Select Committee on Environment, Food and Rural Affairs Written Evidence


Memorandum submitted by Farmers' Union of Wales (BTB 06)

1.  EXECUTIVE SUMMARY

  Due to the lack of significant geographical boundaries along large lengths of the England-Wales border, and the trade that takes place between the two countries, the prevalence of TB in England has a significant effect on the situation in Wales, as do policies instigated in England. Any policies adopted by DEFRA in England are therefore of direct consequence for Welsh farmers and the FUW, and often lay the foundation for policies later adopted in Wales.

  The FUW firmly believes that bovine TB cannot be controlled unless badger removal occurs in and around areas where TB is a problem. Such action can be justified on the following grounds:

  1.1  TB annually results in the deaths of tens of thousands of cattle, badgers, and deer. In the case of cattle, the welfare implications are generally negligible due to early diagnosis and slaughter, but the economic and social effects are dire. In the case of deer and badgers, the deaths caused by the advanced stages of TB are agonising. The current epidemic must therefore be controlled on welfare, social, and economic grounds; to allow TB to continue to spread would only add to the human and animal suffering that TB causes.

  1.2  Scientific evidence from around the globe, not least from the recent Irish Four Area and English Randomised Badger Culling trials, indicates that the removal of wildlife reservoirs is an essential part of TB control.

  1.3  The cattle controls currently in place are based upon principles that have, in the absence of, or effective action against, a wildlife reservoir previously been proven to be effective in the UK.

  1.4  The badger is not endangered in any way, and removing badgers from TB affected areas would have no significant affect on the predominance of the species in the UK. It fact, it seems likely that badger removal could leave the number of badgers in the UK at a higher level than in 1997, when the Krebs report stated that "Badger removal operations are not a threat to overall badger numbers"[1]1

  1.5  It is the belief of the FUW that the current objections amongst some regarding badger culling are not based upon an objective analysis of the scientific evidence regarding TB and the welfare and abundance of badgers, but on the perception that badgers somehow occupy a higher status in the animal kingdom than others, and should be protected at all costs.

2.  BACKGROUND

  2.1  Since 1996 the number of cattle compulsorily slaughtered in the UK due to bovine TB has risen by some 700% since, from 3,752 in 1996 to 29,585 in 2005. The number of cattle compulsorily slaughtered in 1986 was 638, around 2% of the current figure.

  2.2  In 1980, the Zuckerman enquiry into TB was conducted against a background where 28 new herds had tested positive in Great Britain. In the year of the Dunnet TB enquiry, 1986, there were 32 herd breakdowns. In 2005 the total number of new herd TB incidents was 3,514.

  2.3  The current level of TB is higher than it has been for many decades; in 2005 3.9% of herds were confirmed as new herd TB incidents, whereas in 1962 the proportion of total herds with reactors was less than 1.5%. There is now significant concern that the European Union and the wider world will impose further severe restrictions on the exportation of British meat and dairy products due to the TB crisis, and that such action would not only add to the current problems facing the rural economy, but would also be severely detrimental to the image of Britain at a time when the massive efforts made to restore Britain's image in the wake of the BSE and FMD crises are coming to fruition.

  2.4  While there has been in place a compensatory system for those farmers who lose animals as a result of TB, that system does not take into consideration either the total losses experienced by farms, or the emotional impact TB has on farming communities. The current TB crisis is therefore not only of serious concern to the FUW because of the economic effects, but also due to the social and emotional impact it is having on communities and families.

  2.5  In May 2005 the University of Exeter reported that the value of cattle slaughtered was 66% of the total cost of a breakdown on a beef farm and 65% of that on a dairy farm, and that the emotional effects led to severe stresses on communities and families[2]2. The report concluded that:

    ". . . there is little disagreement that the total cost of a TB incident generally exceeds payments for the livestock slaughtered . . . there are significant economic impacts which typically have to be borne by the farm business concerned . . ."

    "An outbreak of bovine TB can have a serious effect on the farm business concerned and movement restrictions, sometimes for extended periods, can make the impact much worse than that of an outbreak of FMD. It is the longer lasting effects which are the source of most of the damage done to the farming industry by bovine TB. Where they apply . . . they typically result in significant consequential effects on the economic performance and growth of the farm business, and not infrequently are associated with serious stress affecting at least some of the farmer, the farm family and the farm staff".

  2.6  Prior to 1973, farmers routinely controlled badgers, just as any other pest, were badgers caused excessive damage in terms of crop or pasture damage, lamb losses, etc. A significant proportion of such control was carried out using firearms. Since 1973 successive pieces of legislation, primarily designed to prevent the abhorrent practice of badger baiting, have had the effect of reducing the humane control of badgers, thus allowing badger densities and numbers to increase without control, probably for the first time in Britain's history.

