15 Pohorecka.indd - Journal of Apicultural Science
Transkrypt
15 Pohorecka.indd - Journal of Apicultural Science
Vol. 55 No. 1 2011 Journal of Apicultural Science 137 EPIZOOTIC STATUS OF APIARIES WITH MASSIVE LOSSES OF BEE COLONIES (2008-2009) K r y s t y n a P o h o r e c k a 1,2, A n d r z e j B o b e r 2, M a r t a S k u b i d a 2, D a g m a r a Z d a ń s k a 2 1 Research Institute of Horticulture, Apiculture Division, Puławy, Poland 2 National Veterinary Research Institute, Department of Parasitology with Laboratory of Honey Bee Diseases, Puławy, Poland E-mail: [email protected] Received 30 May 2011; Accepted 10 June 2011 S u m m a r y In 2008 and 2009, winter bee colony mortality in apiaries showed losses which ranged from 30% to 100%. Analyses of tests results obtained from 1000 colonies (from 142 apiaries) were performed to determine the impact of pathogens on the winter bee colony mortality in apiaries. Relationships between individual pathogens were also determined. Dead bees were sampled separately from an average of 7 colonies in each apiary, and the presence of V. destructor, Nosema spp. and viruses: ABPV, CBPV, IAPV, DWV was detected. Co-infection with 3 or 4 pathogens was detected in over 60% of bee colonies. Infestation of V. destructor was found in 88.7% of the colonies while infection of deformed wing virus (DWV) in 76%. A similar number of colonies (74%) were infected with Nosema spp. parasites. Acute bee paralysis virus (ABPV) was detected in 35% of the examined colonies and chronic bee paralysis virus (CBPV) was found in only 7,8% of the colonies. The level of Varroa destructor and Nosema spp. infestation was high (averaged 192 mites per sample and 18 million Nosema spores per bee). Severe colony losses in examined apiaries could be attributed to the wide prevalence of V. destructor with DWV and ABPV infections, and/or Nosema spp. infestation. Losses can also be attributed to the co-occurrence of these pathogens in bee colonies and their total negative impact on the bees. Keywords: Apis mellifera, winter losses, pathogens. INTRODUCTION High winter losses of bee colonies are one of main but not the only one reason, for the decline in the number of honey bee colonies in many European and North American countries (vanEngelsdorp et al., 2010, 2011; Neumann and Carreck, 2010; Potss, 2010). During the winter of 2007/2008, beekeepers from most regions of Poland reported extraordinary losses of bee colonies. The colony losses amounted to 15.9% between the autumn of 2007 and spring of 2008. About 1.0% of all beekeepers in Poland took part in the 2007/2008 survey (Topolsk a et al., 2008). However, according to beekeeper associations, colony losses were as high as 30.0%. In 2009, colony mortality was significantly lower. Beekeepers lost approximately 8.7% of their colonies during the winter of 2008/2009. The number of beekeepers participating in the 2008/2009 survey amounted to about 1.2% of all beekeepers in Poland. The 8.7% figure was in agreement with the assessment of beekeeper associations. According to the beekeeper associations, the colony mortality was about 9.0% (Topolska et al., 2010). However, in certain regions the losses were substantially higher than the average. The reasons for the mass bee mortality are not clear, especially when mortality was accompanied with a sudden depopulation of honeybees. Among the many mentioned factors, the most important are bee diseases (Cox- Foster et al., 2007; Higest et al., 2008, 2009; 138 Berthoud et al., 2010; Carrec k et al., 2010; Chauzat et al., 2010a; Dahle, 2010; Le Conte, 2010; Martin et al., 2010; Paxton, 2010; Topolska et al., 2010). The epizootic state of polish apiaries is unknown. Therefore, the aim of this study was to identify the pathogens occurring in dead honey bee colonies originated from apiaries where the severe colony losses ranged from 30% to 100%. We also determined the relationships between pathogens and colony mortality as well as the relationships between the pathogens. MATERIAL AND METHODS Research was carried out in 2008 - 2009, in apiaries where the colony losses during the wintering period amounted to at least 30.0%. At the beginning of each year, beekeepers were notified about the purpose of the research. We gave the beekeepers standardized precise rules for sample collection as well as a questionnaire that provided us with information about the scale of bee losses and types of colony management. According to our instructions, in each