Electronic Journal of Polish Agricultural Universities (EJPAU) founded by all Polish Agriculture Universities presents original papers and review articles relevant to all aspects of agricultural sciences. It is target for persons working both in science and industry,regulatory agencies or teaching in agricultural sector. Covered by IFIS Publishing (Food Science and Technology Abstracts), ELSEVIER Science - Food Science and Technology Program, CAS USA (Chemical Abstracts), CABI Publishing UK and ALPSP (Association of Learned and Professional Society Publisher - full membership). Presented in the Master List of Thomson ISI.
2015
Volume 18
Issue 4
Topic:
Economics
ELECTRONIC
JOURNAL OF
POLISH
AGRICULTURAL
UNIVERSITIES
Pospíšil R. 2015. THE COSTS RELATED ANALYSIS OF BOVINE SPONGIFORM ENCEPHALOPATHY EVIDENCE – THE CZECH REPUBLIC STUDY 2001–2014, EJPAU 18(4), #11.
Available Online: http://www.ejpau.media.pl/volume18/issue4/art-11.html

THE COSTS RELATED ANALYSIS OF BOVINE SPONGIFORM ENCEPHALOPATHY EVIDENCE – THE CZECH REPUBLIC STUDY 2001–2014

Richard Pospíšil
Department of Applied Economics, Philosophical Faculty, Palacký University of Olomouc, Czech Republic

 

ABSTRACT

This paper pays attention to analysis of the economic impacts of the bovine spongiform encephalopathy (BSE) occurrence in the Czech Republic, namely the financial compensations to the farmers whose herds had been affected and the costs of animal killing and carcass disposal in the rendering plant. Between February 2001 and the end of  2014, a total of 1 879 749 cows were examined and 30 cases of the BSE were detected. Consequently, 4243 cows in cohorts were killed and their carcasses were safely disposed of. The farmers whose herds had been affected were provided compensations for the losses suffered. The total of the compensations in this period reached EUR 7 752 000. Of these, 83.3% (EUR 6 458 000) were compensations for the value of the killed animals, 9.7% (EUR 752 000) for the related costs, i.e., killing, safe disposal of carcasses and the examination for the BSE, and 6.9% (EUR 535 000) for the losses due to non-materialised production. The average costs per 1 BSE-positive animal were EUR 258 400 and the average costs per 1 cohort animal were EUR 1827. In the rendering plant responsible for killing the infected and cohort animals and safely disposing of their carcasses, the total of 2342 tons of raw material was processed between March 2003 and 2009, and this cost EUR 363 777. The fact that there were only two last cases of the BSE in 2009 suggests a trend towards the disease eradication, which is in agreement with the situation in the other EU countries.

Key words: financial compensation, bovine spongiform encephalopathy (BSE), cattle, infectious diseases, Czech Republic .

INTRODUCTION

For more than two decades, the European beef demand was affected by the existence of bovine spongiform encelphalopathy (BSE) because of its potential danger to human health. The bovine spongiform encephalopathy (BSE) is an infectious disease cause by prions and was first detected in Great Britain in 1985/1986. In 1988, it was ascertained that the major source of infection was the use of meat and bone meal from the fallen stock animals [14]. In the Czech Republic, feeding meat and bone meal to ruminants was banned in 1991 [1]. A significant long-run impact of BSE in Great Britain, by the end of 1993 has reduced the beef market share by 4.5% [5]. Measures were taken to cushion the industry from the full effects of the crisis and to help restore public confidence in beef products. The UK government banned all cattle over thirty months of age from entering the food chain and introduced a scheme through which these animals could be disposed. It also introduced a calf processing aid scheme to provide an outlet for dairy bull calves, which were usually exported. Other measures included payments to compensate and provide support for primary producers and for the rendering industry. The EU imposed a ban on UK beef exports and reopened beef intervention buying. The effect of these measures was to remove from the market a quantity of beef broadly equivalent to the reduction in domestic consumption plus exports. The total cost in additional public expenditure was approximately 1,50 billion GBP in 1996/97 [5].

