- Open Access
Nosema spp. infection and its negative effects on honey bees (Apis mellifera iberiensis) at the colony level
© Botías et al.; licensee BioMed Central Ltd. 2013
- Received: 5 September 2012
- Accepted: 25 March 2013
- Published: 10 April 2013
Nosemosis caused by the microsporidia Nosema apis and Nosema ceranae are among the most common pathologies affecting adult honey bees. N. apis infection has been associated with a reduced lifespan of infected bees and increased winter mortality, and its negative impact on colony strength and productivity has been described in several studies. By contrast, when the effects of nosemosis type C, caused by N. ceranae infection, have been analysed at the colony level, these studies have largely focused on collapse as a response to infection without addressing the potential sub-clinical effects on colony strength and productivity. Given the spread and prevalence of N. ceranae worldwide, we set out here to characterize the sub-clinical and clinical signs of N. ceranae infection on colony strength and productivity. We evaluated the evolution of 50 honey bee colonies naturally infected by Nosema (mainly N. ceranae) over a one year period. Under our experimental conditions, N. ceranae infection was highly pathogenic for honey bee colonies, producing significant reductions in colony size, brood rearing and honey production. These deleterious effects at the colony level may affect beekeeping profitability and have serious consequences on pollination. Further research is necessary to identify possible treatments or beekeeping techniques that will limit the rapid spread of this dangerous emerging disease.
- Brood Cell
- Honey Production
- Brood Production
- Drone Brood
- Infected Coloni
Honey bees are key generalist pollinators that live in large perennial colonies, ensuring high levels of local pollination throughout the flowering season. A. mellifera considerably contributes to general crop pollination, the benefits of which are substantially higher than those resulting from honey production . However, it has been reported that, on a global level, honey bees are primarily reared to produce honey and other marketable products and thus, the economics of honey production influence the global dynamics of bee management more than their influence on agricultural and biological pollination [2, 3]. Honey is by far the most common and best known product from honey bee colonies, both from the quantitative and economic point of view [4, 5], and it represents an essential commodity worldwide which adds nutritional variety to human diets . Honey production and trade is a source of finance with global production reaching 1.07 million tonnes in 2007 . In Spain, which has the largest number of bee colonies, the highest honey production and the second largest population of professional beekeepers after Greece from the European Union , honey production is estimated at 31 800 thousand tonnes. Based on the average price of honey in Spain in 2007 (€ 2377 per tonne) , this activity is valued at approximately € 75.7 million. Given these figures, it is clear that any loss in honey production is an important concern for professional beekeepers, particularly in the most productive countries.
Several factors affect honey production in the colony, including weather conditions , the availability of adequate foraging resources  and colony strength (i.e. brood production, size of the adult bee population, worker bee life expectancy and the individual productivity of workers) .
Honey bee parasites and pathogens have also been reported to negatively influence colony productivity [12, 13], and some of the most damaging diseases of adult honey bees are varroosis caused by the mite Varroa destructor[14, 15], and microsporidiosis caused by the spore-forming microsporidia Nosema apis and Nosema ceranae[16–18]. Both these microsporidian species infect the midgut (ventriculus) of the honey bees’ digestive tract, although they cause two different diseases, with distinct epidemiological, clinical and pathological characteristics [5, 19]. Since the relatively recent discovery of N. ceranae infection in A. mellifera, the number of studies analysing the impact of the infection by this microsporidium (namely Nosemosis type C) on honey bees at the individual level has increased markedly [21–24]. The effect of nosemosis type C at the colony level has also been evaluated [17, 25, 26], primarily focussing on the possible colony collapse in response to infection, and disregarding the potential sub-clinical effects on parameters such as colony strength and productivity. Since several studies have described negative impacts of N. apis infection on these colony parameters [27–29], and in the light of the high prevalence of N. ceranae worldwide [19, 30], we sought to identify the clinical and sub-clinical signs of Nosema infection on colony strength and productivity when N. ceranae is the dominant species, which may affect beekeeping profitability and the efficiency of honey bee pollination.
Honey bee colonies
In this study, 50 homogeneous colonies of Apis mellifera iberiensis in the experimental apiaries located at the “Centro Apícola de Marchamalo” (CAR) were monitored monthly from September 2007 to December 2008. Thereafter, the presence/absence of the queen, colony mortality and clinical and sub-clinical sings of any pathology were recorded each month until December 2010. All colonies were acquired as nuclei (5 combs with worker bees and a queen) from the same professional beekeeper in April 2007, and they were left to develop and adapt to the field conditions of the study until June 2007, when they were introduced into the new hives. At the start of the study, neither colony showed clinical signs of chalkbrood, American or European foulbrood. Furthermore, the absence of V. destructor was recognised after examining the bees according to OIE methods  and Nosema spp. was not detected in the colonies when bee samples (n ≥ 30 foragers) were analysed using a specific duplex PCR .
The areas surrounding the hives contained no genetically modified agricultural crops, and no insecticides such as fipronil or imidacloprid were in use.
The colonies were placed close to another apiary containing colonies naturally parasitised by N. ceranae and/or N. apis, which acted as a natural source of infection.
V. destructor parasitisation was controlled twice a year (Apivar® a.m. amitraz) to avoid the negative effects of this parasite on colony health. This experimental research follow the guidelines of the European Medicines Agency and the methods have been approved by the Spanish National Institute for Agricultural and Food Research and Technology (INIA).
Field assay procedure
Chronology of interventions in all colonies (FB = Forager Bees; HB = House Bees; ALL = All groups)
INTERVENTIONS IN THE COLONIES
1 T 2 T 4 T
2 T 4 T
FB collection and PCR analysis of composite samples
FB collection and PCR analysis of individual bee samples
HB collection and PCR analysis of composite samples
HB collection and PCR analysis of individual bee samples
Data collection of adult bee population and brood rearing
Data collection of honey production
Both sugar-syrup and fumagillin were administered in plastic bags placed over the brood chamber and their consumption was assessed weekly . Fumagillin consumption was calculated on the basis of 30 mg fumagillin per 250 mL syrup ingested. On the day a new dose was administered, the remaining unconsumed doses were removed from the colony and weighed.
