plants. Mound microsites contained significantly more tall (>50 cm) species, and species with burrs compared with non-mound microsites. Germination studies indicated enhanced germination of two common, weedy, mound species ( Marrubium vulgare and Brassica tournefortii ) on the eroded mound surface, and greater germination of the perennial grass Austrodanthonia caespitosa on the cryptogam-dominated non-mound surface. The work suggests that the higher cover-abundance of weedy species is a result of alterations to the soil surface caused by rabbit disturbances, and that destruction of the warren complex, in order to prevent re-invasion and hence re-working of the mound, is required to enable native perennials to colonise. Kaninchenbauten sind ein auffalliges Landschaftsmerkmal des semi-ariden Waldlandes Ostaustraliens. Wir untersuchten die Oberflachenmorphologie und Vegetationszusammensetzung von 10 Kaninchenbauten im zentralen Westen von New South Wales, um ihre Rolle als bevorzugte Standorte fur Unkrautgewachse zu beurteilen. Im Allgemeinen waren die Bautenhugel durch eine degradierte Bodendecke und groben Kies gekennzeichnet, wahrend angrenzende, von Bautenhugeln freie, (Kontroll-) Flachen durch ausgedehnten Kryptogamenbewuchs (Flechten und Moose) charakterisiert waren. Bautenhugel wiesen deutlich mehr exotische Pflanzen als die hugelfreien Flachen auf, und es zeigte sich ein ausgepragter Unterschied zwischen beiden Mikrostandorten bezuglich des Flachenbewuchses durch Gefaspflanzen. Mikrostandorte mit Bautenhugeln wiesen im Vergleich zu denen ohne Bauten deutlich mehr hochwuchsige (>50 cm) Arten und Klettenpflanzen auf. Keimungsstudien zeigten verbessertes Keimen zweier weitverbreiteter, auf Bautenhugeln wachsender Unkrautarten ( Marrubium vulgare und Brassica tournefortii ) auf der erodierten Oberflache der Bauten und verstarktes Keimen des perennierenden Grases Austrodanthonia caespitosa auf der von Kryptogamen dominierten erdhugelfreien Flache. Die Studie deutet darauf hin, dass der dichtere Flachenbewuchs mit Unkrautpflanzen von durch Kaninchenaktivitat hervorgerufenen Veranderungen der Bodendecke verursacht wird. Dies erfordert die Zerstorung der Bautenkomplexe zur Verhinderung einer Neubesiedlung und damit Reaktivierung der Erdhugel durch Kaninchen, um eine Kolonisation durch einheimische perennierde Pflanzen zu ermoglichen.

[1]  D. Eldridge,et al.  The impact of warrens of the European rabbit (Oryctolagus cuniculus L.) on soil and ecological processes in a semi-arid Australian woodland , 2001 .

[2]  Sandra Lavorel,et al.  Disturbance response in vegetation – towards a global perspective on functional traits , 1999 .

[3]  W. Whitford,et al.  Biopedturbation by mammals in deserts: a review , 1999 .

[4]  A. Kinlaw,et al.  A review of burrowing by semi-fossorial vertebrates in arid environments , 1999 .

[5]  W. Whitford Contribution of pits dug by goannas (Varanus gouldii) to the dynamics of banded mulga landscapes in eastern Australia , 1998 .

[6]  Y. Gutterman Ibex diggings in the Negev Desert highlands of Israel as microhabitats for annual plants. Soil salinity, location and digging depth affecting variety and density of plant species☆ , 1997 .

[7]  E. Zaady,et al.  The germination of mucilaginous seeds of t Plantago coronopus, Reboudia pinnata, and t Carrichtera annua on cyanobacterial soil crust from the Negev Desert , 1997, Plant and Soil.

[8]  S. Milton,et al.  Effects of small‐scale animal disturbances on plant assemblages of set‐aside land in Central Germany , 1997 .

[9]  M. Shachak,et al.  Patchiness and disturbance: plant community responses to porcupine diggings in the central Negev , 1995 .

[10]  D. Butler Zoogeomorphology: Animals as Geomorphic Agents , 1995 .

[11]  S. Giannoni,et al.  Vegetation differences caused by pine vole mound building in subalpine plant communities in the Spanish Pyrenees , 1995, Vegetatio.

[12]  C. King,et al.  The European rabbit : the history and biology of a successful colonizer , 1995 .

[13]  S. Lavorel,et al.  Plant life-history attributes: their relationship to disturbance response in herbaceous vegetation. , 1995 .

[14]  D. Eldridge,et al.  Microbiotic soil crusts: a review of their roles in soil and ecological processes in the rangelands of Australia , 1994 .

[15]  P. Ryan,et al.  The role of disturbance in the establishment of indigenous and alien plants at Inaccessible and Nightingale Islands in the South Atlantic Ocean , 1994, Vegetatio.

