Effects of Exposure to Multiple Agrochemicals in Honeybees (Apis mellifera) Tommaso Ignesti Page 1 of 29 Abstract The Honeybee (Apis mellifera) is one of the most economically and environmentally valuable pollinators today. Beekeepers have often been threatened by periodic high colony losses, but the ability to attribute them to specific practices or pathogens and parasites has allowed for the mitigation of such losses fairly efficiently and quickly. However, this has not been the case with the more recent losses that have decimated North American and European apiaries since 2006. The phenomenon has been named Colony Collapse Disorder and it differs from previously described losses in that it is characterized by the unexplained disappearance of large numbers of individuals from seemingly healthy hives. In this study it was hypothesized that an increased mortality is expected as the number of agrochemicals to which individuals are exposed increases. Data on colony losses and pesticide use was gathered for 49 Californian counties, and a correlation analysis performed. A significance of 0.086 suggested that a moderate relationship could be demonstrated, meaning that the threat posed by pesticides to honeybees is expected to rise as the variety of these pesticides is increased, possibly due to synergism. In light of such results, further investigation of the problem is recommended, and the development of a better understanding of the impacts of sublethal doses of pesticides on honeybees, as well as of the ways these interact to possibly increase their toxicity to beneficial species is necessary. Introduction Perhaps one of the properties of honeybees that have given them worldwide fame is their ability to produce honey, a widely enjoyed sweetener used by human beings since the time of the Ancient Egyptian Civilizations. Honey production is only one of the services provided by bees, and this currently amounts to an estimated value of $1.25 billion worldwide (vanEngelsdorp, 2009). Although this is not at all insignificant, the most essential role of honeybees is that of pollinators of a great variety of plants. Not only are these insects required for the reproduction, and thus survival of a number of species in the wild, they also play a fundamental role in modern agriculture. “Fifty two of the 115 leading global food commodities depend on honeybee pollination,” a few of which would experience a 90% or greater yield reduction in their absence (Klein et al., 2007 as found in vanEngelsdorp, 2009). It is consequently estimated that the annual value of agricultural bee pollination Page 2 of 29 worldwide approximates $212 billion (9.5% of total agricultural value), $15-‐20 billion of which is in the United States alone (vanEngelsdorp et al., 2009). Honeybee Ecology The genus Apis includes a total of 10 species found throughout the world in a variety of climatic regions (Le Conte, 2008). This study focuses on Apis mellifera, the European honeybee, whose importance is not only limited to honey production, but extends especially to its role as natural pollinator of both human raised crops and a variety of wild plant species. The domestication of the European honeybee traces back to the Ancient Egyptians for whom honey was the only sweetener available, and was subsequently transferred to Greek and Roman civilizations, until it eventually spread throughout the world (Ransome, 1937). This domestication, as Crane (1975) has pointed out, can be compared in magnitude to that of the dog, as both accompanied man since the first major migrations (Crane, 1975). On the other hand, the remaining nine species of the Apis genus have for the most part remained in Asia, where the genus is thought to have originated (Le Conte, 2008). What differentiated A. mellifera from other species of the Apis genus was the evolution of a total of 22 subspecies that stemmed from various waves of colonization to parts of Europe, Africa, the Middle East, and Russia. Unlike the Asian species, the western honeybees were thus often subject to cold winters and had to develop strategies to survive colder periods. This was done by the accumulation and storage of sufficient amounts of food to sustain the colony when flowers were not blooming, and thus a greater amount of work was required throughout the year, and the supplemental source of nutrition had to be stored in the form of honey. Colony Structure Honeybees organize in colonies, each including one queen, 20 to 80 thousand females, and a few hundred males, or drones. Males only live for a few weeks in the summer, their only role being mating with the queen in a phenomenon called swarming. In swarming the queen leaves the hive with half the colony, mates, and relocates to a new hive, while a new queen will emerge in the previous one, swarm, and return to the same hive where she will start laying eggs. The queen usually stores enough sperm within her abdomen to last for about 2 years of constant egg Page 3 of 29 laying, after which swarming and relocation will take place. The queen has the ability to either fertilize an egg before laying it, thus producing a female worker bee, or lay an unfertilized egg, which will result in a drone. Each egg is laid in a cell within the hive, although new queens might accidentally lay more than one per cell, and the larva will feed on food provided by adult workers, grow, and undergo pupation within the cell. The cell is capped by an