University of Maine Cooperative Extension |
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Honey Bees and Blueberry Pollination The Honey Bee Introduction In Maine, there are more than 50 species of native bees that are associated with lowbush blueberry. However, because of the alarming decline in native bee numbers over the past several decades (due to bee habitat loss, fragmentation, and pesticide use, farmers have relied more and more on managed bees (see the blueberry fact sheets on management of the alfalfa leafcutting bee, # 300; and commercial bumble bees, # 302) for pollination of lowbush blueberry. Honey bees are the “work horses” of managed bees and some estimates suggest that honey bees account for 80% of the insect pollination in agricultural crops. The use of the honey bee in lowbush blueberry has increased tremendously over the past 40 years. In 1965, almost 500 honey bee colonies were brought into Maine for lowbush blueberry pollination. By 1985 about 25,000 honey bee colonies were brought into Maine for lowbush blueberry pollination, but by the year 2000, more than 60,000 colonies were brought into Maine for pollination of this crop. The honey bee is the common name of the bee species, Apis mellifera L. This species, native to Mediterranean Europe, Asia, and Africa, was introduced into North America about 400 years ago for honey and wax production and crop pollination. This bee is different from many of our native bees in that it is social and lives in large colonies consisting of tens of thousands of sterile female worker bees, hundreds of male reproductives (drones), and usually a single female reproductive or queen. Most native bees are solitary (where individual female adult bees nest alone in the soil or in twigs), or primitively social (where female bees of the same species may share nests or even defense of the nest). There are some native bees that are social associated with lowbush blueberry in Maine. These species are represented by the bumble bees that live in small colonies, usually less than 100 individuals with a single reproductive queen. While some native bees are specialists that have evolved as highly efficient pollinators of only one or two species of flowering plants, most are generalists that are capable of pollinating a number of native and introduced plant species. One of the strengths of the honey bee as a pollinator is that it is a very broad generalist and so it can be used for pollination of many different food crops. Other positive attributes of this bee for pollination are that: 1) it can be easily managed in artificial hives; 2) it can be moved into and out of crop fields during and after bloom; 3) it has excellent spatial memory capabilities and this in combination with its ability to communicate the location of nectar rich floral resources among worker bees, means that large numbers of honey bees can quickly take advantage of floral resources and pollinate crops that only flower for a short period; and 4) it can learn how to manipulate and thereby pollinate complex flowers that are not accessible to many species of generalists bees (although, see discussion of honey bees and blueberry flowers below). Some of the drawbacks of honey bees are that: 1) they are defensive around their colony and may sting; 2) having evolved in warmer climates, they usually do not fly on days where the air temperature is below 50º F; and 3) being broad generalists capable of learning and communicating, they can switch from foraging on the intended crop to other more rewarding resource-rich wild flowers. What do honey bees look like? You are most likely to see an adult sterile female worker bee as it comes and goes from a hive or forages for nectar or pollen on a flower. Figure 1 shows a honey bee worker and a queen (larger bee). The worker is about 1/2 inch in length and its color ranges from light brown to dark brown to almost black (there are various races and/or subspecies of honey bees in the U.S. such as Italians, Caucasians, Carniolans, and Africans with differing pigmentation). The large eyes are usually shiny black and the thorax (where the six legs and two pairs of wings are attached) is covered with a dense mat of brown hairs. The abdomen is long and quite often characterized by alternating light and dark bands or rings. There are very few species of large brown bees in lowbush blueberry fields in Maine and so there is little chance for confusion. However, there is a syrphid fly (flower or hover fly) that is a bee mimic and is a similar size and color to the honey bee. Close inspection reveals that this fly has only one pair of wings and that the wings at rest are held in a delta pattern, unlike honey bees that hold their two pairs of wings parallel to their body. Aggressiveness is a variable trait in the honey bee that we normally use in Maine for pollination of lowbush blueberry. The arrival of Africanized honey bees in the U.S. in 1990 means that growers and beekeepers should realize that these more aggressive bees could make their way into Maine during the pollination season. It is not considered likely that Africanized bees can survive the winters in Maine. The