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Rodenticides impact on wildlife
The control of rodent pests is essential in
many environments, indeed it is a legal requirement for land owners and local
authorities. The main weapons in the battle against rats and mice are
anticoagulant rodenticides, which inhibit the vitamin-K cycle, prevent blood
clotting and cause death from internal bleeding. Warfarin, developed in the
1950s, is probably the best known anticoagulant, but second-generation
compounds, such as difenacoum and bromadiolone, are now the most widely used.
Anticoagulants are acutely toxic to most mammals and are highly effective
control agents because of their cumulative effect and low lethal dosage.
Usage of anticoagulants is most common in and around
buildings, and certain active ingredients, such as flocoumafen and brodifacoum,
are only licensed for indoor use. However, farmers and gamekeepers also commonly
use anticoagulants away from farm buildings, to protect feed hoppers and root
crop clamps. When rodenticides are used away from buildings it becomes much
harder to control their impact on non-target species. Other mammals, such as
rabbits, mice and voles are just as likely to ingest the cereal based bait and
these species form a major part of the diet of many predators. Anticoagulants
have long biological half lives, so predators may be especially vulnerable as
residues from each contaminated prey item accumulate in the liver.
The impact of anticoagulants on non-target wildlife is
largely unknown and studies are few and far between, mainly because of high
analytical costs. The latest study, to be published in Environmental
Pollution, comes from Bristol University and the Central Science Laboratory
and is based on the analysis of livers from 40 stoats Mustela erminea and
ten weasels M. nivalis killed by gamekeepers on English shooting estates.
Nine stoats (23%) and three weasels (30%) contained sub-lethal residues of three
anticoagulants: brodifacoum, bromadiolone and coumatetralyl. Perhaps because of
dietary differences between the sexes, the prevalence of residues in female
stoats was significantly higher than in males. As a result of this sex bias,
there is concern that the overall breeding success of stoat and weasel
populations may be reduced. Residue concentrations were generally quite low, but
several livers contained residue concentrations nearing levels (0.1-0.4
mg.kg-1) at which mortalities have been recorded in other trials.
It should be remembered that these animals had been killed by
gamekeepers and had survived exposure until they were trapped. It is hard to say
just how many stoats and weasels receive higher doses and may die as a result of
exposure to anticoagulants. A statutory monitoring programme, the Wildlife
Incident Investigation Scheme, is in place for monitoring anticoagulant and
other sources of pesticide poisoning. The scheme has recorded small, but
increasing, numbers of foxes and badgers dying from exposure to anticoagulants.
However, this programme depends on the public sending in animals found dead in
suspected poisoning incidents. Unfortunately, stoats and weasels are
inconspicuous species, they die out of sight and their bodies are hardly ever
found or sent in. Consequently, there are only one or two records of stoat and
weasel deaths caused by any form of pesticide poisoning.
It is unclear whether exposure has any long term effect on
stoat and weasel populations. Trapping records suggest that both species may be
declining in Britain, and increasing usage of rodenticides is one of several
factors, together with habitat loss and competition with other predators, that
have been implicated in a possible decline. Other predators, such as polecats
and barn owls are also commonly exposed to rodenticides. Polecats are especially
vulnerable because of their tendency to overwinter in farm buildings, where rats
form a substantial part of their diet. In contrast, while barn owls are commonly
exposed to rodenticides, owl populations are probably more affected by habitat
loss and lack of prey than any other factor. The same may apply to stoat and
weasel populations, which are also very sensitive to prey availability.
Projected work at Bristol will further investigate the impact of anticoagulant
exposure on non-target wildlife, with the ultimate aim of minimising the risks
associated with essential rodent control.
Robbie McDonald works at the School of
Biological Sciences, University of Bristol, Woodland Road, Bristol BS8 1UG, UK,
Tel. 44 (0)117 928 9000, Fax 44 (0)117 925 7374, Email: r.a.mcdonald@bristol.ac.uk
[This
article first appeared in Pesticides News No. 41,
September 1998, page 17]
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