From September 2007 until December 2010, clinical signs indicative of pathologies other than Nosema disease, the presence of a queen and colony mortality were recorded on each visit to the apiaries (Table 1).
Monitoring of Nosema spp. infection in the experimental colonies
Detection of infection (composite samples)
To evaluate Nosema spp. infection in the colonies, samples of forager bees (n ≥ 30 bees per sample) and house bees (n ≥ 30 bees) were collected at noon, as described previously . Forager bee samples were collected 10 times, approximately once a month, between September 2007 and December 2008 (Table 1). House bee samples were only collected before and after the interventions in autumn 2007 and spring 2008. DNA was extracted from the composite samples collected and PCR was performed as described previously .
Percentage of infected bees before and after interventions
The percentage of worker bees infected by Nosema spp. was also evaluated in each colony before and after the interventions in the autumn 2007 and spring 2008 in order to determine the effect of the different interventions on the evolution of Nosema spp. infection at the beginning of the assay (autumn) and during the period of most activity in the colonies (spring) . Samples of forager bees (n ≥ 20) and house bees (n ≥ 20) were collected from each colony as described above, one week before the first dose of treatment and two weeks after the last dose (Table 1).
For forager bee samples, the percentage of infected bees was determined by individual PCR analysis of the 20 forager bees from each of the studied colonies, following the procedures described in a previous assay .
For house bees, the percentage of infected bees was determined in randomly selected colonies that remained infected after the interventions, using the same laboratory methods described above for forager bees.
The adult bee population and brood production (i.e. uncapped and capped brood) were evaluated throughout the assay (from October 2007 to December 2008, Table 1) by analyzing the frames covered by bees and quantifying the number of brood cells [17, 37]. Both the adult bee population and the number of brood cells were evaluated each month (except for the months of December 2007, and March and September 2008), for a total of 12 measurements.
The proportion of brood cells (NC) to the number of combs covered by bees (P) was also calculated to determine the ratio of brood to bees (NC/P).
The honey production of each colony was evaluated at the harvesting season (September 2008) by separately weighing all the frames with honey from each colony and calculating the total amount of honey stored in them from the difference in comb weight before and after honey extraction . Only those colonies alive at the harvesting season were used for the analysis.
Dependent variables studied were the following: percentage of infected bees, adult honey bee population, number of brood cells, proportion of brood cells per bee combs and honey production. They were normalized with linear transformations. Two factors were taken into account, one fixed factor (group) and the time effect. We ran Generalized Estimation Equations with probability distribution normal, link function identity, subject effect colony and within-subject effect time point.
Since the presence of interaction in the model revealed that the effects of interventions varied with time effect, the mean values of the different parameters (percentage of infected bees, adult honey bee population, number of brood cells and proportion of brood cells per bee combs) were compared per group and time point using a one-way analysis of variance (ANOVA). To evaluate the effect of the interventions in honey production, the mean values recorded from each group at the harvesting season (Sept. 08) were also compared using one-way ANOVA. Where necessary, ANOVA was followed by Bonferroni or Tamhane post hoc tests, depending on the homogeneity of variance in each case (determined using Levene’s test).
To assess the effect of the interventions in the colonies we ran a paired t test comparing the percentage of infected bees before and after interventions both in autumn 07 and in spring 08.
A Student’s t test was used to compare the prevalence of N. apis versus N. ceranae in individual forager bee samples.
In all statistical studies, differences were considered significant when α ≤ 0.05.
The Spearman’s rank correlation test was used to determine the degree of dependence between the percentage of N. ceranae infected bees and: (a) population size; (b) the amount of brood cells; (c) honey production in the corresponding hives; and (d) the amount of fumagillin consumed in the case of treated colonies (groups 1 T, 2 T and 4 T in autumn 2007, and groups 2 T and 4 T in spring 2008). The same analysis was performed with the percentage of N. apis infected bees. These correlations were performed as a function of the percentage of infected bees from November 2007 and July 2008. Correlations were considered significant when α ≤ 0.05 (2-tailed test).
All analyses were carried out using SPSS 18.0 software.
Monitoring of Nosema spp. infection in experimental colonies
Detection of infection (composite samples)
Percentage of infected bees before and after intervention
As for the effect of the treatment against Nosema in each group in autumn 2007, it significantly decreased the proportion of infected foragers in groups 1 T, 2 T and 4 T from October to November (paired t test, P < 0.001). Conversely, the rates of infection tended to increase from October to November in the untreated colonies (groups CS and C: Figure 3), although this effect was not statistically significant (paired t test, P > 0.05).
In May 2008, before the spring intervention in the corresponding colonies, group 2 T had a smaller proportion of infected bees (P < 0.05) than the control CS and C groups. Similarly, in early July, after treatment application in the corresponding groups (i.e. 2 T and 4 T) and syrup supply in group CS, the percentage of infected bees presented significant differences between groups (ANOVA, F = 46.3, P < 0.001), showing an infection rate significantly lower for groups 2 T and 4 T than that registered in control groups CS and C. In the 1 T group that received fumagillin in autumn 2007 but not in spring 2008, we detected a significantly lower proportion of infected bees than in the untreated groups CS (P = 0.001) and C (P = 0.01), although there were significantly more infected bees than in groups 2 T (P < 0.001) and 4 T (P < 0.001: Figure 3, see Additional file 3).
An intra-group evaluation of the percentage of bees infected in spring 2008 revealed a decreasing trend in the 2 T and 4 T groups and an increasing trend in the 1 T, CS and C groups between May and July (Figure 3, see Additional files 3 and 5). However, no significant differences were detected within any of the experimental groups (paired t test, P > 0.05) before or after treatment (2 T and 4 T) or syrup (CS) administration, or in the colonies that received no intervention (1 T and C).