adult worker and will be uncapped by the emerging young bee. This developmental process will take, on average, two to three weeks (https://agdev.anr.udel.edu/maarec/honey-‐bee-‐biology/the-‐colony-‐ and-‐its-‐organization/). The totality of the work needed for the proper functioning and survival of the colony, with the exception of mating and egg production, is carried out by worker bees, which are sterile females. Their tasks depend on both age and the time of year. For the first few days after emerging, bees stand still within the hive and are fed by others. A special kind of glands will activate after a few days which is used to produce brood food, and the young workers will use these to feed developing larvae. Once these glands stop functioning properly, wax-‐producing glands will have developed, and they begin their tasks of hive building and maintenance, together with taking the first journeys outside the hive during which individuals learn the location of the hive and get accustomed to the surroundings. Before becoming foragers, workers within the hive will also aid in the collection and storage of pollen and nectar from incoming foragers, and in the production of honey. Finally, about three weeks after emerging from their original cell, the workers will be ready do serve as foragers, leaving the hive during the day for food and water collection unceasingly, until they die within the next three weeks (http://www.biology-‐ resources.com/bee-‐01.html). During the coldest months of the year the colony will stop its usual activities. At this time a sufficient amount of food will be stored and the drones will be forced out of the colony as to reduce the amount of food that will be consumed during the winter. As temperatures drop, cracks within the hive are sealed, and the entrance tightened as to minimize the amount of in-‐coming cold air. As the temperature within the hive should not drop below 32°C, adult workers form a tight cluster Page 4 of 29 around brood cells and the queen, regulating the temperature using their body heat. The cluster will be tighter or looser according to outside temperature, and will move during warmer moments as to always be within reach of honey supplies. In this period the older bees progressively die, and by late winter the hive will almost entirely consist of young individuals. As days become longer, and temperature rise, the queen begins laying eggs anew, and the population is normally restored within the following months. (Information from Mid-‐Atlantic Apiculture, British Beekeepers’ Association, Biology Teaching and Learning Resources websites) The colony structure of honeybees is worth mentioning not only because of its fascinating complexity, but because it will also help in understanding how certain factors that will be discussed later might be contributing in the Colony Collapse Disorder phenomenon that will be investigated in this thesis. Colony Collapse Disorder Colony losses have not been an uncommon phenomenon throughout history, and a number of instances have been documented starting in 1896. At the same time, large increases in bee populations have been experienced elsewhere which often were more substantial than decreases. Fluctuations have thus been affecting different continents in different ways, and even within each continent there has been high variation from one region to the next. In the past 50 years for instance, the global bee stock has increased by an estimated 45% (Aizen and Harder, 2009). Although this may be considered a positive fact, managed honeybee populations in North America and Europe have declined by 49.5% and 26.5% respectively (vanEngelsdorp, 2009). At the same time the demand for pollinators for agricultural needs has seen a 300% increase or greater (Aizen and Harder, 2009). Even more alarming is the impact of a fairly new condition, named Colony Collapse Disorder, which since 2006 has caused substantial losses in North American apiaries, mostly in those found within the United States. Colony Collapse Disorder (CCD) has been the object of detailed investigation and although a definite cause has not yet been isolated, those characters that seem to be common of all hives affected by the condition have been well described. These are: (1) “Rapid losses of adult worker bees from affected colonies as evidenced by Page 5 of 29 weak or dead colonies with excess brood populations relative to adult bee populations,” (2) “Noticeable lack of dead worker bees both within and surrounding the affected hive,” (3) and “Delayed invasion of hive pests and kleptoparasitism from neighboring honey bee colonies.” (vanEngelsdorp, 2009) Kleptoparasitism refers to the practice of stealing previously gathered or prepared food from another organism. Thus, in affected hives a small cluster of adult bees and the queen are present, and honey and pollen are not missing (Johnson, 2010). While the condition might not seem particularly alarming, the colony structure is modified to such an extent that makes it impossible for the remaining individuals to both fight diseases and pest invasions, and to carry out those activities required for their survival, including food collection and storage, rearing larvae, and survive unexpected drops in temperature. One of the main reasons CCD has become an alarming issue not only for beekeepers, but for scientists and politicians also, is that it differs in some significant ways from previous