African subspecies was introduced into Brazil in 1956, hybridized with the gentler European races and spread rapidly throughout northern South America, Central America, and into the U.S. The Africanized bees are now established in some southern regions of the U.S. including: Texas, California, New Mexico, Arizona, Puerto Rico and St. Croix. These bees can be extremely defensive, stinging farm workers, passers-by, and livestock, especially after hives have been disturbed or managed. Growers are being warned of the potential for Africanized bees to end up in their fields and should inspect the defensive nature of all rented hives by walking around the hives (once settled in the location) and observe the bees during pollination. Any questions regarding the possibility of Africanized bees on Maine blueberry land should be forwarded to the state apiary inspector, Maine Department of Agriculture, Augusta, ME. The Honey Bee Colony The honey bee colony is usually composed of one queen, several thousand (5,000-75,000) workers, and several hundred drones. The wax that comprises the combs over which the bees cluster is secreted by the worker bees and comprised of adjacent six-sided cells for storing food and brood rearing. Brood refers to the immature stages of the honey bee. The queen deposits a single, small, white egg in the bottom of a cell in a wax comb. She can be very fertile laying about 1,500 eggs per day. After three days, the egg hatches into a larva which is fed a mixture of pollen, nectar, and a rich protein secretion called royal jelly by worker bees for five to six days. Figure 2 shows both uncapped and capped (sealed) brood on a comb. The cell is then sealed by the workers and the larva develops into a pupa (a non-feeding resting stage), and then develops into an adult bee. The adult sterile worker bee emerges from the cell as an adult bee 21 days after the egg is laid. Queen bees require about 16 days and drone bees about 24 days to develop to adult maturity. Colony population buildup occurs through the reproductive efforts of a single queen and the nursing, feeding, foraging, and defensive efforts of the sterile workers. During lowbush blueberry bloom most honey bee colonies are in a phase of rapid population growth and so pollen and nectar foraging should be at a maximum (given that the colony has a strong and healthy foraging force of workers). Swarming is a process of colony reproduction in which the colony splits. When a colony is crowded or if an old queen is failing, the workers will begin to raise a new queen. Just prior to emergence of the new adult queen, the majority of workers will issue from the hive with the old queen in search of a new location for the colony. First, this part of the colony will usually cluster in a large mass surrounding the old queen, typically, on a branch in a tree. Scout bees will leave the swarming colony and search for a protected nesting site (usually dark and dry, often a tree cavity). When scouts find a nest site they return to the swarm and direct the mass of bees and the queen to the new nest site. The part of the colony that remains in the hive will support the new queen that emerges. If one queen emerges before any other queens she will sting and kill the others so that only one queen usually heads the colony. Workers visit flowers to collect both pollen and nectar (about 5-30% of flying honey bees are collecting pollen). Pollen is collected when it becomes entangled with the dense branched hair on the bee body. The bee combs the pollen from the body hair and packs it into pellets on specialized curved spines on the hind legs (pollen baskets) for transport to the hive. About 50-350 flowers are visited per pollen load brought back to the hive and a given bee will make between 1 and 50 pollen collecting trips per day. Pollen is necessary food (protein and lipid source) as is the honey made from nectar (carbohydrate source), for rearing brood. Pollen and honey are stored in the wax comb for the colony’s use. The amount of food material collected and stored depends upon many factors, including: the available flora, colony strength, bee race or subspecies, weather, and available comb space. Water is also essential for the welfare of the colony and is collected to dilute honey consumed by the bees and to regulate the colony temperature and humidity. On hot days colonies may be stressed and suffer if deprived of water even for only a few hours. Much energy is expended by honey bee workers when transporting food and water to the hive. A grower, using honey bees for pollination, will profit by placing the hives inside the field, but close to a water source. Colonies should be placed in a sunny location, near water (or supplied with artificial pools of water), and also placed in a location that is protected, as much as possible, from the wind since high winds reduce the frequency with which bees will leave the hive to forage. Pollination of Lowbush Blueberry The Blueberry Flower and Fruit Lowbush blueberry flowers grow in clusters on the last several inches of the stem. The white, greenish, or pink petals of the flower are united to form a tubular or bell shaped