In particular, the relationship between scientific advice and regulatory policy has been questioned. To regain public trust, scientific advice needs to be evaluated against various criteria, including the quality of the advice, whether it is transparent and intelligible, and the effectiveness of communication practices and strategies. There should be recommendations for best practice regarding public consultation and involvement, and explicit assessment of both scientific advice and public consultation on policy development. These criteria would provide a counter-political imperative to the natural inclination of the existing scientific advisory system to fall back on the style and culture of positivistic science when a problem appears complex, or when lobbying for a particular course of action that supports a particular interest is strong and influential.

In the industrialized countries, for the sake of public health cattle slaughtered at 30 months and older was examined for the presence of priors in the brain tissue. In the Czech Republic, the regular examination of animals came into effect on 1st February 2001 and, by 31th December 2014, a total of 1 879 749 cattle were examined, of which 30 animals were tested positive. Only two outbreaks of the bovine spongiform encephalopathy in 2009 and no case of the BSE within the last five years confirm that, in the Czech Republic, the disease incidence has definitely a decreasing trend, which is in agreement with the situation in the other EU countries. As a result of 30 positive BSE findings, the total of 4243 cows were killed and their carcasses were destroyed. The animals selected to be killed in relation to each BSE occurrence constitute a cohort, which is a group of animals born in the same herd within 12 months preceding or following the date of birth of the affected bovine animal.

Nowadays according to rules of World Organization for Animal Health each of 180 member countries registered for this organization has assigned a risk status with the degree of risk of BSE. As the official BSE status of a country or zone is determined on the basis of an overall assessment of risk, the occurrence of a new BSE case implies a re-assessment of the official risk status only in the event of a change in the epidemiological situation indicating failure of the BSE risk mitigating measures in place.

Member countries recognised as having a negligible BSE risk in accordance with Chapter 11.4. of the Terrestrial Code of World Organization for Animal Health shows Table 1.

Tab. 1. Negligible BSE risk countries
Argentina
Cyprus
Ireland
Netherlands
Slovenia
Australia
Czech Republic
Izrael
New Zealand
Sweden
Austria
Denmark
Italy
Norway
Switzerland
Belgium
Estonia
Japan
Panama
United States
Brazil
Finland
Korea (Rep. of)
Paraguay
Uruguay
Bulgaria
France
Latvia
Peru
Chile
Hungary
Lichtenstein
Portugal
Colombia
Iceland
Luxembourg
Singapore
Croatia
India
Malta
Slovakia

According to Regulation EU No. 2013/76/EU (from 4th February 2013) it is not necessary to investigate in healthy animals in these countries (from 1st July 2013). Table 2 shows countries with controlled BSE risk that are required to test all animals aged over 30 months.

Tab. 2. Controlled BSE risk countries
Canada
Germany
Nicaragua
Spain
Chinese Taipei
Lithuania
Poland
United Kingdom
Costa Rica
Mexico
Romania

In the Czech Republic the procedure for the destruction of the killed animals developed over years. At the first, 2001 BSE occurrence, the animals were killed on the farm and buried within its boundary. However, this proved difficult in terms of hygiene and sanitation and was ethically unacceptable. Therefore, on the following five occasions, the animals were killed and their carcasses disposed of at the regular rendering plants. This, however, carried a risk of contaminating both the premises and products and thus, in 2003, the rendering plant Asanace Žichlínek Ltd. was assigned by the State Veterinary Administration to become an institution specialized in killing all the BSE suspected animals, and in processing and disposing of their carcasses in the following years. The meat and bone meal produced was subsequently incinerated in cement works.