apiary, samples of dead bees were supposed to be collected for laboratory tests separately, from bottom boards of 10 randomly chosen colonies. Samples were immediately sent to the laboratory after the first spring beekeeper inspection; between March and 30 April in 2008 and 2009. In 2008 and 2009, we received the material for laboratory tests from about 300 beekeepers. The samples came from apiaries located in all 16 Polish provinces, but most of the samples came from 9 regions of Poland: Małopolskie (46 apiaries), Lubelskie (39 apiaries), Zachodniopomorskie (36 apiaries) Mazowieckie (29 apiaries), Wielkopolskie (29 apiaries), Dolnośląskie (22 apiaries), Świetokrzyskie (21 apiaries), Śląskie (21 apiaries), and Lubuskie (10 apiaries). The samples were kept in separate test tubes and stored at -20°C until used. Samples from each apiary were individually examined. Varroa destructor was detected by the shaking method and the number of mites was recorded. In each sample, infestation with Nosema spp. was investigated microscopically. A Bürker haemocytometer was used to determine the number of Nosema spp. spores. Each homogenized sample was prepared from the abdomens of 30 bees and 30 ml of water. The occurrence of bee viruses i.e. Chronic bee paralysis virus (CBPV), Acute bee paralysis virus (ABPV), Deformed wing virus (DWV), and Israeli acute paralysis virus (IAPV) were detected using one step RT-PCR. Five dead bees from each sample were homogenized and used for total RNA extraction by use of the Total RNA Mini Kit (A&A BIOTECHNOLOGY) and afterwards for reverse transcription - PCR, by employing the One-step RT-PCR Kit (Qiagen). Each virus was targeted with a single diagnostic primer pair (Tab. 1). One step RT-PCR was performed using the following thermal profile: reverse transcription for 30 min at 50°C followed by polymerase chain reaction: 15 min at 95°C followed by 35 cycles with 1 min at 94°C, 1 min at 55°C, and 1 min at 72°C, followed by 10 min at 72°C for final Table 1 Primers used for the detection of ABPV, CBPV, DWV and IAPV Virus Sequence of primer (5’-3’) Length of product (bp) Reference ABPV GCT CCT ATT GCT CGG TTT TTC GGT TTA TGT GTC CAG AGA CTG TAT CCA TCA GAC ACC GAA TCT GAT TAT TG ACT ACT AGA AAC TCG TCG CTT CG TCG ACA ATT TTC GGA CAT CA ATC AGC GCT TAG TGG AGG AA ATC GGC TAA GGG GTT TGT TT CGA TGA ACA ACG GAA GGT TT 900 C h e n et al. (2006) 569 B l a n c h a r d et al. (2007) 702 C h e n et al. (2006) 767 C ox- Fo s t e r et al. (2007) B l a n c h a r d et al. (2008) CBPV DWV IAPV Vol. 55 No. 1 2011 Journal of Apicultural Science extension. Positive and negative controls were included in each run of RT - PCR. Amplicons were analyzed by means of 1.0% agarose gel electrophoresis, staining by ethidium bromide, and visualizing by UV light. Specificity of the PCR products was verified by sequencing, and comparing to isolates of ABPV, CBPV, DWV and IAPV available on GenBank database. Unfortunately, due to a number of reasons, some beekeepers took less than the requested number of samples, and not all samples were collected according to our instructions. That was why, in some cases, either samples were not suitable for examining or we were unable to perform all the tests. For our analysis, we only took into account the results from those apiaries that fulfilled 2 requirements. The first requirement was that samples were collected from at least 5 colonies and they were tested for the presence of all 6 pathogens. The second requirement was that beekeepers gave complete and precise information on the extent of losses in their questionnaire. We have statistically analyzed data from 142 apiaries (total 1000 bee colonies) that fulfilled the 2 requirements for both 2008 and 2009. For each apiary, 7 samples were analyzed on average. The percentage of the winter-losses were calculated for each apiary individually. The percentage was based on the number of successfully overwintered colonies in relation to the number of colonies prepared for wintering in autumn. In order to 139 analyze the impact of the pathogens, we grouped apiaries according to those that had a similar percentage of winter losses, i.e. the groups were at 10%-intervals on a range from 30% to 100%. Statistical analysis Linear regression analysis and test t for α=0.05 were carried out in order to determine the impact of: the number of pathogens that had co-occurred, the level of the V. destructor infestation, level of the Nosema spp. infestation, and viral infections