[16]  J. Johansen CRYPTOGAMIC CRUSTS OF SEMIARID AND ARID LANDS OF NORTH AMERICA , 1993 .

[17]  K. R. Clarke,et al.  Non‐parametric multivariate analyses of changes in community structure , 1993 .

[18]  G. Harden Flora of New South Wales , 1992 .

[19]  I. Sneddon Latrine Use by the European Rabbit (Oryctolagus cuniculus) , 1991 .

[20]  Y. Gutterman,et al.  Porcupine diggings as a unique ecological system in a desert environment , 1990, Oecologia.

[21]  M. Gutman,et al.  Responses of mediterranean grassland plants to grazing and protection. , 1989 .

[22]  A. E. Ainsley,et al.  Genstat 5 Reference Manual , 1987 .

[23]  H. T. Clifford,et al.  THE INFLUENCE OF DIASPORE MORPHOLOGY AND SOIL-SURFACE PROPERTIES ON THE DISTRIBUTION OF GRASSES , 1987 .

[24]  R. Reader,et al.  Topographic Variation in the Abundance of Hieracium Floribundum: Relative Importance of Differential Seed Dispersal, Seedling Establishment, Plant Survival and Reproduction , 1986 .

[25]  B. Foran The impact of rabbits and cattle on an arid calcareous shrubby grassland in central Australia , 1986, Vegetatio.

[26]  R. Lange,et al.  Rabbits and the failure of regeneration in Australian arid zone Acacia , 1983 .

[27]  P. Grubb THE MAINTENANCE OF SPECIES‐RICHNESS IN PLANT COMMUNITIES: THE IMPORTANCE OF THE REGENERATION NICHE , 1977 .

[28]  R. L. Caskey,et al.  An Attempt at Rabbit Control by Warren Ripping in Semi-Arid Western New South Wales , 1976 .

[29]  K. R. Clarke,et al.  Change in marine communities : an approach to statistical analysis and interpretation , 2001 .

[30]  J. Morgan,et al.  Vegetation Changes after 10 Years of Grazing Exclusion and Intermittent Burning in a Themeda triandra (Poaceae) Grassland Reserve in South-eastern Australia , 1999 .

[31]  P. Walker,et al.  Natural Regeneration of Ground Storey Vegetation in a Semi-Arid Woodland Following Mechanical Disturbance and Burning. 1. Ground Cover Levels and Composition. , 1995 .

[32]  M. Braysher,et al.  Managing vertebrate pests: rabbits. , 1995 .

[33]  R. Gittins,et al.  Natural Regeneration of Ground Storey Vegetation in a Semi-Arid Woodland Following Mechanical Disturbance and Burning. 2. Response of Individual Species. , 1995 .

[34]  R. Tremont Life-History Attributes of Plants in Grazed and Ungrazed Grasslands on the Northern Tablelands of New South Wales , 1994 .

[35]  C. Gaillard The environmental impact of burrowing animals and animal burrows , 1993 .

[36]  G. Mutze Long-term effects of warren ripping for rabbit control in semi-arid South Australia. , 1991 .

[37]  A. Meadows,et al.  The Environmental impact of burrowing animals and animal burrows : the proceedings of a symposium held at the Zoological Society of London on 3rd and 4th May 1990 , 1991 .

[38]  A. Slee,et al.  Effects of Rabbit and Kangaroo Grazing on Two Semi-Arid Grassland Communities in Central-Western New South Wales , 1989 .

[39]  G. F. Griffin,et al.  Range assessment and monitoring in arid lands: the derivation of functional group to simplify vegetation data , 1988 .

[40]  K. Harper,et al.  A role for nonvascular plants in management of arid and semiarid rangelands , 1988 .

[41]  I. Parer,et al.  The History and Structure of a Large Warren of the Rabbit, Oryctolagus-Cuniculus, at Canberra, Act , 1987 .

[42]  L. Hunt,et al.  Practical and economic aspects of rabbit control in hilly semiarid South Australia , 1987 .

[43]  I. Parer,et al.  Recolonisation by rabbits (Oryctolagus cuniculus) after warren destruction in Western New South Wales. , 1986 .

[44]  D. Wood Effectiveness and economics of destruction of rabbit warrens in sandy soils by ripping. , 1985 .

[45]  J. Eveleigh,et al.  Observations on the effectiveness of warren destruction as a method of rabbit control in a semi-arid environment. , 1976 .

[46]  M. Crisp,et al.  Age Structure, Distribution and Survival under Grazing of the Arid-Zone Shrub Acacia burkittii , 1976 .

[47]  Keith H. Northcote,et al.  A factual key for the recognition of Australian soils , 1971 .

[48]  F. Ratcliffe The Rabbit in Australia , 1959 .

[49]  J. G. The Rabbit in Australia , 1936, Nature.