Feral European Rabbit (Oryctolagus Cuniculus)
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European Rabbits in Chile: the History of a Biological Invasion
Historia. vol.4 no.se Santiago 2008 EUROPEAN RABBITS IN CHILE: THE HISTORY OF A BIOLOGICAL INVASION * ** *** PABLO C AMUS SERGIO C ASTRO FABIÁN J AKSIC * Centro de Estudios Avanzados en Ecología y Biodiversidad (CASEB) . email: [email protected] ** Departamento de Biología, Facultad de Química y Biología; Universidad de Santiago de Chile. Centro de Estudios Avanzados en Ecología y Biodiversidad (CASEB). email: [email protected] *** Departamento de Ecología, Pontificia Universidad Católica de Chile. Centro de Estudios Avanzados en Ecología y Biodiversidad (CASEB). email: [email protected] ABSTRACT This work analyses the relationship between human beings and their environment taking into consideration the adjustment and eventual invasion of rabbits in Chile. It argues that in the long run, human actions have unsuspected effects upon the environment. In fact rabbits were seen initially as an opportunity for economic development because of the exploitation of their meat and skin. Later, rabbits became a plague in different areas of Central Chile, Tierra del Fuego and Juan Fernández islands, which was difficult to control. Over the years rabbits became unwelcome guests in Chile. Key words: Environmental History, biological invasions, European rabbit, ecology and environment. RESUMEN Este trabajo analiza las relaciones entre los seres humanos y su ambiente, a partir de la historia de la aclimatación y posterior invasión de conejos en Chile, constatando que, en el largo plazo, las acciones humanas tienen efectos e impactos insospechados sobre el medio natural. En efecto, si bien inicialmente los conejos fueron vistos como una oportunidad de desarrollo económico a partir del aprovechamiento de su piel y su carne, pronto esta especie se convirtió en una plaga difícil de controlar en diversas regiones del país, como Chile central, Tierra del Fuego e islas Juan Fernández. -
The Wild Rabbit: Plague, Polices and Pestilence in England and Wales, 1931–1955
The wild rabbit: plague, polices and pestilence in England and Wales, 1931–1955 by John Martin Abstract Since the eighteenth century the rabbit has occupied an ambivalent position in the countryside. Not only were they of sporting value but they were also valued for their meat and pelt. Attitudes to the rabbit altered though over the first half of the century, and this paper traces their redefinition as vermin. By the 1930s, it was appreciated that wild rabbits were Britain’s most serious vertebrate pest of cereal crops and grassland and that their numbers were having a significant effect on agricultural output. Government took steps to destroy rabbits from 1938 and launched campaigns against them during wartime, when rabbit was once again a form of meat. Thereafter government attitudes to the rabbit hardened, but it was not until the mid-1950s that pestilence in the form of a deadly virus, myxomatosis, precipitated an unprecedented decline in their population. The unprecedented decline in the European rabbit Oryctolagus( cuniculus) in the mid- twentieth century is one of the most remarkable ecological changes to have taken place in Britain. Following the introduction of myxomatosis into Britain in September 1953 at Bough Beech near Edenbridge in Kent, mortality rates in excess of 99.9 per cent were recorded in a number of affected areas.1 Indeed, in December 1954, the highly respected naturalist Robin Lockley speculated that 1955 would constitute ‘zero hour for the rabbit’, with numbers being lower by the end of the year than at any time since the eleventh century.2 In spite of the rapid increases in output and productivity which British agriculture experienced in the post-myxomatosis era, the importance of the disease as a causal factor in raising agricultural output has been largely ignored by agricultural historians.3 The academic neglect of the rabbit as a factor influencing productivity is even more apparent in respect of the pre-myxomatosis era, particularly the period before the Second World War. -
Impacts of Rabbits in Wetlands
Impacts of Rabbits in Wetlands Fact Sheet 1 Victorian distribution and habitats Diet Wild Rabbits occur throughout Victoria in a range of Rabbits are highly resilient to harsh environmental habitats from subalpine to stony deserts and subtropical conditions, including extended periods of poor nutrition. grasslands to wet coastal plains. They are particularly As herbivores, Rabbits eat a wide variety of plants, abundant in Mediterranean-type climates, but not including: green grass, herbs, young seedlings, usually in dense forests, black soil plains or above 1600 pastures, roots and crops. Rabbits can often graze m elevation1. plants to ground level and they eat up to one-third of their body weight per day. Even at moderate densities Soils are a major factor influencing local and regional (e.g. five Rabbits per ha) they can remove half the distribution. Rabbits prefer well-drained deep soils and pasture produced in an average