In accordance with the EU common Agricultural Policy and farming promotion, the EU provides financial compensations to farmers who have suffered losses due to the BSE. Their allocation is regulated by the Act no. 166/1999 on Veterinary Care and on Amendment of Certain Related Acts (Veterinary Act), with particulars given in the Title IX Compensation of Costs and Losses Incurred in Connection with Dangerous Contagious Diseases [2]. This defines reimbursements to farmers whose cattle herds have been affected by the transmissible diseases specified in the Annexes 3 and 4 to this Act. For 62 specified dangerous transmissible diseases, it outlines the indemnity strategies and the general itemisation of the compensation. The Czech legislation is in full agreement with the Regulation No. 999/2001 of the European Parliament and of the council, of 22nd May 2001, laying down the rules for the prevention, control and eradication of certain transmissible spongiform encephalopathies, as amended [12].

To provide a deeper insight into the legal and economic aspects associated with the BSE in the Czech Republic, the first part of the study was focused on the evaluation of the indemnity policy and quantification of reimbursements provided for farmers according to the Veterinary Act in the period from 2001 to 2014. The total costs were itemised and the cost items broken down to cover the individual operations the farmers were responsible for in the BSE management and for which they were subsequently reimbursed.

In the second part, my aim was to calculate the costs related to the killing and disposal of the animals brought to the rendering plant Asanace Žichlínek Ltd. between october 2003 and 2009. This calculation ends in 2009, because after this year there was no occurrence of BSE in the Czech Republic and no kiliing and disposal of animals in this rendering plant

MATERIAL AND METHODS

The chief method used in the first part was the evaluation of legal rules, i.e. legal acts, regulations and implementing provisions, and their application to the BSE occurrence in czech herds. in addition, the EU legislation concerning this issue was analysed and compared with the relevant legislation of the Czech Republic.

The method of economic evaluation was the analysis of statistical data related to the costs of the BSE eradication in the czech republic; this information was provided by the Ministry of Agriculture of the Czech Republic [13]. Subsequently, the data was related to the individual cost compensation items, as specified by the Veterinary Act.

The analysis presented in the second part was based on account records provided by the Asanace Žichlínek Ltd. [11]. It included an evaluation of the whole process consisting of animal killing, carcass mechanical processing, heat treatment, sterilisation, drying, hammer-mill pressing and pulverisation, and dispatching of the processed material. The costs of transporting the animals to be killed at the rendering plant were not included. They were born by the farmers who were subsequently reimbursed by the Ministry of Finance in accordance with the Veterinary Act.

RESULTS

Part 1. Economic evaluation of loss compensations
The reimbursements for the 2001–2014 periods were itemised, analysed and finally summarised.

Table 3 shows the compensations for all costs spent in relation to the BSE between 2001 and 2014. A total of 30 animals tested BSE-positive and, consequently, 4 243 animals coming from 141 herds were killed due to the constitution of cohorts. The total of compensations in this period reached EUR 7 752 000. The average occurrence was 2.14 BSE-positive animals per year, the average costs per 1 BSE-positive animal were EUR 258 400, and the average costs per 1 cohort of animals (killing and carcass disposal) were EUR 1 827.

Of these, 83.3% (EUR 6 458 000) were compensations for the value of the killed animals, 9.7% (EUR 752 000) for the related costs, i.e., killing, safe disposal of the carcasses and examination for the BSE, and 6.9% (EUR 535 000) for the losses due to the non-materialised production.

The number of cohorts is not in agreement with the total of 141 herds affected, as shown in Table 3. This is because there were instances when an animal from the original cohort was transferred or sold to another herd. Its new keeper, having to comply with the Emergency Veterinary Measures, then had this cows killed and thus one cow was reported in association with two or more herds.

Tab. 3. Total costs (in EUR thousand) associated with 30 BSE cases in the period 2001 to 2014
Period
Numberof herds  by cohort size
Number 
of animal killed
Value of animals
Killing
Safe carcas disposal
Examination for BSE
Related costs*
Observ.
of emerg. veter. measur.
Non- material production
Total
2001 to 2014
A.  109
219
383.4
8.6
39.9
6.0
3.8
0.0
5.0
446.6
B.    17
854
1164.5
16.2
90.1
34.7
6.3
4.0
97.4
1413.2
C.    15
3170
4910.1
55.1
321.2
130.8
27.0
15.3
432.6
5892.1
∑   141
4243
6458.0
79.9
451.2
171.5
37.1
19.3
535.0
7752.0
A = 1–10 animals in a cohort; B = 11–100 animals in a cohort; C > 100 animals in a cohort
* Costs related to killing and safe disposal of carcasses and farm decontamination