on the losses of colonies and the relations between pathogens. Comparisons of average values of evaluated parameters for homogeneous groups were performed using the ANOVA test, and multiple comparisons with Tukey and KruskalWallis tests on a level of significance α=0.05. Statistica 8 software was used. RESULTS The most numerous groups were those which had losses ranging from 30% to 50.0% (Tab. 2). In the other groups, the numbers of apiaries and samples were similar. In all the investigated apiaries from autumn to spring, about 5440 bee colonies were lost (58.4%). Depending on the size of the apiary, from 3 to 385 of the colonies died (38 on average) (Tab. 3). Samples containing none of the six examined pathogens amounted to 0.4%. Only 9.0% of the samples were infected with 1 pathogen. On the other hand, there was not even one sample which contained all six pathogens. The number of samples with 5 pathogens Table 2 Number of apiaries and the different percentages of the winter losses Extent of bee colony losses (%) Number of apiaries Mean number of dead colonies per apiary Number of examined samples (colonies) 30-40 41-50 40 24.7 280 26 34.5 182 51-60 14 45.2 98 61-70 16 39.7 112 71-80 14 46.1 98 81-90 14 64.5 104 91-100 18 82.0 126 140 Table 3 Number of wintered and collapsed bee colonies in the apiaries analyzed in 2008-2009 9367 Average number of colonies per apiary 65.9 Range of the number of the colonies per apiary (min-max) 4-595 5439 38.3 3-385 State of apiaries Total Number of colonies in autumn Number of colonies collapsed from autumn to spring Table 4 Level of the V.destructor infestation in the examined samples (colonies) V. destructor Level of infestation per sample (number of mites) Range Mean SD (min-max) Test results Range of level infestation (number of mites per sample) Percentage of samples (n=1000) negative samples n.d. 11.3 0 0 0 31.6 19.1 1.0- 49.0 14.6 positive samples low 1.0 -50.0 high >50.0 57.1 287.5 51.0- 2628.0 310.04 total for positive 88.7 192.0 1.0-628.0 280.42 n.d.= not detected Table 5 Level of the Nosema spp. infestation in the examined samples (colonies) Range of level infestation Test results (number of spores x106 per ml) negative samples Nosema spp. positive samples Percentage of samples (n=1000) Level of infestation per sample (number spores x106 per ml) Range Mean SD (min-max) 0 25.5 0 0 0 low (from 0.01 to 1.0 ) medium (from 1.01 to 5.0) 11.0 0.49 0.01-1.0 0.28 17.5 2.82 1.02-5.00 1.14 high > 5.0 46.1 27.66 5.02-207.37 26.0 Total for positive 74.5 17.8 0.01-207.37 23.3 n.d.= not detected was also low (2.0%). There was a large number of colonies in which the presence of 2, 3 or 4 pathogens were detected. Such samples reached 26.7%, 38.0% and 24.0%, respectively. The presence of Varroa mites and the deformed wing virus was detected most frequently. V. destructor was found in 88.7% of samples, and there were 192 mites per sample, on average. A high infestation level of V. destructor was detected in more than half of the samples (Tab. 4). Nosema spp. infestation was also very frequent (74.6%) and level of infestation was also high. About 46.0% of the samples had more than 5 million spores per milliliter of homogenate, and about 18 million Nosema spores/ml were found, on average, in samples from infected colonies (Tab. 5). The deformed wing virus (DWV) was widespread; 76.1% of colonies were infected. Acute bee paralysis Vol. 55 No. 1 2011 Journal of Apicultural Science 141 Table 6 Relations between pathogen number, level of the V. destructor, level of the Nosema spp. infestation and percentage of dead colonies Parameters of the regression function α = 0.05 Regression Regression Coefficient of Y coefficient constant determination R2 X Number of co-occurring pathogens (from 1 to 6) Level of Percentage of V. destructor infestation (in number of mites per sample) dead colonies Level of Nosema spp. infestation (in mln.spor/ml sample) p-value 1.8716 53.1540 0.0061 0.0014 0.0017 58.1540 0.0004 0.5400 - 0.0311 47.1440 0.0026 0.0220 Table 7 Extent of bee colony losses depending on the co-occurring of different pathogens and level of Varroa destructor and Nosema infection Level of V. destructor infestation ABPV negative Level of Nosema spp. samples = 0 infection positive (number of spores x106/ml) ABPV samples = 1 from 0.01 to 1.0 ≤ 100 mites per sample from 1.01 to 5.0 >5.0 from 0.01 to 1.0 >100 mites per sample from 1.01 to 5.0 >5.0 DWV negative samples =0 DWV positive samples =1 Colony losses (%) 0 0 63.17 ab 1 0 90.80 c 0 1 51.16 a 1 1 61.30 ab 0 0 55.97 a 1 0 68.52 b 0 1 54.85 a 1 1 63.27 ab 0 0 52.87 a 1 0 47.13 a 0 1 57.53 a 1 1 57.65 a 0 0 55.01 a 1 0 75.31 bc 0 1 58.47 a 1 1 75.30 bc 0 0 57.28 a 1 0 88.10 c 0 1 54.18 a 1 1 63.60 ab 0 0 52.68 a 1 0 65.50 b 0 1 55.66 a 1 1 61.00 ab Different letters denote statistically significant differences at α=0.05 142 virus (ABPV) was detected in 35.4% of the colonies, and CBPV in 7.8%. Israeli acute paralysis virus was detected for the first time in Poland, in only 1 colony. Analysis of the relation between pathogens and rate of bee mortality Significant (p=0.014) but poor (r=0.08) relations between the number of detected pathogens and the increase in colony mortality were found. The average numbers of pathogens co-occurring in bee colonies were similar in all analyzed groups. The number of co-occuring pathogens ranged between 2.9 in the case of the apiaries which had lost 30% of their colonies, and 3.2 for apiaries which had lost all of their colonies. Analysis of the relations between V. destructor and Nosema spp infestation and the severity of the colony losses were made. The analysis showed that the increase in dead colony numbers was not connected with the increase in the level of infestation by these parasites. Infestation level of the V. destructor and Nosema spp. did not differ among varying degree of colony losses in apiaries (Tab. 6). The number of DWV infected bee colonies were high in all apiaries and statistical analysis did not reveal an impact of this virus on increasing colony mortality ABPV 1 = positive samples ABPV 0 = negative samples (p-value 0.33). However, a correlation between the presence of ABPV and bee colony losses was found. The increase in the number of colonies infected with this virus was accompanied by the increase in colony mortality (Fig. 1). If the number of pathogens detected in mixed infection had a slight impact on the extent of the colony losses, this was significantly dependent on the type of co-occurring pathogens. We observed a significantly high bee colony mortality for those apiaries where, apart from other photogenes, ABPV was detected (Tab. 7). Analysis of the relationships between the individual pathogens Significant (p<0.001) but poor (r=- 0.15) relationships were found for the level of V. destructor infestation and the level of Nosema spp. infection (Fig. 2). However, a very strong correlation was observed between the level of V. destructor infestation and the infection of bee colonies with DWV. The level of V. destructor infestation was significantly higher for colonies infected with DWV (Fig. 3). This interaction was not found for V. destructor and ABPV infection. The mean number of Varroa mites (185.8 per sample) in colonies with ABPV Fig. 1. Analysis of the relation between the prevalence of ABPV and the extent of bee colony losses (α=0.05, p<0.001). Vol. 55 No. 1 2011 Journal of Apicultural Science Fig. 2. Analysis of the relation between the level of V. destructor (in number of mites per sample) and Nosema spp. (in number of spores x106/ml) infestation (α=0.05). DWV 1 = positive samples DWV 0 = negative samples Fig. 3. Analysis of the relation between the level of V. destructor infestation (in number of mites per sample) and DWV (α=0.05, p=0.01). 143 144 DWV 1 = positive samples DWV 0 = negative samples Fig. 4. Analysis of the relation between the level of Nosema spp. infestation (in number of spores x106/ml) and DWV ((α=0.05, p<0.001). Fig. 5. The extent of bee colony losses in examined apiaries from different provinces of Poland. did not differ significantly from the number of Varroa mites (161.9 per sample) in colonies in which ABPV infection was not detected (p-value=0.18). Similarly, there was no interdependence between V. destructor and CBPV virus infection. The mean number of Varroa mites in colonies with CBPV amounted to 146.2, and the mean number of Varroa mites was 172.4 in colonies where CBPV was not Vol. 55 No. 1 2011 Journal of Apicultural Science present (p-value=0.39). We also did not observe any relationship between the level of Nosema spp. and ABPV or Nosema spp. and CBPV infection. The mean number of Nosema spores (12.2 x 106 per 1 ml) in colonies with ABPV did not differ significantly from the number of parasites (13.9 x106 per 1 ml) in colonies without detected ABPV infection (p-value=0.246). The mean number of Nosema spores in colonies with CBPV amounted to 12.9 x106, and 13.2 x106 in colonies