corolla, which hangs open-end downward. Ten stamens (stalks bearing the anthers containing the male germ cells or pollen) are inserted at the base of the corolla, around the style (female organ containing the female germ cells or ovules). The style extends beyond the stamens, out of the corolla and is receptive only on its tip, the stigma. Figure 3 shows a picture of a lowbush blueberry flower with petals removed to show the style and stigma (in green) and stamens surrounding style (in brown). The ovary is at the base of the style. During the period of stigma receptivity, pollen is released through pores on the end of the anther (these unusual anthers are called poricidal and can be envisioned as a salt shaker; when the anthers are shaken or agitated by a bee they release pollen). Nectar is produced in nectaries at the base of the corolla. The amount and concentration of nectar increases from 0 to 48 hours after anthesis (onset of pollen release). Because the anthers are protected by the bell-shaped corolla and the pollen is relatively heavy and sticky, wind does not aid in the pollination process. Stigma receptivity may last five to eight days depending on the weather and clone genetics, among other factors (for instance, the plant micro-nutrient is believed to extend the period of stigma receptivity in blueberries). However, if pollination does not occur within two to three days after the flower opens, fruit set is less likely and by 7-8 days becomes improbable. As soon as fertilization occurs (fusion of pollen and ovule germ cells), the flower begins to lose its attractiveness and development of the ovary (fruit) begins. The ovary matures into the many seeded (fertilized ovules) berry that ripens two to three months after flowering. The berry may contain as many as 65 small seeds which do not interfere with fruit palatability. The number of developing seeds per berry influences the size and rate of ripening of the fruit. More seeds result in larger and earlier maturing berries. There is considerable variation between genetic clones, geographic regions, and between years (i.e.. weather) in the pollination of lowbush blueberry in the field. Many lowbush blueberry clones growing under favorable conditions are, typically, capable of setting up to 80-90 percent of their blossoms. Some may even reach 100 percent. However, in June there is often a drop of fruit by the plants. This “June drop” may range from slightly greater than 0% to 60% of the set fruit, depending upon weather and probably clone genotype. There is, however, considerable self-sterility (3-90% self-sterility reported in some studies) and some cross-sterility in lowbush blueberries (some of this might be due to clones that are completely male sterile, but some of this is due to inter-specific incompatibility). This sterility results in failure of fertilization or early abortion of fruits. There can be multiple species of Vaccinium, generally referred to as lowbush blueberry, as many as five species in some fields. In addition, in some fields, 45% of the lowbush blueberry clones produce scarce amounts of pollen. With so much self-sterility and pollen scarcity, free transfer of pollen between clones is essential to maximize fruit production. Therefore, it is critical that bees be locally abundant or be brought into fields to insure cross-pollination between clones. Since insect pollination is essential for maximum blueberry production, failure to produce good crops is frequently the result of poor pollination. The lowbush blueberry plant species diversity will be a major consideration in determining whether the additional expense of bringing in honey bees to maximize pollination is cost effective. This is discussed next. Incompatibility Among Lowbush Blueberry Species Insect Pollination of Lowbush Blueberry Blueberry pollination is performed naturally by native bumble bees and solitary bees. Fifty-nine species of native bees have been observed in native lowbush blueberry fields. Bumble bees, when present, play a major role in blueberry pollination. The bumble bee works a few blossoms in one spot, then flies and works another spot, thus facilitating cross-pollination between clones. Bumble bee queens forage up to 400 yards from their nest site. Because of their size, they can shake out and distribute a large quantity of pollen from blueberry flowers. What makes bumble bees especially efficient pollinators is that they work the bloom at a very high speed (10-20 flowers / minute vs. 5-9 flowers / minute for honey bees), in addition, bumble bees are buzz pollinators (i.e.. they vibrate the flower shaking the pollen from the poricidal anthers) unlike honey bees. Bumble bees can place more than 50 pollen grains upon a lowbush blueberry stigma in a single floral visit (0-10 for a honey bee). Another characteristic of bumble bees that make them an efficient pollinator of lowbush blueberry is that they possess long tongues. This allows them to extract nectar from flowers with long corollas such as some clones of lowbush blueberry. It has been observed that honey bees will not visit all clones of lowbush blueberry. Some of the clones with long corollas and narrow