year in Australia’s arid- warrens are more prevalent on lower slopes and flats zone5. Rabbits gain moisture from their food and do not which are usually areas that are highly productive in need access to water, except in semi-arid areas. They terms of pasture2. Rabbit densities are greatest in non- pass hard droppings, usually from eating plant stalks, or arable rough country including creeks and river banks, they pass soft droppings which are often re-eaten to erosion gullies, rocky outcrops and forest-grassland maximize nutrient uptake. interfaces3. Wetlands are particularly well suited for Rabbits due to suitable soils for warren construction. Many significant Victorian wetlands and adjacent habitats have been impacted by Rabbits, including the Kerang Lakes, Winton wetlands, Hattah-Kulkyne Lakes, Phillip Island wetlands, Cheetham wetlands and urban wetlands in the Yarra basin. -
Introduction to Risk Assessments for Methods Used in Wildlife Damage Management
Human Health and Ecological Risk Assessment for the Use of Wildlife Damage Management Methods by USDA-APHIS-Wildlife Services Chapter I Introduction to Risk Assessments for Methods Used in Wildlife Damage Management MAY 2017 Introduction to Risk Assessments for Methods Used in Wildlife Damage Management EXECUTIVE SUMMARY The USDA-APHIS-Wildlife Services (WS) Program completed Risk Assessments for methods used in wildlife damage management in 1992 (USDA 1997). While those Risk Assessments are still valid, for the most part, the WS Program has expanded programs into different areas of wildlife management and wildlife damage management (WDM) such as work on airports, with feral swine and management of other invasive species, disease surveillance and control. Inherently, these programs have expanded the methods being used. Additionally, research has improved the effectiveness and selectiveness of methods being used and made new tools available. Thus, new methods and strategies will be analyzed in these risk assessments to cover the latest methods being used. The risk assements are being completed in Chapters and will be made available on a website, which can be regularly updated. Similar methods are combined into single risk assessments for efficiency; for example Chapter IV contains all foothold traps being used including standard foothold traps, pole traps, and foot cuffs. The Introduction to Risk Assessments is Chapter I and was completed to give an overall summary of the national WS Program. The methods being used and risks to target and nontarget species, people, pets, and the environment, and the issue of humanenss are discussed in this Chapter. From FY11 to FY15, WS had work tasks associated with 53 different methods being used. -
Raising Hares
Raising Hares Photographs by Andy Rouse/naturepl.com The agility and grace of the European hare (Lepus europaeus) is a familiar sight in the British countryside, and their spirited springtime antics mark the end of winter in the minds of many. Despite their similarities in appearance to the European rabbit, the life history and behaviour of the European hare differs significantly from that of their smaller cousins. We join photographer Andy Rouse as he captures the story of the hare and discovers the true meaning of ‘Mad as a March hare’. Brown hares are widespread throughout central and west- ern Europe, including most of the UK, where they were thought to be introduced by the Romans. “I’ve been passionate about watching and photographing hares for years”, says Rouse. “They are always a challenge because they’re so wary and elusive. Getting decent images usually requires hours of lying quietly in a ditch! So I was de- lighted when I found a unique site in Southern England that has a thriving population of hares”. “Hares are wonderful to work with”, says Rouse. “Concentrating on one population opens up much greater opportunities than photo- graphing at a multitude of sites. It has been such a pleasure getting to know individuals on this project”. “I took these images at a former WWI airfield”, says Rouse. “It is the oldest in the world and still in use, with grass runways. The alternation of cut and long grass provides ideal habitat for hares, which are traditionally found along field margins”. “The hares here are used to people so it’s easier to observe them and predict their behaviour”, says Rouse. -
Invasive European Rabbits in Australia