where CBPV was not detected (p-value=0.889). In the case of Nosema spp. infection, only a strong negative relation between this pathogen and DWV was observed. The bee colonies infected with DWV had a significantly lower level of Nosema spp. infection (Fig. 4). Analysis of the extent of colony losses among apiaries from the different regions of Poland The highest rate of overwintering mortalities (above 60%) were observed 145 in 4 apiaries located in the KujawskoPomorskie, Lubelskie, WarmińskoMazurskie and Zachodniopomorskie provinces. In apiaries belonging to the other 7 provinces, losses of bees were also high and amounted to more than half of their bee colonies (Fig. 5). The epizootic status of apiaries from some regions of the country differed significantly. In colonies from the Warmińsko-Mazurskie voivodeship, the level of V. destructor infestation and ABPV infection was significantly higher. In samples from Lubelskie, Świętokrzyskie, Dolnośląskie, Śląskie and Wielkopolskie only the number of V. destructor mites was higher. In apiaries from KujawskoPomorskie and Zachodniopomorskie, where losses of colonies were high, we did not find significant differences in the level of V. destructor, Nosema spp., and virus infections in comparison with provinces where losses were lower (Tab. 8). Table 8 Prevalence of pathogens in colonies from different region of Poland Province V. destructor Nosema spp. ABPV CBPV infestation infection DWV infection infection (mean number (mean number (%infection (% of infected of infected (% of infected of mites/ of spores x colonies) colonies) colonies) 6 sample) 10 /1 ml) Dolnośląskie 157.9 ab 12.6 a 64.2 ab 0.0 86.8 Kujawsko-Pomorskie 65.1 a 9.1 a 66.7 ab 8.3 91.7 Lubelskie 196.9 ab 11.5 a 31.1 a 4.4 80.0 Lubuskie 111.0 a 13.8 a 32.7 a 2.0 63.3 Łódzkie 5.0 a 5.4 a 0.0 a 0.0 100.0 Małopolskie 139.3 a 17.7 a 40.4 a 16.0 65.4 Mazowieckie 135.5 a 8.4 a 22.3 a 5.0 77.7 Opolskie 7.8 a 27.1 ab 50.0 a 0.0 40.0 Podkarpackie 129.9 a 38.6 b 40.0 a 5.7 68.6 Podlaskie 23.2 a 2.0 a 10.0 a 0.0 90.0 Pomorskie 27.9 a 16.5 a 28.6 a 0.0 90.5 Śląskie 176.2 ab 7.5 a 4.2 a 0.0 62.5 Świętokrzyskie 308.0 bc 14.1 a 21.9 a 9.4 78.1 Warmińsko-Mazurskie 471.5 c 10.7 a 100.0 b 10.0 100.0 Wielkopolskie 258.0 bc 8.0 a 37.7 a 5.3 85.1 Zachodniopomorskie 133.8 a 13.5 a 34.9 a 13.4 73.3 Different letters denote statistically significant differences at α=0.05 146 DISCUSSION Our laboratory test results revealed that the epizootic status of the examined apiaries posed a real threat to the functioning of bee colonies and was the main cause of death for most of them. We found a noticeable prevalence of 3 out of the 6 detected pathogens. Our results show the dominant role of Varroa destructor associated with the DWV viral infection and/or Nosema spp., in relation to winter colony losses. The pathological effect of V. destructor on bees is well known, and among other effects, the effect of the V. destructor depends on the rate of the mite infestation of the colonies (Genersch, 2010). We detected Varroa mites in almost all the surveyed colonies. Half of the bee colonies had high infestation levels (on average about 200 parasites per sample). The number of Varroa mites in those colonies probably reached the “critical threshold” which could lead to their death (Delaplane and Hood, 1999). In the case of absence of Varroa destructor, most viruses isolated from honey bees were considered to be non-threatening to the bees. Such viruses mainly caused covert, symptomless infection. DWV and ABPV interactions with V. destructor, transmission of virus particles, and immune suppression of pupae and adult bees, leads to rapid virus replications and outbreaks of viral infection (Yang and Cox-Foster, 2005; van Engelsdorp and Meixner, 2009; Genersch, 2010). Berthoud et al. (2010) reported statistically significant correlations between ABPV and DWV winter mortality of bee colonies. The ABPV and DWV viral loads depended on the health status of colonies and were significantly higher in dead colonies. In Germany (Genersch et al., 2010), the negative impact of DWV and ABPV on winter bee colony mortality has been confirmed by bee monitoring program. Highfield et al. (2009) reported that DWV can potentially act independently of Varroa mites to collapse a bee colony bringing about colony losses. Therefore, DWV may be a major factor in winter losses. ABPV has been found to be associated with dead colonies infested with Varroa mites in Russia and the United