Part 2. Evaluation of the costs associated with animal killing and carcass processingat the Asanace Žichlínek Ltd
In the period from october 2003 to the end 2014, a total of 3793 cattle were killed and their carcasses destroyed and disposed of at the rendering plant. This included 701 cows in 2003; 1167 in 2004; 1262 in 2005; 288 in 2006; 131 in 2007, 23 in 2008 and 221 animals in 2009. In the terms of the cohort size, the largest one (7th) included 875 cows, the smallest (27th) had only three animals. The average was 126 animals per 1 cohort. The animals of  27th cohort derived from the BSE case detected on 19th December 2007 were gradually identified and destroyed early in 2008. The selected economic items and their distribution in the years 2003 to 2009 are shown in Table 4. Table ends in 2009, because after this year there was no occurrence of BSE in the Czech Republic.

Tab. 4. Selected costs of BSE-related cattle disposal at the rendering plant Asanace Žichlínek Ltd. and their distribution over the period 2001 to 2009
Quarter 1
Quarter 2
Quarter 3
Quarter 4
Total
2003
EUR/kg
0.15
kg processed
415 080
415 080
animal killed
701
701
total costs
53 807
53 807
2004
EUR/kg
0.15
0.15
0.15
0.15
kg processed
362 869
60 800
190 951
94 410
709 030
animal killed
607
101
310
149
1167
total costs
47 039
7881
24 753
12 238
91 911
2005
EUR/kg
0.17
0.17
0.17
0.17
kg processed
257 220
293 200
146 800
115 200
812 420
animal killed
397
454
240
171
1262
total costs
42 870
54 296
27 185
21 333
145 684
2006
EUR/kg
0.19
0.19
kg processed
158 426
32 620
191 046
animal killed
236
52
288
total costs
29 338
6041
35 379
2007
EUR/kg
0.19
kg processed
79 220
79 220
animal killed
131
131
total costs
14 670
14 670
2008
EUR/kg
0.25
kg processed
14 680
14 680
animal killed
23
23
total costs
3534
3534
2009
EUR/kg
0.30
kg processed
62 660
62 660
animal killed
221
221
total costs
18 792
18 792
    Total costs for 2003 to 2009
363 777

From Table 4, it follows that a total of 2342 tons of raw material was processed at costs ranging from EUR 0.15 to EUR 0.30 per 1 kg between 2003 and 2009. The gradual increase in the cost per 1 kg was due to a rise in operation costs including higher wages and increased energy prices. Based on the cost per 1 kg processed material, the total costs associated with animal killing and carcass disposal reached EUR 53 807 in 2003, EUR 91 911 in 2004, EUR 145 684 in 2005, EUR 35 379 in 2006, EUR 14 670 in 2007, EUR 3534 in 2008 and EUR 18 792 in 2009. The total costs for the whole period of 2003–2009 amounted to EUR 363 777.

DISCUSSION

Although early and stringent veterinary precautions were adopted, in the first place a ban on feeding meat and bone meal (MBM) to cattle in 1991, the first case of the BSE in the Czech Republic was detected in 2001. The most probable cause was an indirect contamination of cattle feed with the imported MBM or with the MBM intended for feeding pigs and poultry

and allowed for use before 2003 [14]. In the period from 1st February 2001 to 31th December 2014, 30 BSE-positive cases were identified by the active monitoring for the BSE involving 1 879 479 cows. The detection was so effective thanks to the well co-ordinated laboratory diagnostic procedures carried out in the laboratories of the State Veterinary institutes in Prague, Jihlava and Olomouc.