Moreover, in the treated colonies, syrup with fumagillin consumption was inversely proportional to the percentage of Nosema-infected bees (autumn intervention, r = −0.54, P = 0.021; spring intervention, r = −0.69, P < 0.001; Spearman’s rank correlation). In addition, there was a significantly higher prevalence of N. ceranae over N. apis when the two Nosema species were analysed in individual forager bees (Figure 3), both in the autumn (F = 54.9, P < 0.001; Student’s t- test) and in the spring (F = 19.3, P < 0.001, Student’s t- test).
As indicated in the methods, only a small group of colonies that were infected after the composite sample analysis were randomly selected to evaluate the rate of infection. Less than 5% of bees were infected in all the colonies analysed from the treated groups after the intervention in October 2007 and May 2008, except for colony 4 T-6, in which 35% of the bees were infected with N. ceranae after the autumn treatment. In the untreated colonies the levels of infection were in the range of 10% to 30% after the autumn and spring interventions (Figure 2B).
Adult bee population size and brood production
A significant negative correlation was detected between population size and the percentage of N. ceranae infected bees of any colony in July 2008 (r = − 0.57, P = 0.001; Spearman’s rank correlation), while such correlation was not observed in November 2007 (r = − 0.32, P = 0.07; Spearman’s rank correlation). No correlation was found between the percentage of N. apis infected bees and the population size in November 2007 (r = − 0.26; P = 0.12) or July 2008 (r = − 0.14; P = 0.23; Spearman’s rank correlation).
Like the adult bee population, the brood area was larger in the treated groups at several time points during the assay. Initially (October 2007), brood rearing was similar between groups (ANOVA, F = 0.6, P = 0.3), although significant differences appeared in February (ANOVA, F = 4.6, P = 0.003) and April 2008 (ANOVA, F = 5.4, P = 0.001) that were associated with a significant increase in brood cells in the 2 T and 4 T groups as compared with control CS and C groups (Figure 4B, Additional file 6). In May 2008, group C produced significantly less brood than groups 2 T (P = 0.03) and 4 T (P = 0.03), although one month later (June 2008) brood production was only greater in group 2 T with respect to the control groups CS (P = 0.002) and C (P = 0.004). At the end of the trial, in October 2008, group 2 T again contained significantly more brood cells than the control CS (P = 0.01) and C groups (P = 0.007). The brood production in the treated colonies (1 T, 2 T and 4 T) peaked in June, while that of the control colonies CS and C reached its highest level in July (Figure 4B, Additional file 6).
No significant correlation was observed between the proportion of bees parasitised by N. ceranae and the amount of brood cells in November 2007 (r = 0.28, P = 0.11; Spearman’s rank correlation) or July 2008 (r = − 0.19, P = 0.27; Spearman’s rank correlation), as resulted with the proportion of N. apis parasitised bees and the brood in November 2007 (r = 0.34; P = 0.21; Spearman’s rank correlation) or July 2008 (r = − 0.07; P = 0.67; Spearman’s rank correlation). On the contrary, the ratio of brood cells to adult bee combs (NC/P) in July was significantly greater in the control CS and C groups than in the treated groups (ANOVA, F = 6.7, P < 0.001; Figure 4C). By contrast, in August only the CS group exhibited a significantly higher NC/P ratio with respect to groups 1 T (P = 0.004), 2 T (P = 0.03) and 4 T (P = 0.006).
Natural queen supersedure and colony mortality
Only 4 of the 50 colonies underwent natural queen supersedure during the study: 2 colonies in group 1 T (colonies 1 T-6 and 1 T-8), 1 from group 4 T (4 T-9) and 1 from the C group (C-7) in June 2008, while colony C-3 changed its queen in July 2008 (see Additional file 1).
Several colonies died before the end of the study in December 2008. One colony from group 4 T collapsed in February 2008 with signs of chalkbrood disease. Another colony from group 4 T and one of group 1 T died in July and May 2008 respectively after one month producing only drone brood (queenless or laying worker colony; see Additional file 1).
Three CS colonies died in the winter-spring of 2008, one with symptoms of American Foulbrood (AFB) prior to collapse, while no bees remained inside the colony after collapse in the other 2. In group C, 3 colonies died during the same period, 2 of which only produced drone brood before collapse. In these colonies no death or crawling bees were detected around the hives or faecal marks.
In the analyses prior to collapse, all the dead colonies contained a percentage of N. ceranae infected forager bees of over 45% (range 45-95%).
In the period following interventions in the colonies, 2 colonies from the 1 T group collapsed, exhibiting symptoms of AFB in January 2009. Of the untreated colonies, 4 CS and 3 C colonies died between July 2009 and October 2010, leaving no bees in the hive (see Additional file 1). Thus, in December 2010 the percentage of surviving colonies was 70% in group 1 T, 100% in group 2 T, 80% in group 4 T, 30% in group CS and 40% in group C.
The amount of honey produced by each colony in September 2008 was significantly related to the percentage of N. ceranae parasitized bees in the corresponding hives in July 2008 (r = − 0.51, P = 0.002; Spearman’s rank correlation), but not in November 2007 (r = − 0.29, P = 0.09; Spearman’s rank correlation). On the contrary, no correlation was found between the honey production and the percentage of N. apis parasitized bees in November 2007 (r = − 0.28, P = 0.11; Spearman’s rank correlation) or July 2008 (r = − 0.21, P = 0.14; Spearman’s rank correlation).
The colonies that died before the harvesting season (2 colonies from group 4 T, 3 colonies in group CS and 3 colonies from group C) were not considered when calculating the mean honey production of each group (Figure 5B).
In this field study, we confirm the negative influence of Nosema infection on adult honey bee population size and brood production, and we show that when these microsporidia are not controlled, infection provokes a significant decrease in honey production. Since N. ceranae was the dominant species in the infected colonies throughout the study, the observed effects may principally be attributed to this microsporidium. However, although N. apis shows a small prevalence within the infected colonies and was not constantly present in them throughout the assay, a negative effect of this microsporidium over the colonies health cannot be discarded.