States (Allen and Ball, 1996). In our study, the ABPV virus was present in 35% of the dead colonies. Losses were significantly higher in apiaries in which ABPV was found. We detected the spores of the Nosema spp. parasite in 75% of bee samples. The average level of infestation was high and amounted to 18 million spores per bee. The preliminary study of the epidemiological factors related to honey bee colony losses conducted in Spain, showed that colony losses could be caused by Nosema ceranae (Higes et al., 2010), and that Nosema ceranae was more virulent than N. apis. However, regardless of the genus, Nosema spp. was considered to be the cause of winter mortalities when the number of spores was higher than 10 million per bee (Chauzat et al., 2010b). Because over 90% of bee colonies were co-infected it is difficult to clearly define, which of the detected pathogens played a key role in winter mortality of bees. Each of the identified pathogens causes serious detrimental effects on the individual insects and ultimately leads to disturbances in the functioning of bee colonies. Therefore, in co-infection, the synergistic, negative impact of pathogens is observed. Similar results concerning the level of the V. destructor invasion in Polish apiaries, were obtained by Topolska (2008). In studies carried out on samples of dead bees collected from 104 apiaries from various regions of Poland, severe V. destructor infestation, bees with deformed wings, or ABPV infection were detected in 55% of the apiaries. In 32% of the apiaries a severe Nosema spp. infestation was detected. For four years, Chauzat et al. (2010) examined the incidence of infectious agents and parasites in apiaries in which the loss of colonies did not exceed 10%. They reported a lower percentage of colonies infected by V. destructor (20% on average) and Nosema spp. (27%). The numbers were different for beekeepers Vol. 55 No. 1 2011 Journal of Apicultural Science (hives) of various provinces who have high mortality problem in their colonies. This may attest to the fact, that in provinces from which the most samples came from, the problem of mass colony losses affected the larger amount of apiaries. Confirmation of these assumptions are data published by Topolska (2008). The highest losses of bee colonies were found in Lubelskie, Zachodniopomorskie and Wielkopolskie. We also received a large number of samples from them. In some apiaries from these provinces (Wielkopolskie, Śląskie, Świętokrzyskie, Lubelskie) significantly higher levels of the V. destructor infestation were found. CONCLUSION 1. The epizootic status of the examined apiaries suggests that bee pathogens are one of the main factors involved in high mortality of honey bee colonies. 2. Severe colony losses in Polish apiaries could be attributed to high levels of V. destructor infestation with DWV and ABPV viral infection and/or Nosema spp. infection. 147 C ha uz a t M -P., M a rte l A. C ., Ze gga ne S., D ra jnude l P., Sc hurr F., C le me nt M . C ., R ibie re -C ha be rt M ., A ube rt M ., Fa uc on J . P. (2010b) - A case control study and survey on mortalities of honey bee colonies (Apis mellifera) in France during the winter of 2005-6. J. Apic. Res., 49(1): 40-51 C ox-Fos te r D. L., C onla n S., H olme s E. C ., Pa la c ios G ., Eva ns J . D ., M ora n N . A ., Q ua n P. L., B ris e T., H omig M ., G e is e r D . M ., M a rtins on V ., va nEnge ls dorp D ., K a lks te in A . L., D rys da le A ., H ui J ., C iu L., H utc his on S. K ., Simons J . F., Egholm M ., Pe ttis J ., Lipkin W . I. (2007) - A metagenomic survey of microbes in honey bee Colony Collapse Disorder. Science, 318(5848): 283-287. D a hle B . (2010) - The role of Varroa destructor for honey bee colony losses in Norway. J. Apic. Res., 49(1): 124-125. D e la pla ne K . S., H ood W . M . (1999) Economic threshold for Varroa jacobsoni Oud. in the southeastern of USA. Apidologie, 30: 383-395. Alle n M . F . , an d Ba ll B. V . (1996) - The incidence and world distribution of the honey bee viruses. Bee World, 77: 141-162. va nEnge ls dorp D ., M e ixne r M . D . (2009) - A historical review of managed honey bee populations in Europe and United States and the factors that may affect them. J. Invertebr. Pathol., doi 10.1016/j. jip.2009.06.11 B erth o u d H . , Imd o rf A . , H au ete r M ., R ad lo ff S . , N eu man n P . (2010) - Virus infection and winter losses of honey bee colonies (Apis mellifera). J. Apic. Res., 49(1): 60-65. va nEnge ls dorp