Do Trapping Interventions Effectively Reduce or Eradicate Populations of the American Mink (Mustela vison)? (systematic review)
American mink, Mustela vison, are native to North America. They were brought to Great Britain for fur farming in 1929. Deliberate releases and inevitable escapes have resulted in feral population establishment in Britain. As M. vison is considered a threat to native fauna population control is an option. Commonly used techniques are trapping, shooting, and hunting. Assessment of the effectiveness of these techniques will inform management planning where there are ecological and/or economic impacts arising from presence of M. vison populations.
To assess if management interventions effectively reduce or eradicate population numbers of Mustela vison?
- Is heterogeneity within results introduced through ecological variation within the studies?
- Are isolated M. vison populations reduced more effectively?
- Is effectiveness of an intervention altered by seasonality?
Relevant studies were located through the computerised searches of English Nature’s ‘Wildlink database’, JSTOR, ISI Web of Knowledge (comprising BIOSIS previews: 1969 to 2004, CAB abstracts: 1973 to 2004, ISI current contents: 1997 to 2004, ISI proceedings: 1990 to 2004, ISI Web of Science: 1975 to 2004), Scirus: 1920 to present, Copac: 1100 to present, ScienceDirect, Index to Theses online: 1973 to 2004, Agricola, Scopus: 1966 to 2004 and Digital Dissertations. Web searches were made using www.alltheweb.com (PDF, and word doc. search), www.google.co.uk, and direct interrogation of the following websites: DEFRA, Scottish Natural Heritage, The Wildlife Conservation Research Unit (WildCRU) at Oxford University, The Royal Society for the Protection of Birds, The National Trust, British Wildlife, The Mammal Society, Mammals Trust, and The British Trust for Ornithology.
A secondary search was made of bibliographies of all articles accepted at full text.
American Mink, Mustela vison, populations.
After initial scoping of the literature, the main intervention under consideration was the practice of trapping M. vison for population control. Studies over all time scales and geographical locations were included.
Any articles that did not include a control site/comparator were rejected in the first instance. Lower quality evidence was later incorporated into the review due to the lack of comparators in the studies located.
Any study that reported on the outcome of trapping for the control of M. vison was accepted. Ideally, studies that reported on change in abundance were most relevant. It was a requirement that if abundance was the measurement, the population size before and after trapping was assessed independently of the number of M. vison trapped.
Data collection and analysis
Article inclusion/exclusion assessments were performed by the primary reviewer with a subset assessed by a second reviewer for verification of repeatability within the methodology; any disagreements were resolved by discussion. Data extraction and study quality were performed by the primary reviewer with the use of pre-designed assessment forms, and then entered into a spreadsheet. Due to the lack of available data, statistical analysis could not be performed. Results are thus presented qualitatively in a summary table.
Available qualitative evidence from 7 studies demonstrates that M. vison populations decrease over the time of observation. Due to the lack of control areas within the experimental designs, observed decreases cannot be attributed to any single factor, i.e. traps, as there is no formal investigation into other intrinsic and extrinsic variables that could also be acting upon the M. vison population.
No firm deductions can be made from current studies because of limitations of study design and lack of controls for comparison. Future studies should incorporate a more robust experimental design, including a population estimation before and after the intervention occurs and a control population that is not subject to the intervention.
Introduced American Mink (Mustela vison) are a cause for concern to many UK conservation organisations, game keepers and farmers, as an invasive species. M. vison were first introduced into the U.K in 1929 on fur farms for the fur trade. Escapes led to breeding in the wild, first known to occur in 1956 (Usher, 1986). Further releases both accidental and deliberate have led to feral populations of Mustela vison becoming widespread across Britain and they are also present in Ireland, Finland, Iceland and France (Chanin, 1981).
M. vison are generalist predators, hunting both on land and in water, preying on rabbits, birds, eggs, and fish. They have no natural predators in the UK, and are associated with a wide range of aquatic and semi-aquatic habitats (Halliwell & Macdonald, 1995). In the 1960s occurrences in the UK were rare, but by 1980 there had been a ten-fold increase in numbers, showing their adaptability and dispersal capacity (Tapper, 1980).
Management interventions to control M. vison include hunting with dogs, shooting and lethal or non-lethal trapping (Defra, UK, Department for Environment, Food and Rural Affairs). There are no UK approved fumigants or poisons for M. vison, but forms of immuno-contraception are being developed (Macdonald, 2003). With each intervention there is the possibility of killing non target species (Short & Reynolds, 2000), and further disturbing the area, therefore non-lethal trapping is the most commonly used intervention, as non-target species can be released if caught.
A systematic review is proposed to determine the effectiveness of control methods to reduce the population numbers of M. vison, and any possible deleterious effects of control techniques. Depending on the quality and quantity of studies available on each intervention, the review may focus on one or more of the interventions listed in Table 1.