  2.7  In 1997, Professor Stephen Harris of Bristol University concluded that, during the previous decade, the number of annex setts in the UK had increased by 87%, subsidiary setts by 54%, and outlying setts by 55%, whereas the number of disused setts had declined by 41%. The experience of our members has been of a continuing rise in badger numbers since Professor Harris' survey.

  2.8  The significant increase in badger numbers during the last 30 years is indisputable, and we are not aware of any bodies who do not accept that such growth has occurred.

  2.9  There is now significant anecdotal and scientific evidence that the increase in badger numbers has resulted in the decline of the hedgehog, due to predation. The Mammals Trust recently reported a 20% decline in hedgehog numbers over the last four years, while in 2004 Defra funded researcher Richard Young told the European Hedgehog Research Group that:[3] 3

    "Surveys revealed negative correlations between badger density and hedgehog abundance, predicting that badgers can achieve sufficiently high densities to exclude hedgehogs from rural habitats"

  and that

    ". . . these results, combined with information from previous research, show that high badger density can have a major impact on hedgehogs in rural and even suburban habitats".

  2.10  The findings of Dr Young are perfectly in line with the observations of FUW members that badger and hedgehog abundances are inversely linked, and that the proliferation of badgers has led to hedgehogs becoming an extremely rare sight.

  2.11  Many of our members have expressed concern that, just as it took many decades for the elimination of red squirrels by greys to become recognised by Government, the hedgehog may similarly be in danger of becoming extremely rare due to the growth in badger numbers.

3.  TB CONTROLS

  3.1  It is well established that disease risks and the propensity for wildlife reservoirs to become established are a positive function of population densities and numbers. The badger population and density growth has naturally exacerbated the potential for TB wildlife reservoirs to become established.

  3.2  Since 1986, badger control measures in response to TB incidents have gradually been stepped down, and were finally abandoned in 1996. The gradual reduction in badger control in diseased areas has been accompanied by an exponential rise in the number of cattle culled due to TB (Appendix I). The number of cattle compulsorily slaughtered in 2005 due to TB was 29,585, 28% more than in 2004.

  3.3  The Farmers' Union of Wales have long recognised the importance of controlling bovine tuberculosis (bTB) in all significant species, those species being cattle, badgers, and deer.

  3.4  Previously successful TB control policies have either involved the testing and culling of cattle in the absence of a significant wildlife reservoir (ie when badger densities were significantly lower than at present), or have been accompanied by the efficient removal of wildlife susceptible to TB (such as occurred during the 1970s and 1980s)

  3.5  While some individuals and organisations continue to claim that the role of badgers in TB transmission is not relevant, the conclusions of both the RBC and Irish Four Areas trials demonstrate beyond doubt that badgers play a major role in the transmission of TB.

  3.6  The perturbation effect that occurred in areas surrounding the RBCT areas demonstrates beyond doubt the significance of the role that badgers play in transmitting TB; if badgers were not a significant factor, then perturbation would not have occurred.

  3.7  While the FUW have no objection to the principle of using trapping as a method of badger control, it is our belief that the inherent inefficiencies of trapping and the disruption that pre-baiting and then setting traps causes to badger populations made a significant contribution to perturbation.

  3.8  The FUW does not believe that trapping is in any way more humane than other possible methods of badger control, and that it has traditionally been used simply for cosmetic reasons, rather than any real benefits in terms of animal welfare.

  3.9  As well as being remarkably inefficient, trapping and then killing badgers is also phenomenally expensive, with estimated costs per animal culled varying between £700 and £4,000.

  3.10  As confirmed by the RBC and Irish Four Areas trials, affects of all major TB vectors must be minimised if the disease is to be controlled. Those vectors are, beyond doubt:

    (a)  Cattle to cattle.

    (b)  Cattle to badgers.

    (c)  Badgers to badgers.

    (d)  Badgers to cattle.

  3.11  Notwithstanding actions taken in the RBCT areas, during the last 10 years only vectors (a) and (b) have been addressed by the Government. It is therefore not surprising that TB has increased at such a dramatic rate.

  3.12  Given the widely accepted significant increase in the badger population, it is the view of the FUW that necessary culling in regions affected by TB would have an insignificant affect on the UK badger population as a whole, and it is not unlikely that the total number of badgers left after such a cull would be higher than the number 10 years ago, when the Krebs Report clarified that culling would not in any way an endanger the species1.

  3.13  Since a cull would not have a significant impact on the UK badger population as a whole, and would certainly not endanger the species in any way, the FUW is firmly of the opinion that the iconic nature of badgers severely impedes the abilities of some to make objectively analyses of the scientific evidence relating to badgers and TB. For example, despite the fact that badgers outnumber deer many-fold in Wales, we are unaware of any significant objections being made to the control of deer for disease control purposes. In fact, Defra are actively encouraging deer control. Similarly, Biodiversity Minister Jim Knight recently stated in relation to grey squirrels that "we must control them effectively now or there will be serious consequences".