INVASIVE EUROPEAN RABBITS IN AUSTRALIA Michael Evans OBJECTIVES AND GOALS • Examine why rabbits are so successful in Australia • Understand variability in rabbit survival amongst age classes and climate conditions • Were founder effects experienced? • Examine potential control methods 2 BACKGROUND AND INTRODUCTION • Oryctolagus cuniculus • Originally from Iberian Peninsula. Now found nearly worldwide • Introduced from England in 1788 • Released into wild in 1859 • Large growth rate and dispersal led to roughly 600 million rabbits within 100 years • Outcompeted native bilbies which are now endangered. • Cause extensive crop damage and soil erosion. Responsible for extensive plant extinction 3 Stodart & Parer 1988 REPRODUCTION • Mostly monogamous. Dominant males are polygynous • First reproduction at 4 months • Litter size of 2-12 rabbits, although 9+ is rare • Potential for 4-7 litters in one year. Average gestation time is one month • One pair can produce 30-40 offspring in one year • Lifespan of roughly 9 years • Recover quickly from droughts 4 POPULATION CONTROL METHODS • Limited predation through foxes and eagles • Rabbit-proof fence construction in 1901. Currently three in western Australia. • Hunting for sport and food • Myxoma virus in 1950 led to myxomatosis. Led to decline but gradual increase due to resistance. • Less virulent strain currently • Rabbit haemorrhagic disease spreads beginning in 1995. Referred to as RHD. • Mortality of roughly 90% • Transferred orally, nasally, conjunctively • May be transferred to their predators 5 • Thrive in years with less than 1000mm of rain • Graph B is for populations with myxomatosis while Graph C is for RHD. • RHD causes lower survival in 4-12 months and over 12 months. 6 Tablado et al. -
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And Weasels, 1883–1920 163
DOI:King: 10.20417/nzjecol.41.29 Spread of stoats and weasels, 1883–1920 163 REVIEW Liberation and spread of stoats (Mustela erminea) and weasels (M. nivalis) in New Zealand, 1883–1920 Carolyn M. King Environmental Research Institute, School of Science, University of Waikato, Hamilton 3240, New Zealand (Email: [email protected]) Published online: 29 May 2017 Abstract: This paper reviews the timing and spread of weasels and stoats across the South and North Islands of New Zealand during the late nineteenth century, entirely from historical records. The flavour of the debates and the assumptions that led to the commissioning of private and government shipments of these animals are best appreciated from the original documents. I describe the sites of the early deliberate releases in Otago, Canterbury, Marlborough, and Wairarapa, and list contemporary observations of the subsequent dispersal of the released animals to named locations in Southland, Westland, Wellington, Hawke’s Bay, Auckland and Northland. Originally, weasels were landed in far greater numbers than stoats (2622 weasels and 963 stoats listed in shipment records) and, while at first they were very abundant, they are now much less abundant than stoats. Two non-exclusive hypotheses could explain this historic change: (1) depletion of supplies of their preferred small prey including birds, mice, roosting bats, lizards, frogs and invertebrates, and (2) competition with stoats. Contemporary historic written observations on the first impacts of the arrivals of weasels and stoats on the native fauna offer graphic illustrations of what has been lost, but usually failed to consider the previous impacts of the abundant rats (Rattus exulans since the late 13th century, and R. -
The High Abundance of Wild Ungulates in a Mediterranean Region: Is This Compatible with the European Rabbit? Author(S): Antonio J
The high abundance of wild ungulates in a Mediterranean region: is this compatible with the European rabbit? Author(s): Antonio J. Carpio, José Guerrero-Casado, Leire Ruiz-Aizpurua, Joaquín Vicente and Francisco S. Tortosa Source: Wildlife Biology, 20(3):161-166. 2014. Published By: Nordic Board for Wildlife Research DOI: http://dx.doi.org/10.2981/wlb.13113 URL: http://www.bioone.org/doi/full/10.2981/wlb.13113 BioOne (www.bioone.org) is a nonprofit, online aggregation of core research in the biological, ecological, and environmental sciences. BioOne provides a sustainable online platform for over 170 journals and books published by nonprofit societies, associations, museums, institutions, and presses. Your use of this PDF, the BioOne Web site, and all posted and associated content indicates your acceptance of BioOne’s Terms of Use, available at www.bioone.org/page/terms_of_use. Usage of BioOne content is strictly limited to personal, educational, and non-commercial use. Commercial inquiries or rights and permissions requests should be directed to the individual publisher as copyright holder. BioOne sees sustainable scholarly publishing as an inherently collaborative enterprise connecting authors, nonprofit publishers, academic institutions, research libraries, and research funders in the common goal of maximizing access to critical research. Wildlife Biology 20: 161–166, 2014 doi: 10.2981/wlb.13113 © 2014 The Authors. This is an Open Access article Subject Editor: Klaus Hackländer. Accepted 4 December 2014 The high abundance of wild ungulates in a Mediterranean region: is this compatible with the European rabbit? Antonio J. Carpio, José Guerrero-Casado, Leire Ruiz-Aizpurua, Joaquín Vicente and Francisco S. -
Evaluating How Swedish Hunters Determine Which Species Belong in Nature