The number of adult bees, sealed brood and the amount of honey produced are valuable indicators of hive health . In our experimental conditions, the health status of the colonies was worse when they were highly infected with N. ceranae than when infection was controlled, suggesting that this microsporidium may have deleterious effects at the colony level, as suggested previously [17, 39, 40]. It is also worth mentioning that part of the non-treated colonies died leaving no bees in the hive at the moment of collapse, coinciding with signs described in a preceding study . Therefore, the parameters here presented regarding hive health status, taken together with other recently shown [36, 41, 42], may be considered as sub-clinical signs of nosemosis type C. However, as the number of colonies per group and sample sizes were limited, definitive conclusions cannot be made and the results presented here should be supported by more research.
The percentage of Nosema-infected forager bees is thought to be a potentially useful indicator of the extent of colony infection [12, 17, 43, 44]. The proportion of Nosema- infected forager bees in our colonies revealed significantly stronger infection than in the untreated colonies (groups CS and C) after the autumn and spring interventions, which may account for the observed differences in the fitness parameters like population size, brood production and honey production from those of the treated colonies (groups 1 T, 2 T and 4 T). Moreover, after the spring intervention we detected a significant negative correlation between N. ceranae infection and the size of the worker population, as seen previously [17, 39]. Indeed, there were significantly fewer bee combs in the spring and summer months in the colonies with the strongest N. ceranae infection (groups CS and C). Colony population size depends mainly on the worker bee life span  and as N. ceranae has a negative impact on this parameter in honey bees [21, 45, 46], it probably exerts a direct negative impact on colony size in accordance with our results.
Nosema infection was less prevalent in house bees than in forager bees, as reported previously [17, 35, 47]. Since the probability of acquiring infection is likely to increase with age and novel diseases are more often picked up by foragers, young workers should be less likely to be infected . A direct link has been reported between infection levels in forager and house bees [49, 50], but in the present assay we failed to establish such a correlation as the number of colonies in which the proportion of infected house bees was analysed was very limited. However, a subsequent study suggested that the interior bees may more accurately reflect the infection level within the colony . In our experimental conditions, forager bee infection rates of at least 45% were shown in all the collapsed colonies, while the percentage of infected house bees in collapsed colonies, only measured in colonies CS-7 and 4 T-6, was 20% and 35%, respectively. However, infection levels of 35% were also recorded in house bees in a colony that did not collapse (colony C-3) in July. This particular colony underwent natural queen supersedure in July, which may have subsequently decreased its infection rate and thus, the likelihood of collapse . Yet as the infection rate was not monitored after this time point, this hypothesis could not be corroborated. In colony C-6, which also underwent queen supersedure in June, the infection rate in house bees after one month was lower than that observed in the treated colonies (15%), while the forager bees exhibited a very high level of Nosema infection (75%). Thus, the influence of queen replacement on Nosema infection appears to primarily affect the house bee population, and the foragers to a lesser extent, although again this hypothesis could not be confirmed since infection rates were not subsequently measured.
Brood production was not correlated with infection levels, although less infected colonies had significantly more brood cells than those in highly infected groups at different time points throughout the study, consistent with earlier studies of Nosema- infected colonies [17, 29, 51]. Furthermore, brood production was slower in the untreated groups (groups CS and C), peaking in July, than in groups 1 T, 2 T and 4 T, which began growing earlier and reached maximum levels one month earlier (June).
Adult bee population size and brood production are correlated [39, 52, 53], and as mentioned above, increased bee mortality has been described in N. ceranae- infected bees. The smaller populations observed in strongly infected colonies may therefore reflect a combination of decreased brood rearing and increased forager death in these colonies. Furthermore, thermoregulation and brood food production may be dysregulated in infected colonies with small populations , resulting in reduced brood rearing efficiency . Nurse bees begin to forage precociously in response to high forager death rates [54, 56–58]. While this strategy restores the proportion of foragers in the population, it also shortens the overall lifespan of adult bees [59–61], as well as their effectiveness and resilience as foragers . This strategy also reduces the time each bee can dedicate to colony growth and brood production. Thus, when the rate of brood production is insufficient to replace the forager bees lost due to Nosema infection, the decline of the colony may accelerate [17, 58].
Colonies with high levels of N. ceranae infection throughout the study (groups CS and C) had significantly more brood cells relative to the adult bee population during the summer months (July and August). As the bee colony grows, a decrease in the ratio of brood to bees has been reported previously [53, 63, 64], as observed during the evolution of the colonies with a milder degree of infection here (groups 1 T, 2 T and 4 T). By contrast, strongly infected colonies (groups CS and C) did not grow at the same rate as treated colonies, and they did not experience a similar decrease in the proportion of brood to bees. The higher ratio of brood to bees in severely infected colonies may reflect the increased rearing effort in the colony in an attempt to replace the worker bees lost due to Nosema infection , although further studies will be necessary to confirm this hypothesis.
Since honey production is generally correlated with the number of worker brood cells and the worker population [27, 65], larger colonies tend to store more honey . In addition, nectar foragers from larger colonies visit more flowers on each trip, with a shorter handling time per flower when compared to those from small colonies . However, Nosema may negatively influence the flight ability of infected honey bee foragers [68, 69] and as such, the value of the nectar and pollen resources will depend on the status of the colony . According to our results, colonies with more severe N. ceranae infection, with smaller colonies and brood area, had lower yields of honey, as reported previously for N. apis- infected colonies [12, 51].
Although there was no correlation between N. ceranae infection and variations in colony strength or increased winter mortality in several recent studies [26, 71, 72], in our experimental conditions this microsporidium was very pathogenic to honey bee colonies, as shown by its impact on population size, the amount of brood and honey production. These conflicting findings may reflect differences in the experimental procedures used, as different methods and time points were used when measuring infection, colony strength and other parameters related to colony health. Accordingly, it may be necessary to standardise the procedures to evaluate Nosema infection in honey bee colonies in order to accurately compare the results from different studies and regions, and to better understand the differences in the epidemiology and pathology of this microsporidium worldwide.