corollar openings do not allow honey bees access to the nectar rewards of the flower. However, one disadvantage of the bumble bee is that only over-wintered bumble bee queens are present during the majority of the lowbush blueberry bloom period in Maine. Usually queens are not numerous, although some small blueberry fields that are not managed intensively in Maine have more than adequate populations of queen bumble bees to ensure maximum pollination Many other native bee species are also natural pollinators of lowbush blueberries. Many of these species are solitary, but some are primitively social living in loose multi-female aggregations. Native bees nest mostly in uncultivated, sparsely vegetated, sandy soils, or they are twig nesters in a variety of shrubs that exhibit soft pith within their branches. Their flight activity is usually confined to their nests (200-800 yards of their nest). These bees are from many families and are quite diverse in size and habits, digger bees (Family: Andrenidae), sweat bees (Family: Halictidae), cellophane bees (Family: Coletidae), and mason and leafcutting bees (Family: Megachilidae). Some of the species such as Osmia atriventris, commonly called the Maine blueberry bee, is very adept at pollinating blueberry. It drums the anthers with its forelegs in order to extract pollen from the lowbush blueberry plant. Many of these species are excellent pollinators of lowbush blueberry, but may be negatively impacted by weather from year to year, parasites and diseases, and many of the common lowbush blueberry production practices (especially insecticide applications). Because of the year to year fluctuations in native bee populations, many blueberry growers use honey bee colonies for pollination in order to reduce the risk of having a year of poor pollination due to low native bee densities. In other areas, native bee numbers are never high enough for adequate levels of pollination. This is often the case in the blueberry barrens in downeast Maine. So how does one know whether honey bees are a good management option? It is important to not only know the lowbush blueberry plant species structure in your field (discussed above), but also the native bee population strengths in your field. Determining The Need for Honey Bees – native bee densities PB = 14.5 + (7.8 * HB) + (17.7* NB) Using the above predictive model, if on average 3 native bees are observed per minute in a square yard of bloom, then the expected percent berries (PB) will be 67.5% or ((17.7 * 3) + 14.5). Now, if no native bees are present, and honey bees are used so that an average of 5 honey bees are observed per minute in a square yard of bloom, then the expected percent berries is 53.5% or ((7.8 * 5) + 14.5). It is important to remember that percent berries is less than percent fruit set...it is the proportion of berries remaining after June drop, or those fruit that will most likely mature into a harvestable crop. Forty to sixty percent berries (PB) is an average expectancy for a non-irrigated field in a year with adequate soil moisture. If one uses the above predictor, it must be realized that this is a linear model, and so it is possible to have bee densities which will yield greater than 100% PB. If this happens, just assume the prediction to be 100%. All of the above estimates can be used to determine whether the bee foraging force (native bee or honey bee) is adequate for pollination, given that there are no serious problems with blueberry plant species incompatibility. However, the decision to invest in commercial pollination is more complicated than it appears. First of all, evaluating the native bee densities in a particular field in one year may not be a good index of the bee densities two years from that instance when the field is in bloom again. Native bee populations can fluctuate in lowbush blueberry fields considerably from one year to the next (from 2-10 times). At this point there is no means of accurately predicting the density of native bee populations into the future. Unfortunately, honey bee contracts usually have to be made during the fall or winter before bloom and so there isn’t very much lead time for instantaneous decision making. There are two possible benefits to measuring your native bee densities. The first is to assess fields in the early bloom stage immediately before honey bee hives arrive. In this case, judgments can be made regarding the relative strength of native bee populations in each field and then honey bee hives can be apportioned to each field relative to the native bee strength, putting more hives in the fields that have the lowest native bee populations. This practice is only practical if hives are not placed in fields until 20-25% bloom (the recommendation). The second use of estimating native bee populations in a particular field is to gather long-term data on the bee populations for a given field (5-10 years) to establish the risk (1 year in 10 years or 3 years out of 10 years) that poor pollination will result in the absence of honey bees. This would be a good practice in small fields that may have high native bee densities most years. However, the final analysis of any