To reduce the economic impact of the BSE on farmers, legal means have been established to reimburse farmers for the losses both direct and related. The latter involve costs of the examination for the BSE, transport of animals to a specialised rendering plant, their killing and safe disposal of their carcasses, and cleaning and disinfection of the holding and its equipment, though this procedure is questionable, because the BSE is not a truly contagious disease. In addition, the farmer is reimbursed for losses due to the non-materialised production. however, all these compensations cannot completely cover the costs incurred in relation to the BSE.

In the first place, the producer-consumer relations, usually taking a long time to establish, are destroyed and the return to the market is difficult; also, large costs are necessary to build up the herd again. These costs are difficult to calculate and their compensation cannot be claimed because they are not treated by the legislation. A BSE incident is also associated with

several adverse consequences, such as a loss of jobs in an agricultural enterprise, which can have a deep impact on rural populations. The ensuing problems in the broadest sense of the word can partly be eased by the commercial insurance policy. The past experience showed that most of the farmers were insured. Any  payment of insurance benefit has no effect on the amount of cost compensation based on the Veterinary Act. Since a farmer-insurance company relationship is a business one, it was not possible to find out the information on benefit payments and to include it in this study.

The total amount of compensations paid was EUR 203 704 in 2001, EUR 59 259 in 2002, EUR 1 740 741 in 2003, EUR 1 474 074 in 2004, EUR 3 403 704 in 2005 and EUR 411 111 in 2006. In 2007, it was only EUR 6278, because the 27th case was an eleven-year-old cow whose cohort included only three animals left due to slaughtering of the other cows. Compensations provided in relation to the 28th BSE-positive case detected on 19th December 2007 were paid in March 2008 and reached EUR 50 222. The last two cases of BSE occurrence in 2009 cost 402 907. The total costs associated with the BSE occurrence in the czech republic amounted to EUR 7 752 000. The average costs per 1 BSE-positive animal were EUR 258 400 and the average costs per 1 cohort of animals (killing and disposal of the carcasses) were EUR 1 827.

To ease the negative economic impacts of the BSE, the EU provides financial support for all member states. For instance, in 2007 the Czech Republic received EUR 1 640 000 for the active monitoring and EUR 2 500 000 for the eradication [7].

It is interesting that the amounts of reimbursement presented in the international literature are reported only as the total costs per certain period, including the data from the great Britain which suffered most. The calculation of cost compensations is based on tables prepared in advance in which, for each cattle age category, the amount of compensation is given without any respect to the animal’s actual productivity [8]. The British government study has reported that the total net cost of the BSE crisis to the Exchequer by the end of the fiscal year 2001/2002 reached £ 4.2 billion, to which the EU contributed £ 487 million, which is 11.6% [4]. It is evident that this high sum of money was relevant to the exceptionally high number of the BSE-positive cows that had exceeded 187 000 animals by that fiscal year. This sum also included £ 720 million to compensate for the loss of markets in the EU countries, because the European commission banned beef export in March 1996 (in the USA, import of British beef was banned in the late 1980s). The beef production accounts for about 0.5% of the British gross domestic product and the British beef industry has over 130 000 employees. With the decrease in beef meat prices, the prices of all other kinds of meat increased in the great Britain. This chiefly concerned poultry and lamb meat, which increased in price approximately by 5%, with pork price remaining generally unchanged [9].

In Northern Ireland, the beef producing industry employs over 5000 workers and the additional 600 000 are employed in the related industrial branches [6]. Thus, the rate of employment in this industry has a deep social impact. The costs of re-qualification for workers who had lost their jobs due to the reduced beef production were estimated to be 7.9% of all costs related to the BSE crisis [10].

This study paid attention to the costs of animal killing and their carcass disposal in the rendering plant specialised for this purpose. The evaluation was based on the cost per 1 kg of the processed material, which ranged from EUR 0.15 in 2003 to EUR 0.30 in 2009. Between March 2003 and the end 2009, the total of 3793 bovine animals associated with the BSE occurrence were killed there and their carcasses were destroyed and disposed of; this accounted for 2342 tons of the processed material. The total costs for the whole period amounted to EUR 363 777. The considerable increase in costs during this period is in agreement with the inflation development (wagepush, energy price increase) in the domestic economy and is also related to the increased financial demands for the hygienic and technological quality of the rendering plant operation (septic and aseptic units, disinfecting fords, separation of processing routes) after the Czech Republic joined the EU.