incidences of colony losses, and while remaining for the most part unknown, its causes seem to have coincided with the significant changes caused by an expanding global economy. The major difference between past colony losses and CCD is that for the former clear causes had been evident and clearly detected through scientific inquiry. These included increasing number of pests, parasites, diseases, habitat losses, reduction in pollen and nectar availability, and exposure to toxic pesticides (Johnson, 2010). In contrast, a correlation between any of these factors and current losses has not yet been found for CCD even though substantial studies have been done. Furthermore, the disorder has coincided with the radical agricultural changes driven by the fast increase in human population and the development of a global economy. This led to a significant modification of the habitat honeybees are exposed to both because of the increasing ease with which non-‐native species are carried from place to place, and because of the implementation of poorly understood agricultural practices focused on increasing productivity, including the introduction of genetically engineered crops and an expanding arsenal of agrochemicals (Johnson et al., 2010). Page 6 of 29 Because no single cause has been isolated in studies on CCD to date, scientists were led to believe that a number of factors are acting simultaneously and contributing in the losses. These include both pathogenic factors such as diseases and pests, as well as non-‐disease factors such as pesticide exposure, genetically modified organisms, and climate change. The Threats and Their Origins It should be clear that the environment to which bees are exposed has a substantial impact on their ability to perform well. In addition, the effects of environmental changes on honeybee populations become threatening relatively fast, despite beekeepers’ attempts to moderate them. This can largely be explained by the colony being an organism onto itself which relies on the delicate interaction of a multitude of individual parts governed by a variety of behaviors. These behaviors are not merely the individual’s reactions to its environment as driven by its own needs. Rather, individuals understand themselves as necessary components of a colony, understand the needs of the colony as their own, and their behaviors are governed by the colony’s needs. As a result, a colony can survive only because, and as long as these behaviors are not radically modified. Behavioral modifications can either be due to the physical unsuitability of the individual, as when a failure to perform foraging activities is determined by the malfunctioning of the wings and therefore an inability to fly, or to cognitive impairment, as when an individual fails to return to the hive due to memory loss, or when an individual fails to recognize its role within the colony. Both physical suitability and cognitive functions are in turn largely influenced by both biotic and abiotic factors present within the colony’s environment, and the threat they pose to the species will be related to the degree by which they deviate from the norm. At the same time, this deviation is strongly determined by climatic conditions and weather patterns. It can thus be concluded that colonies are threatened mostly by changes in climatic and weather events, followed by changes among single environmental (biotic or abiotic) factors to which bees are exposed to. This notion will aid in the understanding of the following discussion. Parasites and Pathogens Page 7 of 29 Parasites and pathogen are among the biotic factors mentioned previously, and they can impact behavior by impairing individuals either physically, cognitively, or both. One of the main parasites that have contributed to colony losses over the past 30 years is the mite Varroa destructor. Varroa destructor is a known ectoparasite (a parasite that only remains on the skin of the host, not attacking it internally) of the Eastern honeybee (Apis cerana) and was first discovered in European honeybees in the first half of the last century (Rosenkranz, 2009). Since then it has spread worldwide, and has been one of the major threats to beekeepers because of its ability to transfer a variety of viruses to their host, and because of their use of substantial amounts of hemolymph from both adult bees and broods, thus greatly weakening the host since its early life stages. The mites attach to adult bees and feed on their hemolymph, reproducing by entering the capped brood cells within the hive where they can lay eggs and have enough food from the brood’s hemolymph to sustain their offspring (Rosenkranz, 2009). This loss of hemolymph since early developmental stages results in significant weight loss for the hatching bees and drones, and consequently a reduced flight performance is experienced (Duay et al., 2002). Parasitism has also been related to reduced life span (Amdam et al., 2004), reduced learning capability, increased absence from the colony, and reduced ability to return to the colony (Kralj et al., 2007). Finally a decreased chance of mating is experienced by parasitized drones (Duay et al., 2002). In addition to the transfer of several viruses to their host, and the damage caused at both an individual and the colony level, the threat is increased by several other factors; (1) being a new parasite to European honeybees “a balanced host-‐parasite relationship