The treatment used against Nosema in the present study (Fumidil B®) showed to be successful at temporarily reducing N. ceranae infection levels in the colonies, as demonstrated previously [17, 73], and allowed us to compare the health status of strongly and mildly infected colonies.
Collapsed colonies (2 in group 4 T, 3 in group CS and 3 in group C) exhibited severe N. ceranae infection prior to collapse, consistent with previous reports [17, 74]. The collapse of treated colonies in group 4 T may have occurred due to poor fumagillin consumption and hence, limited efficacy . Alternatively, in-hive conditions in this group may have been severely disturbed due to the administration of fumagillin in the winter time (unlike groups 1 T and 2 T), triggering a deadly infection by this microsporidium. Otherwise, since this group received the treatment more frequently, a negative impact of this molecule over colony health may have occurred , but all these suggestions should be studied more. One of the collapsed colonies of group 4 T was affected by chalkbrood disease, while another colony from the CS group that died exhibited symptoms of foulbrood disease. N. ceranae infection in these colonies may have provoked the outbreaks of stress-related diseases such as chalkbrood  and foulbrood disease. However, the surviving colonies in the CS and C control groups presented high levels of N. ceranae infection throughout the study, remaining alive but undergoing the effects of a chronic disease, as demonstrated by the reduced levels of fitness components such as colony size, brood rearing and honey production.
Despite the remarkable impact of Nosema infection on beekeeping economics [11, 12, 29], this effect is often underestimated by beekeepers . However, in our experimental conditions N. ceranae infection was highly pathogenic to honey bee colonies, as witnessed by sub-clinical signs such as significant decreases in colony size, brood rearing capacity, honey production and, as reported previously [17, 74], a decrease in the rate of survival. The study revealed that the control of Nosema in autumn and spring could be enough to mitigate these negative effects of nosemosis type C on colony health and productivity, which in turn may affect beekeeping profitability and have dramatic consequences on crop pollination and in natural ecosystems. As treatments for Nosema are currently unavailable in many countries, further studies of potential treatments or beekeeping techniques are urgently required to combat the rapid spread of this dangerous emerging disease.
We wish to thank J. Almagro, J. García, J. M. Martínez Llana, E. Garrido Bailón, S. Rodrigo, P. Gaspar, A. Sanz, V. Albendea, A. Cepero, T. Corrales, C. Rogerio, C. Abascal and S. Sagastume for their technical support. This study was funded by the Junta de Comunidades de Castilla-La Mancha (Consejería de Agricultura y Medio Ambiente and Consejería de Educación), the Ministerio de Agricultura, Medio Rural y Marino (API/FEGA-MAPYA funds and Plan Apícola Nacional 2011–2013) and INIA (RTA-2009-000105-C02-01-FEDER Funds). INCRECYT FEDER funds.
- Food and Agriculture Organization of the United Nations (FAO): Tools for conservation and use of pollination services. Economic valuation of pollination services: review of methods. 2006, Rome: FAO Agriculture Department, Seed and Plant Genetic Resources Division (AGPS)Google Scholar
- Aizen MA, Harder LD: The global stock of domesticated honey bees is growing slower than agricultural demand for pollination. Curr Biol. 2009, 19: 915-918. 10.1016/j.cub.2009.03.071.View ArticlePubMedGoogle Scholar
- Bradbear N: Bees and their role in forest livelihoods. A guide to the services provided by bees and the sustainable harvesting, processing and marketing of their products. 2009, Rome: Food and Agriculture Organization of the United Nations (FAO)Google Scholar
- Hill DB: Proceedings of the North American Conference On Enterprise Development Through Agroforestry. Farming the Agroforest for Specialty Products: October 1998. Pollination and honey production in the forest and agroforest. 1998, St. Paul, Minnesota, Minneapolis: Center for Integrated Natural Resources and Agricultural Management, University of Minnesota, 133-138.Google Scholar
- Mutinelli F: The spread of pathogens through trade in honey bees and their products (including queen bees and semen): overview and recent developments. Rev Sci Tech. 2011, 30: 257-271.PubMedGoogle Scholar
- Food and Agriculture Organization of the United Nations (FAO): FAOSTAT. 2009,http://goo.gl/UmUj6,Google Scholar
- Ministerio de Medio Ambiente y Medio Rural y Marino (MARM): El Sector de la Miel en Cifras. Principales Indicadores Económicos en 2010. 2011, Subdirección General de Productos Ganaderos,http://goo.gl/LoSHz,Google Scholar
- Ministerio de Medio Ambiente y Medio Rural y Marino (MARM): Anuario de estadística 2006–2007. 2007, Capítulo 24,http://goo.gl/7Q0eH,Google Scholar
- van Engelsdorp D, Meixner MD: A historical review of managed honey bee populations in Europe and the United States and the factors that may affect them. J Invertebr Pathol. 2010, 103: S80-S95.View ArticleGoogle Scholar