Costs described here did not include the costs of transporting the animals to be killed to the rendering plant. These were covered by the farmer who was subsequently reimbursed by the Ministry of Finance in accordance with the Act no. 166/1999 on Veterinary Care and on the Amendment of Certain Related Acts. These costs greatly varied depending on the distance between the farm and the rendering plant and on whether the farmers had their own  transporting facilities or had to hire it.

In one instance, no long-distance transport was needed. It was when the first BSE case was discovered in 2001 in the village of Dušejov in the Jihlava district. All 134 cows of the cohort were killed on the farm and buried in its vicinity. The carcasses were placed four metres deep in the ground and were covered up with a 1.5-to 2-metre layer of soil [10]. Although this method of disposal may seem complicated, the total costs were only EUR 2866 (hydrogeological expert report EUR 300, wages EUR 478, local transport EUR 1593, fencig EUR 495) [13], which was much less than what the process of disposal would have cost in a rendering plant.

However, for the public health and environmental reasons it was not possible to continue with this method of disposal. Moreover, the cohorts derived from the later BSE cases were larger in size that the first cohort buried in Dušejov. For instance, the cohort from the 7th case in 2003 had 875 cows and that from 22nd case in 2005 had 333 cows, and the burial of so many animals would not have been feasible.

The rendering process produces meat and bone meal; one kilogram of raw material gives 0.28 to 0.29 kg of it. In addition, 0.08 to 0.09 kg of animal fat is obtained; the residual fat content in meat and bone meal is 13% to 18% and residual moisture is 2.8%.

The meat and bone meal produced is transported to cement works for incineration at the temperature of about 1 200°C. One kilogram of meat and bone meal gives about 0.25 kg ash. By the process carried out at the rendering plant and by the subsequent incineration in a cement factory, 30 to 40 kg ashes are produced. The ashes are included in the cement  production and become a part of the final product. Considering that the total number of cows killed and disposed of at the rendering plant Asanace Žichlínek was 3 793, the total amount of ashes produced in the cement works was 637 tons.

The rendering plant paid 5 cents the cement works for 1 kg meat and bone meal to be incinerated, and claimed an equal compensation from the Ministry of Agriculture of the Czech Republic. The funds to cover the expenses related to the disposal of meat and bone meal had been included in the state budget (the “general Treasury Administration” chapter) until 2007. From that year on, the funds were no longer available and the meat and bone meal was incinerated in the cement works free of charge. however, the cement works can utilize the caloric power of the meat and bone meal, because its 18 MJ per kg equals to the fuel efficiency of 1 kg lignite [3]. Considering that the average price of 1 ton of lignite is EUR 125, the 637 tons of burnt meat and bone meal contributed about EUR 79 625 to the cement factory’s budget.

CONCLUSION

Beef food safety events have contributed to considerable market volatility, produced varied consumer reactions, created policy debates, sparked heated trade disputes, and generally contributed to beef industry frustrations. The beef sector has undergone a series of changes as a result of BSE and successive food scares and agricultural policy reforms. The purpose of the paper was to analyze the impact of costs related to BSE disease control in the Czech Republic since 2001. Some factors have a positive impact – like health protection of people, others a negative impact, on efficiency of animal husbandry and beef meat demand.

The impact on particular sectors and within sectors varied considerably, depending on the distribution of compensation payments and the ease of adjustment. Beef producers in aggregate were in the main largely protected from the crisis by one-off compensation payments, although there was a distribution of impacts within the sector. Slaughterers and renderers also benefited from the operation of the various schemes introduced in the wake of the crisis.