European Journal of Wildlife Research (2020) 66: 77 https://doi.org/10.1007/s10344-020-01418-6 ORIGINAL ARTICLE Evaluating how Swedish hunters determine which species belong in nature M. Nils Peterson1 & Alyssa Chen1 & Erica von Essen1 & Hans Peter Hansen1 Received: 30 January 2020 /Revised: 17 August 2020 /Accepted: 24 August 2020 / Published online: 27 August 2020 # Springer-Verlag GmbH Germany, part of Springer Nature 2020 Abstract Understanding whether people view non-native species as belonging in a place will help guide important conservation efforts ranging from eradications of exotics to re-introduction of extirpated species. In this manuscript we describe the degree to which Swedish hunters perceive key wildlife species as belonging in Swedish nature. We surveyed 2014 Swedish hunters randomly selected from a database of all registered hunters with a 47.5% response rate. We measured hunters’ perceptions of the belonging of 10 key species on the Swedish landscape, compared them with confidence intervals for proportions, and predicted them using regression models. Construct validity was assessed through pretesting and focus groups. Our results suggest Swedish hunters consider species introduced wholly by humans as less likely to belong in Sweden compared with species that evolved in situ, species with negative socio-economic impact as less likely to belong in Sweden compared with species with no impact or positive economic impacts, and species with wide distributions to be seen as more likely to belong in Sweden compared with those with narrow distributions. Perceptions of wolves, fallow deer, and European rabbits differed from these broad trends potentially due to unique cultural constructions of belonging for the species and the duration since anthropogenic introductions for the latter species. -
Policy on Rabbits in South Australia
POLICY ON RABBITS IN SOUTH AUSTRALIA Adopted by the Minister for Environment and Conservation 28 September 2005 Policy Objectives Primary producers, the environment and the public protected from damage and hazards caused by rabbits. Minimal impact on wild rabbit management programs as a result of the keeping and sale of domestic breeds of rabbits. Rabbits will not establish on offshore islands. Rabbit Research will be maintained to address immediate problems and to pursue longer term options by identifying new technologies and any potential risks to control techniques. Implementation Management of wild rabbits Landholders have a responsibility to destroy all wild rabbits (Oryctolagus cuniculus) on offshore islands (except Wardang Island) and manage wild rabbits in all other areas of the State (see policy explanation and interpretation – part 4). Keeping and sale of wild rabbits. The keeping and sale of wild rabbits is prohibited in all areas. Keeping and sale of domestic breeds of rabbits in especially sensitive areas. The keeping and sale of domestic breeds of rabbits is prohibited on all offshore islands with the exception of Wardang Island where wild rabbits are already established. Keeping and sale of domestic breeds of rabbits for whole of the State (excluding offshore islands other than Wardang Island) q:\natural resources\biosecurity\apcg\policy\pest animal policies\rabbits\rabbit policy current\rabbitpolicy 2 2005.doc 6 August 2010 The deliberate release of domestic breeds of rabbits into the wild is prohibited. The keeping and sale of domestic breeds of rabbits is permitted subject to statutory requirements under other legislation (eg Prevention of Cruelty to Animals Act 1985 and subordinate legislation, and planning regulations under the Local Government Act 1934 – see policy explanation and interpretation – part 4). -
European Wild Rabbit (Oryctolagus Cuniculus)
pean wild ro ra u b E b he feral European rabbit is one of the most i T widely distributed and abundant mammals t in Australia. It causes severe damage to the natural environment and to agriculture. Feral rabbit control (Oryctolagus cuniculus) is complicated because of welfare and harvesting issues, and because both native and introduced predators feed on feral rabbits in many parts of Australia. A combination of traditional control techniques and biological control holds the best promise for reducing feral rabbit populations Ecology and minimising the damage they cause. Feral rabbits occur in many different habitats across Australia, ranging from deserts to coastal plains — History wherever there is suitable soil for digging warrens. Domesticated rabbits arrived in Australia with the They are scarce in areas with clay soils and abundant First Fleet. In Tasmania, feral rabbits were abundant where soils are deep and sandy, such as in the north- on some estates as early as 1827. On the mainland, east of South Australia. In arid areas, feral rabbits Thomas Austin freed about a dozen on his property need access to water, but elsewhere they can often near Geelong, Victoria, in 1859. From there they obtain enough moisture from their food. spread, reaching the Queensland – New South Wales Feral rabbits are night-time grazers, preferring green border by 1886 and covering most of their present grass and herbs. They also dig below grasses to reach range by 1910. This was despite the Western Australian roots and seeds. In the breeding season, feral rabbits Government’s 1700-km rabbit-proof fence, built form territorial groups made up of one to three males between 1901 and 1907.