- Naug D: Nutritional stress due to habitat loss may explain recent honeybee colony collapses. Biol Conserv. 2009, 142: 2369-2372. 10.1016/j.biocon.2009.04.007.View ArticleGoogle Scholar
- Woyke J: Correlations and interactions between population, length of worker life and honey production by honeybees in a temperate region. J Apicult Res. 1984, 23: 148-156.Google Scholar
- Fries I, Ekbohm G, Villumstad E: Nosema apis, sampling techniques and honey yield. J Apicult Res. 1984, 23: 102-105.Google Scholar
- Murilhas AM: Varroa destructor infestation impact on Apis mellifera carnica capped worker brood production, bee population and honey storage in a Mediterranean climate. Apidologie. 2002, 33: 271-281. 10.1051/apido:2002013.View ArticleGoogle Scholar
- Le Conte Y, Ellis M, Ritter W: Varroa mites and honey bee health: can Varroa explain part of the colony losses?. Apidologie. 2010, 41: 353-363. 10.1051/apido/2010017.View ArticleGoogle Scholar
- Rosenkranz P, Aumeier P, Ziegelmann B: Biology and control of Varroa destructor. J Invertebr Pathol. 2010, 103: S96-S119.View ArticlePubMedGoogle Scholar
- Sanford MT: Diseases and pests of the honey Bee. Circular 766. Edited by: Florida Cooperative Extension Service. Institute of Food and Agricultural Sciences. 1987, Gainesville FL: University of Florida, 32611-Google Scholar
- Higes M, Martín-Hernández R, Botías C, Garrido-Bailón E, González-Porto AV, Barrios L, del Nozal MJ, Bernal JL, Jiménez JJ, García-Palencia P, Meana A: How natural infection by Nosema ceranae causes honey bee colony collapse. Environ Microbiol. 2008, 10: 2659-2669. 10.1111/j.1462-2920.2008.01687.x.View ArticlePubMedGoogle Scholar
- Heintz C, Ribotto M, Ellis M, Delaplane K: Best management practices (BMPs) for beekeepers pollinating California’s agricultural crops. 2011, Culture: Managed Pollinator CAP Coordinated Agriculture Project. Bee, 17-19.Google Scholar
- Higes M, Martín-Hernández R, Meana A: Nosema ceranae in Europe: an emergent type C nosemosis. Apidologie. 2010, 41: 375-392. 10.1051/apido/2010019.View ArticleGoogle Scholar
- Higes M, Martín R, Meana A: Nosema ceranae, a new microsporidian parasite in honeybees in Europe. J Invertebr Pathol. 2006, 92: 93-95. 10.1016/j.jip.2006.02.005.View ArticlePubMedGoogle Scholar
- Paxton RJ, Klee J, Korpela S, Fries I: Nosema ceranae has infected Apis mellifera since at least 1998 and may be more virulent than Nosema apis. Apidologie. 2007, 38: 558-565. 10.1051/apido:2007037.View ArticleGoogle Scholar
- Dussaubat C, Brunet J-L, Higes M, Colbourne JK, Lopez J, Choi J-H, Martín-Hernández R, Botías C, Cousin M, McDonnell C, Bonnet M, Belzunces LP, Moritz RFA, Le Conte Y, Alaux C: Gut pathology and responses to the microsporidium Nosema ceranae in the honey bee Apis mellifera. PLoS One. 2012, 7: e37017-10.1371/journal.pone.0037017.PubMed CentralView ArticlePubMedGoogle Scholar
- Martín-Hernández R, Botías C, Barrios L, Martínez-Salvador A, Meana A, Mayack C, Higes M: Comparison of the energetic stress associated with experimental Nosema ceranae and Nosema apis infection of honeybees (Apis mellifera). Parasitol Res. 2011, 109: 605-612. 10.1007/s00436-011-2292-9.View ArticlePubMedGoogle Scholar
- Vidau C, Diogon M, Aufauvre J, Fontbonne R, Viguès B, Brunet JL, Texier C, Biron DG, Blot N, El Alaoui H, Belzunces LP, Delbac F: Exposure to sublethal doses of fipronil and thiacloprid highly increases mortality of honeybees previously infected by Nosema ceranae. PLoS One. 2011, 6: e21550-10.1371/journal.pone.0021550.PubMed CentralView ArticlePubMedGoogle Scholar
- Genersch E, von der Ohe W, Kaatz H, Schroeder A, Otten C, Büchler R, Berg S, Ritter W, Mühlen W, Gisder S, Meixner M, Liebig G, Rosenkranz P: The German bee monitoring project: a long term study to understand periodically high winter losses of honey bee colonies. Apidologie. 2010, 41: 332-352. 10.1051/apido/2010014.View ArticleGoogle Scholar
- Gisder S, Hedtke K, Möckel N, Frielitz MC, Linde A, Genersch E: Five-year cohort study of Nosema spp. in Germany: does climate shape virulence and assertiveness of Nosema ceranae?. Appl Environ Microbiol. 2010, 76: 3032-3038. 10.1128/AEM.03097-09.PubMed CentralView ArticlePubMedGoogle Scholar
- Fries I: Comb replacement and Nosema disease (Nosema apis Z.) in honey bee colonies. Apidologie. 1998, 19: 343-354.View ArticleGoogle Scholar
- Anderson DL, Giacon H: Reduced pollen collection by honey bee (Hymenoptera, Apidae) colonies infected with Nosema apis and sacbrood virus. J Econ Entomol. 1992, 85: 47-51.View ArticleGoogle Scholar
- Farrar CL: Nosema losses in package bees as related to queen supersedure and honey yields. J Econ Entomol. 1947, 40: 333-338.View ArticlePubMedGoogle Scholar
- Fries I: Nosema ceranae in European honey bees (Apis mellifera). J Invertebr Pathol. 2010, 103: S73-S79.View ArticlePubMedGoogle Scholar
- Office International des Epizooties (OIE): Manual of standards for diagnostic test and vaccines. 2004, Paris: OIE, 5Google Scholar
- Martín-Hernández R, Meana A, Prieto L, Martínez-Salvador A, Garrido-Bailón E, Higes M: Outcome of colonization of Apis mellifera by Nosema ceranae. Appl Environ Microbiol. 2007, 73: 6331-6338. 10.1128/AEM.00270-07.PubMed CentralView ArticlePubMedGoogle Scholar