Between February 2001 and the end of 2014, the total of 1 879 479 cows were examined and 30 cases of the BSE were detected. consequently, 4 243 cows in cohorts were killed and their carcasses were safely disposed of. The total of compensations in this period reached EUR 7 752 000. Of these, 83.3% (EUR 6 458 000) were compensations for the value of the killed animals, 9.7% (EUR 752 000) for the related costs, i.e., killing, safe disposal of carcasses and examination for the BSE, and 6.9% (EUR 535 000) for the losses due to the non-materialised production. The average costs per 1 BSE-positive animal were EUR 258 400 and the average costs per 1 cohort of animals were EUR 1 827. In the rendering plant in Žichlínek responsible for killing of the infected and cohort animals and safely disposing of their carcasses, the total of 2 342 tons of raw material were processed between March 2003 and, and this cost EUR 363 777.

ACKNOWLEDGEMENTS

Work on this article was supported by the grant from Philosophical Faculty of Palacký University, IGA_FF_2015_014, Continuities and Discontinuities of Economy and Management in the Past and Present.

REFERENCES

  1. Anonym, 1991. Vyhláška č. 413/1991 Sb., o registraci některých druhů krmiv, jejich dodavatelů a o odborné státní kontrole (Decree No. 413/1991 Sb., about registration of feed, its suppliers and specific state control). Mze ČR, Praha.
  2. Anonym, 1999. Zákon č. 166/1999 o veterinární péči a o změně některých souvisejících zákonů (Act no. 166/1999 coll. on Veterinary Care and on Amendment of Certain Related Acts). Mze ČR, Praha.
  3. Anonym, 2008. Protokol č. 383/2007/PoV (record no. 383/2007/PoV). Laboratoř paliv, odpadů a vod VÚHU, a.s. Most.
  4. Brinkle J., 2002. Impact of BSE on the UK Economy. National Audit office, NC, USA.
  5. Burton M., Young T., 1996. The Impact of BSE on the Demand for Beef and Other Meals in Great Britain. Trevor & Francis, 28 (6), 687–693.
  6. Caskie P., Moss J.E., Davis J., 1998. The beginning of the end or the end of the beginning for the BSE crisis? Food Policy, 23, 231–240.
  7. EU-Dg SAnco E.2, 2006.  Hygiene and control measures. Annual Activity report, 42–43.
  8. DEFRA, 2007. Compensation for Bovine TB, BSE, Brucellosis and Enzootic Bovine Leukosis. Information Bulletin, ref: 238/07.
  9. Leeming J., Turner P., 2004. The BSE crisis and the price of red meat in the UK. Applied Economics, 36, 1825–1829.
  10. Meloun V., 2006. Výskyt BSE v České republice do roku 2006 (BSE occurrence in the Czech Republic till 2006). [Dissertation Thesis.] Státní veterinární správa Čr, Brno.
  11. Nicák J., 2008. Osobní sdělení, [Personal communication]. Účetní doklady Asanace, spol. s r.o. Žichlínek.
  12. Pospíšil R., 2008. Hlavní zásady a struktura náhrad poskytovaných chovatelům s výskytem bovinní spongiformní encefalopatie v chovech skotu (Majority of compensations to Breeders with BSE occurrence in Breeding cattle). Acta Universitatis Agriculturae et Silviculturae Mendeleianae Brunensis, 56, 257–261; ISSN 1211-8516.
  13. Saksún J., 2008. Informace Ministerstva zemědělství ČR k výskytu BSE v ČR (Ministry of Agriculture information on BSE occurrence in the Czech Republic). Mze, ČR.
  14. Semerád Z., 2007. Osobní sdělení, [Personal communication]. SVS, ČR.
  15. Wilesmith J.W., Wells G.A.H., Cranwell M.P., Ryan J.B.M., 1988. Bovine spongiform encephalopathy: epidemiological studies. Veterinary record, 123, 638–644; ISSN 0042-4900. Arrived on 10th november 2008.

Accepted for print: 26.11.2015


Richard Pospíšil
Department of Applied Economics, Philosophical Faculty, Palacký University of Olomouc, Czech Republic
Křížkovského 12
771 80 Olomouc
Czech Republic
email: richard.pospisil@upol.cz

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