D ., H a ye s J r. J ., U nde rw ood R . M ., C a ron D ., Pe ttis J . (2010) - A survey of honey bee colony losses in the United States, fall 2008 to spring 2009. J. Apic. Res., 49(1): 7-14. C a rre c k N . L . , B all B. V . , M a rtin S . J . (2010) - Honey bee colony collapse and changes in viral prevalence associated with Varroa destructor. J. Apic. Res., 49(1): 66-71. va nEnge ls dorp D ., H a ye s J r J ., U nde rw ood R . M ., C a ron D ., Pe ttis J . (2011) - A survey of managed honey bee colony losses in the USA, fall 2009 to winter 2010. J. Apic. Res., 50(1): 1-10. REFERENCES C h au za t M. P., Ca rp en ti e r P., M ad ec F . , B o u g e a rd S . , Co u g o ule N ., D rajn u d el P . , C leme n t M. C ., A u b ert M . , F a u co n J . P . (2010a) - The role of infectious agents and parasites in the health of honey bee colonies in France. J. Apic. Res., 49(1): 30-39. G e ne rs c h E. (2010) - Honey bee pathology: current threats to honey bees and beekeeping. Appl. Microbiol. Biotechnol., 87: 87-97. 148 Ge n ers c h E . , v o n d er O h e W . , K a a tz H ., S c h ro e d er A . , O tte n C . , B üc hle r R . , B erg S . , Ritte r W. , G is de r S., M eix n e r M . , L ie b ieg G . Ro s en k ra nz P. (2010) - The German bee monitoring project: a long term study to understand periodically high winter loses of honey bee colonies. Apidologie, Doi10.1051/apido/2010014 Hig h fie ld A . C. , E l N aga r A ., M ac k in d er L . C. M . , N o ël L. M . L. J . , H all M . J . , M artin S. J ., S c h ro e d er D . C . (2009) - Deformed wing virus implicated in overwintering honeybee colony losses. Applied and Environmental Microbiology, 75(22): 7212-7220. Hig es M . , M a rtin -H e rn an d e z R ., B o tia s C., G a rrid o -B ailon E., G o n za le s -P o rto A . V . , Ba rrios L., N o z a l M . J . D . , G a rc ia -P a le nc ia P., M ea n a A . , (2008) - How natural infection by Nosema ceranae causes honey bee colony collapse. Environmental Microbiology, 10: 2659-2669. Hi g e s M . , M a rtin -H e rn an d e z R ., B o tia s C., G a rrid o -B ailon E., G o n za le s -P o rto A. V., G a rc ia P a le n cia P . , M e a n a A . , N o za l M . J . D ., M a y o R . , Be rn al J . L . (2008) - Honey bee colony collapse due to Nosema ceranae in professional apiaries. Environmental Microbiology Reports, 1: 110-113. L e Co n te Y . , E llis M . , Ritte r W. (2010) Varroa mites and honey bee health: can Varroa explain part of the colony losses? Apidologie, 41(3): 353-363. M a rtin S. J ., B a ll B . V ., C a rre c k N . L. (2010) - Prevalence and persistence of deformed wing virus (DWV) in untreated and acaricide-treated Varroa destructor infested honey bee (Apis mellifera) colonies. J. Apic. Res., 49(1): 72-79. N e uma nn P., C a rre c k N . L. (2010) Honey bee colony losses. J. Apic. Res., 49(1): 1-6. Pa xton R . J . (2010) - Does infection by Nosema ceranae cause “Colony Collapse Disorder” in honey bees (Apis mellifera)? J. Apic. Res., 49(1): 80-84. Potts S. G ., R obe rts S. P. M ., D e a n R ., M a rris G ., B row n M . A ., J one s R ., N e uma nn P., Se tte le J . (2010) - Declines of managed honey bees and beekeepers in Europe. J. Apic. Res., 49 (1): 15-22. Topols ka G ., G a jda A ., H a rtw ig A . (2008) - Polish honey bee colony-loss during the winter of 2007/2008. J. Apic. Sci., 52(2): 95-110. Topols ka g., G a jda A ., Pohore c ka K ., B obe r A ., K a s prz a k S., Skubida M ., Se mkiw P. (2010) - Winter colony losses in Poland. J. Apic. Res., 49(1): 126-128. Y a ng X ., C ox-Fos te r D . L. (2005) Impact of an ectoparasite on the immunity and pathology of an invertebrate; evidence for host immunosuppression and viral amplification. Proc. Natl. Acad. Sci. USA 102: 7470-7475. Vol. 55 No. 1 2011 Journal of Apicultural Science 149 STAN EPIZOOTYCZNY PASIEK, W KTÓRYCH WYSTĄPIŁA MASOWA ŚMIERTELNOŚĆ RODZIN PSZCZELICH (2008-2009) Pohorecka K., Bober A., Skubida M., Zdańska D. S t r e s z c z e n i e Celem badań była ocena sytuacji epizootycznej w pasiekach, w których odnotowano masową śmiertelność rodzin pszczelich i określenie roli organizmów patogennych dla pszczół w etiologii tego zjawiska. Badaniami objęto pasieki, w których w okresie jesienno-zimowym zginęło co najmniej 30% rodzin pszczelich. W latach 2008-2009 badaniami objęto około 300 pasiek zlokalizowanych na terenie całego kraju. Największą liczbę pasiek do badania zgłoszono z terenu województwa małopolskiego, lubelskiego, zachodniopomorskiego, mazowieckiego, wielkopolskiego, dolnośląskiego, śląskiego, świętokrzyskiego