- Higes M, Nozal MJ, Álvaro A, Barrios L, Meana A, Martín-Hernández R, Bernal JL, Bernal J: The stability and effectiveness of fumagillin in controlling Nosema ceranae (Microsporidia) infection in honey bees (Apis mellifera) under laboratory and field conditions. Apidologie. 2011, 42: 364-377. 10.1007/s13592-011-0003-2.View ArticleGoogle Scholar
- Meana A, Martín-Hernández R, Higes M: The reliability of spore counts to diagnose Nosema ceranae infections in honey bees. J Apicult Res Bee World. 2010, 49: 212-214. 10.3896/IBRA.18.104.22.168.View ArticleGoogle Scholar
- Martín-Hernández R, Botías C, Garrido-Bailón E, Martínez-Salvador A, Prieto L, Meana A, Higes M: Microsporidia infecting Apis mellifera: coexistence or competition. Is Nosema ceranae replacing Nosema apis?. Environ Microbiol. 2012, 14: 2127-2138. 10.1111/j.1462-2920.2011.02645.x.View ArticlePubMedGoogle Scholar
- Botías C, Martín-Hernández R, Días J, García-Palencia P, Matabuena M, Juarranz A, Barrios L, Meana A, Nanetti A, Higes M: The effect of induced queen replacement on Nosema spp. infection in honey bee (Apis mellifera iberiensis) colonies. Environ Microbiol. 2012, 14: 845-859. 10.1111/j.1462-2920.2011.02647.x.View ArticlePubMedGoogle Scholar
- Higes M, Meana A, Suárez M, Llorente J: Negative long-term effects on bee colonies treated with oxalic acid against Varroa jacobsoni Oud. Apidologie. 1999, 30: 289-292. 10.1051/apido:19990404.View ArticleGoogle Scholar
- Meikle WG, Mercadier G, Holst N, Nansen C, Girod V: Impact of a treatment of Beauveria bassiana (Deuteromycota: Hyphomycetes) on honeybee (Apis mellifera) colony health and on Varroa destructor mites (Acari: Varroidae). Apidologie. 2008, 39: 247-259. 10.1051/apido:2007057.View ArticleGoogle Scholar
- Soroker V, Hetzroni A, Yakobson B, David D, David A, Voet H, Slabezki Y, Efrat H, Levski S, Kamer Y, Klinberg E, Zioni N, Inbar S, Chejanovsky N: Evaluation of colony losses in Israel in relation to the incidence of pathogens and pests. Apidologie. 2011, 42: 192-199. 10.1051/apido/2010047.View ArticleGoogle Scholar
- Eischen FA, Graham RH, Rivera R: Proceedings of the 2012 American Bee Research Conference: 7–8 February 2012. Impact of Nosema ceranae on honey bee colonies: A 14 month study. 2012, Greenbelt MD: American Bee Journal (Dadant Corporate Offices, Hamilton, IL), 6-7.Google Scholar
- Botías C, Martín-Hernández R, Barrios L, Garrido-Bailón E, Nanetti A, Meana A, Higes M: Nosema spp. parasitization decreases the effectiveness of acaricide strips (Apivar®) in treating varroosis of honey bee (Apis mellifera iberiensis) colonies. Environ Microbiol Rep. 2011, 4: 57-65.View ArticlePubMedGoogle Scholar
- Hedtke K, Jensen PM, Jensen AB, Genersch E: Evidence for emerging parasites and pathogens influencing outbreaks of stress-related diseases like chalkbrood. J Invertebr Pathol. 2011, 108: 167-173. 10.1016/j.jip.2011.08.006.View ArticlePubMedGoogle Scholar
- Doull KM: The effects of time of day and method of sampling on the determination of Nosema disease in beehives. J Invertebr Pathol. 1965, 7: 1-4. 10.1016/0022-2011(65)90143-6.View ArticleGoogle Scholar
- Pickard PS, El-Shemy AAM: Seasonal variation in the infection of honeybee colonies with Nosema apis Zander. J Apicult Res. 1989, 28: 93-100.Google Scholar
- Higes M, García-Palencia P, Martín-Hernández R, Meana A: Experimental infection of Apis mellifera honey bees with the Microsporidia Nosema ceranae. J Invertebr Pathol. 2007, 94: 211-217. 10.1016/j.jip.2006.11.001.View ArticlePubMedGoogle Scholar
- García-Palencia P, Martín-Hernández R, González-Porto AV, Marín P, Meana A, Higes M: Natural infection by Nosema ceranae causes similar lesions as in experimentally infected caged-workers honey bees (Apis mellifera). J Apicult Res. 2010, 49: 278-283. 10.3896/IBRA.1.49.3.08.View ArticleGoogle Scholar
- Smart MD, Sheppard WS: Nosema ceranae in age cohorts of the western honey bee (Apis mellifera). J Invertebr Pathol. 2012, 109: 148-151. 10.1016/j.jip.2011.09.009.View ArticlePubMedGoogle Scholar
- Schmid-Hempel P: Infection and colony variability in social insects. Phil Trans R Soc Lond B. 1994, 346: 313-321. 10.1098/rstb.1994.0148.View ArticleGoogle Scholar
- Gajda A: Proceedings of the COLOSS Workshop, Nosema disease, lack of knowledge and work standardization: 19–22 October 2009. The size of bee sample for investigation of Nosema sp. infection level in honey bee colony. 2009, Guadalajara: FA COST Action FA0803 Prevention of honeybee Colony Losses (COLOSS research network), 23-Google Scholar
- Traver BE, Williams MR, Fell RD: Comparison of within hive sampling and seasonal activity of Nosema ceranae in honey bee colonies. J Invertebr Pathol. 2011, 109: 187-193.View ArticlePubMedGoogle Scholar
- Yücel B, Dogaroglu M: The impact of Nosema apis Z. infestation of honey bee (Apis mellifera L.) colonies after using different treatment methods and their effects on the population levels of workers and honey production on consecutive years. Pak J Biol Sci. 2005, 8: 1142-1145.View ArticleGoogle Scholar
- Moeller FE: The relation between egg-laying capacity of queen bee and population and honey production of their colonies. Am Bee J. 1958, 98: 401-402.Google Scholar