  3.14  The FUW is concerned that what we have already described as the abhorrent practice of badger baiting has disproportionately influenced the totally separate issue of pest control by acceptable humane means.

  3.15  Despite the widely accepted increase in badger numbers, there exists an influential perception amongst members of the general public that badgers are rare. This can primarily be attributed to the large proportion of people living in urban environments and the nocturnal nature of the badger. Nevertheless, recent DEFRA funded research conducted by Reading University revealed that 71% of the general public though wildlife management was sometimes necessary, and 51% thought that there could be fewer badgers as long as they did not become endangered.

  3.16  Members of the FUW who routinely controlled badgers prior to the 1973 Badger Protection Act can confirm that badger control with rifles can be a highly efficient and humane method of control. Allowing such a method to be practiced has been one of the policies advocated by the FUW as a method of controlling the wildlife reservoir.

  3.17  The Government have advocated the use of rifles as a humane way of controlling both deer and foxes; species that make far more difficult targets for marksmen than badgers.

4.  THE FUW POSITION REGARDING CULLING

  4.1  The FUW accepts the view recently put forward by the Independent Science Group[4]4 (ISG) that systematic and prolonged culling extending to large areas could be expected to have an overall positive impact on cattle and herd breakdown rates. It is worth noting that the 300 km2 figure referred to by the ISG would, in simplistic terms, represent circular areas with radii in the region of only six miles.

  4.2  However, it is our understanding that the views of the ISG are based upon culling being carried out using the trapping method used in RBC trial areas. For the reasons already given above, it seems likely that perturbation effects could be reduced by using more efficient and less disruptive culling methods.

  4.3  Despite the 300 km2 area quoted by the ISG, it is the view of the FUW that the area over which culling action could be carried out in a way that minimises perturbation effects could be far less than 300 km2 in smaller areas where TB is a problem. For example, if a TB wildlife reservoir exists in an area just one mile in diameter, we would anticipate that culling over a three mile diameter would drastically reduce perturbation effects.

  4.4  We therefore believe that systematic and prolonged culling should take place in "buffer-zones" that surround TB affected areas, as well as within those areas, in order to minimise perturbation effects.

  4.5  In terms of the methods of culling, the FUW believes that, in order to minimise costs and maximise effectiveness, no suitable method should be excluded. Suitable methods include shooting, snaring, and gassing using cyanide gas or carbon monoxide. For the reasons already given above, trapping should be avoided unless all other methods are deemed impractical.

  4.6  Farmers and their agents, gamekeepers, etc., within TB affected areas and buffer-zones should be licensed and encouraged to contribute to culling in selected areas, while ensuring that all culled animals are recorded and collected for testing. However, the Government must also play a role in tackling the disease reservoir, particularly given that the Government's abandonment of all action against the wildlife reservoir has directly resulted in the proliferation of TB.

  4.7  Ministry staff should therefore be employed in targeted areas where farmers are either unwilling or unable to take appropriate action to control badgers. For example, where necessary, Ministry employees or agents should be employed to lamp badgers, lay snares, and gas setts in targeted areas.

  4.8  The very nature of TB means that actions to reduce the wildlife reservoir should be carried out over a period of five to 10 years; a one-off cull would not be effective, and is likely to lead to the re-infection of wildlife and problems such as perturbation.

  4.9  Action must also be taken to control badgers in areas where TB incidents are low, but wildlife is suspected to be the source of a problem; for example, where a TB positive RTA badger has been picked up in a four year testing parish, or where a single farm in a four year testing parish suffers breakdown that are suspected to be linked to badgers.

  4.10  Given the disruption caused in RBCT areas by animal rights extremists (for example, the large proportion of traps stolen), and the violent and destructive nature of some individuals involved in animal rights activities, it is essential that the relevant authorities protect the identities of all those involved in a cull, while taking a robust attitude towards deterring, dealing with, and prosecuting such extremists.

January 2006



1   1 Bovine Tuberculosis in Cattle and Badgers, Report to The Rt Hon Dr Jack Cunningham MP by Professor John R Krebs FRS and the Independent Scientific Review Group, 1997. Back

2   2 Sheppard, A, Turner, M, An Economic Impact Assessment of Bovine Tuberculosis in South West England, Centre for Rural Research, University of Exeter, 25 May 2005. Back

3   3 The effect of Badgers on hedgehog abundance and distribution, Richard Young, Central Science Laboratory, Woodchester Park Research Station, Proceedings of the 6th International Meeting of the European Hedgehog Research Group, April 2004. Back

4   4 ISG Letter to stakeholders, 23 January 2006. Back


 
previous page contents next page

House of Commons home page Parliament home page House of Lords home page search page enquiries index

© Parliamentary copyright 2006
Prepared 15 March 2006