i lubuskiego. W roku 2008 przebadano próby pochodzące z 265 pasiek, w roku 2009 z 24 pasiek. Materiał do badań laboratoryjnych stanowiły próbki martwych pszczół pobierane przez pszczelarzy w czasie pierwszych wiosennych przeglądów, oddzielnie z kilku-kilkunastu (w zależności od wielkości pasieki) losowo wybranych rodzin pszczelich. Z każdej pasieki, zbierano w formie ankiety dodatkowe informacje niezbędne do późniejszej analizy wyników badań. W celu zwiększenia dokładności analiz laboratoryjnych, badania wykonano na pojedynczych próbkach pszczół. W każdej próbce oznaczano: - obecność roztoczy V. destructor - metodą makroskopową, z uwzględnieniem oznaczenia liczby pasożytów w każdej próbie. - obecności grzybów z rodzaju Nosema spp. - metodą mikroskopową wg Cantwella (1970) w modyfikacji własnej. - obecność wirusów najbardziej patogennych dla pszczół: wirusa chronicznego paraliżu pszczół (CBPV), wirusa ostrego paraliżu pszczół (ABPV), wirusa zdeformowanych skrzydeł (DWV), oraz izraelskiego wirusa ostrego paraliżu pszczół (IAPV) metodą RT-PCR. Analizę statystyczną uzyskanych wyników przeprowadzono łącznie dla 2 lat badań. Do analizy wybrano wyniki tylko z tych pasiek, w których próbki pobrano z co najmniej 5 rodzin, pobrany materiał pozwalał na wykonanie badań we wszystkich kierunkach, a informacje zawarte w ankietach pozwalały ocenić wielkość strat. Ogółem analizę statystyczną przeprowadzono dla danych uzyskanych z badań 1000 próbek (rodzin), które zostały pobrane ze 142 pasiek. W analizowanych pasiekach, w okresie jesienno-zimowym zginęło od 30 do 100% rodzin. Największą grupę stanowiły pasieki, w których straty mieściły się w zakresach od 30 do 40% i od 41 do 50%, w związku z czym, w tej grupie przebadano największą liczbę rodzin. W pozostałych, zwiększających się o 10% przedziałach strat, liczba przebadanych pasiek i rodzin była zbliżona. Ogółem, w pasiekach tych zginęło około 5440 rodzin pszczelich (58,4%), przy czym w zależności od liczebności pasiek, osypywało się w nich od 3 do 385 rodzin, średnio 38 rodzin. W większości badanych rodzin (99,6%) stwierdzono obecność co najmniej jednego spośród oznaczanych patogenów, przy czym w około 90% rodzin były to zakażenia mieszane. Równoczesne zakażenie 2 patogenami wykryto w 26,7% rodzin, trzema - w 38% rodzin, a czterema - w 24% rodzin. Niewielki procent rodzin (2%) był zakażony równocześnie 5 patogenami, a w żadnej z rodzin nie stwierdzono równoczesnej obecności wszystkich sześciu. Inwazję V. destructor stwierdzono w 88,7% rodzin, przy czym w zakażonych próbkach było średnio 192 pasożyty. Wysoki poziom inwazji (>50 roztoczy na próbkę) wykryto w 57% rodzin. Natomiast obecność spor Nosema spp. stwierdzono w 74,5% rodzin, a wysoki poziom inwazji (>5 milionów spor/ml) w 46,1% spośród wszystkich przebadanych rodzin. W próbkach zakażonych rodzin stwierdzono średnio 18 milionów spor/ml. 150 Wśród infekcji wirusowych DWV był obecny w 76,1% rodzin, ABPV w 35,4%, CBPV tylko w 7,8% rodzin. Po raz pierwszy w kraju, w próbce z 1 rodziny pszczelej wyizolowano wirusa IAPV. Nie stwierdzono istotnych zależności pomiędzy liczbą zidentyfikowanych w rodzinach patogenów, a procentem martwych rodzin w pasiekach. Równoczesną obecność średnio 3 patogenów stwierdzano w rodzinach z pasiek o najniższym poziomie strat (30%), jak i w pasiekach, w których ginęły wszystkie rodziny. Rodziny pszczele z pasiek o różnym nasileniu strat nie różniły się także między sobą poziomem inwazji V. destructor, Nosema spp. i obecnością wirusa CBPV i DWV. Stwierdzono natomiast istotną zależność pomiędzy liczbą rodzin zakażonych wirusem ABPV, a ich śmiertelnością. Wzrostowi udziału martwych rodzin towarzyszył wzrost liczby rodzin zakażonych tym wirusem. Analiza zależności pomiędzy badanymi patogenami wykazała bardzo silną zależność pomiędzy poziomem inwazji V. destructor, a występowaniem zakażenia wirusem zdeformowanych skrzydeł (wartość współczynnika determinacji bliska jedności). Wzrost poziomu inwazji V. destructor powodował rozwój tej infekcji wirusowej w rodzinach pszczelich. W przypadku zakażenia Nosema spp. stwierdzono silną, ujemną zależność pomiędzy tym patogenem, a wirusem DWV. W pozostałych analizach nie stwierdzono istotnych zależności pomiędzy badanymi patogenami (poziomem inwazji V. destructor a CBPV, oraz poziomem inwazji Nosema spp. a CBPV i ABPV). Słowa kluczowe: Apis mellifera, straty zimowe, patogeny. Vol. 55 No. 1 2011 Journal of Apicultural Science 151