is lacking and beekeepers do not have long-‐term experience in dealing with this pest,” (2) “it has spread almost worldwide within a short time period and it may now be difficult to find a Varroa free honeybee colony anywhere, other than in Australia,” (3) “without periodic treatment, most of the honey bee colonies in temperate climates would collapse within a 2-‐3 year period,” (4) “regular treatments increase the cost for beekeeping and the risk of chemical residues in bee products” (Rosenkranz, 2009). Page 8 of 29 Another pathogen that has been related to reduced lifespan, reduced colony performance, and increased winter mortality (Fries et al., 1984) is the microsporidia of the genus Nosema. One species of Nosema, N. apis has been a known pathogen of the European honeybee for a long time, and thus has not been the object of intensive studies regarding recent colony collapse. On the other hand, the fairly new introduced N. ceranae from Asia, has posed a much greater hazard to beekeepers since 1995 (vanEngelsdorp, 2009). Not only have beekeepers been unable to treat this new pest properly due to their inexperience with it, N. ceranae also seems to be more virulent than its predecessor (vanEngelsdorp, 2009). This species is transmitted through the ingestion of spores to which bees are exposed in the environment or within the hive, as housecleaning bees remove infected feces and other unwanted residues (vanEngelsdorp, 2009). While Nosema infestation has been correlated with heavy losses in some European countries such as Spain, a recent study conducted in the United States found that only about half of the sampled colonies were infected with Nosema ceranae, and there wasn’t a significant difference between populations with CCD and control populations (vanEngelsdorp, 2009). Subsequently, hives that have been affected by Colony Collapse Disorder typically do not have populations of Varroa and Nosema that are known to cause economic injury or population decline (vanEngelsdorp, 2009). In addition to the negative effects related to the presence and activity of these pests within hives and individuals, the risk of virus transmission is also significantly increased when infestation occurs. Of the 18 viruses that have so far been discovered to affect honeybees (Chen and Siede, 2007), five have been shown to be vectored by Varroa mites. These include the Kashmir bee virus, Sacbrood virus, Acute bee paralysis virus, Israeli acute paralysis virus, and Deformed wing virus (Boecking and Genersch, 2008), all of which had been a minor problem for honeybee health before the introduction of Varroa mites (Allen et al., 1986). Even though none of these viruses have been described as a major cause of Colony Collapse Disorder, their presence decreases the colony strength and speeds the collapse process, especially in later stages and over winter months. Page 9 of 29 One of the viruses impacting honeybees mostly at the individual level is the Deformed Wing Virus (DWV), an RNA virus that mainly affects bees on the pupal stage, but does not usually result in colony failure (Martin, 2001). The virus is vectored by Varroa mites, which transfer it to their host while feeding on them, and it is now one of the most widespread viruses in colonies parasitized by these mites (Martin, 2001). As demonstrated by Martin et al. (2001), the virus is especially damaging to bees encountering it in the pupal stage, resulting in higher pupae mortality (20% of infected individuals), and reduced longevity of emerging adults, while individuals becoming infected as adults are not affected in any significant way other than becoming potential vectors until they die (Martin, Ball & Carreck, unpublished data). Under field conditions, many of the pupae that have become infected will survive, thus leaving the colony in a seemingly healthy status by the end of the fall, with a sufficient number of emerging adults to withstand overwintering. But being infected by the virus, the majority of these adults die prematurely, thus leading to an imbalance in age structure and inability to perform the activities necessary for the survival of the colony (such as maintaining a suitable temperature) (Martin, 2001). Thus, the negative effects of the virus on the colony are amplified when Varroa mites are present, as the parasite feeds on pupae hemolymph and reproduces within the brood cell, resulting in higher infection rates. This overwintering collapse of seemingly healthy colonies, together with evidence indicating DWV presence in a large number of CCD colonies, lead to the investigation of a possible correlation between the two phenomena. However, such correlation has not been established (Cox-‐Foster et al., 2007). Another virus associated with Varroa presence and potentially a factor playing a role in Colony Collapse Disorder is the Israeli Acute Paralysis Virus (IAPV). This virus is part of a larger complex of similarly acting viruses including the Acute Bee Paralysis Virus, and Kashmir Bee Virus. The viruses persist within the colony usually without presenting apparent signs of infection at either the colony or individual level, but are highly virulent in both larvae and adults, causing paralysis, trembling, and inability to fly soon followed by death (de Miranda, 2009). IAPV has been the subject of recent investigation both because it is known to be vectored by Page 10 of 29
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