- Free JB, Racey PA: The effect of the size of honeybee colonies on food consumption, brood rearing and the longevity of the bees during winter. Entomol Exp Appl. 1968, 11: 241-249. 10.1111/j.1570-7458.1968.tb02048.x.View ArticleGoogle Scholar
- Wang DI, Moeller FE: The division of labor and queen attendance behaviour of Nosema infected worker honeybees. J Econ Entomol. 1970, 63: 1539-1541.View ArticleGoogle Scholar
- Medrzycki P, Sgolastra F, Bortolotti L, Bogo G, Tosi S, Padovani E, Porrini C, Sabatini AG: Influence of brood rearing temperature on honey bee development and susceptibility to poisoning by pesticides. J Apicult Res. 2010, 49: 52-59. 10.3896/IBRA.1.49.1.07.View ArticleGoogle Scholar
- Winston ML, Ferguson LA: The effect of worker loss on temporal caste structure in colonies of the honeybee (Apis mellifera L.). Can J Zoolog. 1985, 63: 777-780. 10.1139/z85-113.View ArticleGoogle Scholar
- Huang ZY, Robinson GE: Regulation of honey bee division of labor by colony age demography. Behav Ecol Sociobiol. 1996, 39: 147-158. 10.1007/s002650050276.View ArticleGoogle Scholar
- Khoury DS, Myerscough MR, Barron AB: A quantitative model of honey Bee colony population dynamics. PLoS One. 2011, 6: e18491-10.1371/journal.pone.0018491.PubMed CentralView ArticlePubMedGoogle Scholar
- Neukirch A: Dependence of the life span of the honeybee (Apis mellifica) upon flight performance and energy consumption. J Comp Physiol. 1982, 146: 35-40.View ArticleGoogle Scholar
- Schmid-Hempel P, Wolf RJ: Foraging effort and life span in workers of social insects. J Anim Ecol. 1988, 57: 509-522. 10.2307/4921.View ArticleGoogle Scholar
- Wolf TJ, Schmid-Hempel P: Extra loads and foraging life-span in honeybee workers. J Anim Ecol. 1989, 58: 943-954. 10.2307/5134.View ArticleGoogle Scholar
- Oskay D: PhD thesis. Plasticity in flight muscle development and honey bee division of labor. 2007, Río Piedras, Puerto Rico: University of Puerto Rico, Department of Biology, Faculty of Natural ScienceGoogle Scholar
- Farrar CL: 51st–52nd Annual Report of the Beekeepers’ Association of the Province of Ontario, 1930 and 1931. The influence of the colony’s strength on brood-rearing. 1932, Ontario: Department of Agriculture, 126-130.Google Scholar
- Moeller FE: The relationship between colony populations and honey production as affected by honey bee stock lines. Prod Res Rep U.S. Dept Agric. 1961, 55: 20-Google Scholar
- Szabo TI, Lefkovitch LP: Effect of brood production and population size on honey production of honeybee colonies in Alberta, Canada. Apidologie. 1989, 20: 157-163. 10.1051/apido:19890206.View ArticleGoogle Scholar
- Eckert CD, Winston ML, Ydenberg RC: The relationship between population size, amount of brood, and individual foraging behaviour in the honey bee, Apis mellifera L. Oecologia. 1994, 97: 248-255. 10.1007/BF00323157.View ArticleGoogle Scholar
- Wolf TJ, Schmid-Hempel P: On the integration of individual foraging strategies with colony ergonomics in social insects: Nectar-collection in honeybees. Behav Ecol Sociobiol. 1990, 27: 103-111. 10.1007/BF00168453.View ArticleGoogle Scholar
- Krajl J, Fuchs S: Nosema sp. influences flight behavior of infected honey bee (Apis mellifera) foragers. Apidologie. 2010, 41: 21-28. 10.1051/apido/2009046.View ArticleGoogle Scholar
- Mayack C, Naug D: Parasitic infection leads to decline in hemolymph sugar levels in honeybee foragers. J Insect Physiol. 2010, 56: 1572-1575. 10.1016/j.jinsphys.2010.05.016.View ArticlePubMedGoogle Scholar
- Schmid-Hempel P, Winston ML, Ydenberg RC: Foraging of individual workers in relation to colony state in the social Hymenoptera. Can Entomol. 1993, 125: 129-160. 10.4039/Ent125129-1.View ArticleGoogle Scholar
- Williams GR, Shutler D, Little CM, Burgher-Maclellan KL, Rogers REL: The microsporidian Nosema ceranae, the antibiotic Fumagilin-B®, and western honey bee (Apis mellifera) colony strength. Apidologie. in pressGoogle Scholar
- Stevanovic J, Stanimirovic Z, Genersch E, Kovacevic SR, Ljubenkovic J, Radakovic M, Aleksic N: Dominance of Nosema ceranae in honey bees in the Balkan countries in the absence of symptoms of colony collapse disorder. Apidologie. 2011, 42: 49-58. 10.1051/apido/2010034.View ArticleGoogle Scholar
- Williams GR, Sampson MA, Shutler D, Rogers REL: Does fumagillin control the recently detected invasive parasite Nosema ceranae in western honey bees (Apis mellifera)?. J Invertebr Pathol. 2008, 99: 342-344. 10.1016/j.jip.2008.04.005.View ArticlePubMedGoogle Scholar
- Higes M, Martín-Hernández R, Garrido-Bailón E, González-Porto AV, García-Palencia P, Meana A, del Nozal MJ, Mayo R, Bernal JL: Honey bee colony collapse due to Nosema ceranae in profesional apiaries. Environ Microbiol Rep. 2009, 1: 110-113. 10.1111/j.1758-2229.2009.00014.x.View ArticlePubMedGoogle Scholar
- Topolska G, Hartwig A: Diagnosis of Nosema apis Infection by investigations of two kinds of samples: dead bees and live bees. J Apicult Sci. 2005, 49: 75-79.Google Scholar
This article is published under license to BioMed Central Ltd. This is an Open Access article distributed under the terms of the Creative Commons Attribution License (http://creativecommons.org/licenses/by/2.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.