decision regarding capital expenditures to improve pollination should be based upon what the actual percent of berries on a stem are that have resulted from pollination. This is addressed below. How to Assess Success of Pollination If honey bees are decided upon for pollination, the grower must decide whether to raise honeybees or to rent hives from a commercial beekeeper. What a Grower Should Expect from Colonies Raising Your Own Renting Hives Colony Strength - Considerations Fewer flying bees in front of some colonies may indicate that the colonies are not strong. Keep in mind that an examination of the colony inside the hive gives the best indication of its strength. To obtain a very crude “ball park” estimate of the foraging bee strength, count the number of bees RETURNING to the hive in 15 seconds. Then multiply this number by 0.06 (a factor that represents the proportion of an individual foraging bee’s makeup on a well covered comb in one minute). This product (number of returning bees in 15 seconds x 0.06) will provide a crude estimate of the number of full frames in the hive well covered with bees. So, for example, if you count 125 bees returning to the hive in 15 seconds then 125 x 0.06 = 7.5 or the estimated number of full frames well covered with bees is 7.5, a good strong colony. If the number of bees returning to the hive in 15 seconds is too high to count, then count the bees returning in 10 seconds but multiply the number of bees by 0.09 instead of 0.06. Determining Colony Strength – based upon bees on the comb
An additional and important way to estimate colony strength is by estimating the number of square inches of brood. This is because the presence of uncapped brood in a hive stimulates pollen collection – the prerequisite to pollination. To get an estimate of the square inches of uncapped brood, count the number of full brood frames and roughly determine the proportion of the brood that is uncapped, then multiply the total number of full brood frames first by the average proportion of uncapped brood and then multiply this product by 100. A strong colony should have 600 to 1,200 square inches of uncapped brood. A blanket of bees should be seen covering the brood. Another measure is: seven frames that are at least 60% covered with brood in all stages and 25% in the egg or younger uncapped brood stage as shown in Figure 6. Pollination Recommendations and Practices Number of Colonies to Use Because of the wide variety of conditions that exist in an area, the exact number of bees that a blueberry grower will need cannot be given. The number of honey bees needed depends on: 1) the number of native pollinators already in the area; 2) the number of other flowering plants that bloom at the same time as lowbush blueberry and thereby compete for the pollinating insects; 3) weather conditions during bloom period; 4) the amount of available blueberry blossoms; 5) the lowbush blueberry plant species composition within a field; and 6) the grower’s expectation of yield. The following are “rule of thumb” recommendations for the amount of honey bees needed:
Scheduling Delivery of Colonies Distribution of Colonies in the Field The following table gives the number of colonies a grower could use in each cluster to obtain uniform distribution of bees in fields that are at least 7-10 acres in size.
The premise involved in the periodic moving of colonies from field to field is that the first day or so after a colony is moved, the bees forage only near the hive and on flowers in this localized area (most likely blueberry flowers). Whenever bees are moved to a new location, they go through a period of orientation during which they get used to their new surroundings. Throughout this time, they are most effective as pollinators of the flowers nearest the hive. Once fully oriented, their foraging extends further. According to this strategy, bees should be present for three or four days during the peak of blueberry bloom then moved to later blooming fields for more efficient use of their pollinating service. The moves must be to a new field at least 3-4 miles from the old field to avoid disorientation and loss of foragers. This strategy has been tested in New Jersey on highbush blueberry and resulted in increased numbers of honey bees foraging close to the hive on blueberry immediately after the move. Whether hive rotation is practical for most growers in Maine and whether yield increases result in lowbush blueberry is not known. Requirements for Colonies
Increasing the Impact of Honey Bee Hives The idea of removing competing bloom is controversial and has not always been shown to improve crop yields. Recent thinking by pollination research biologists is in favor of enhancing, NOT eliminating alternate bee forage since it often results in attracting bees to an area. Alternate forage also may encourage native bees to nest near the crop. This forage may also result in the increase of native pollinator populations. This is especially true for flowering plants that flower before and after blueberry bloom. Of course this has to be balanced with crop loss due to weedy plant species. The use of attractant sprays has been evaluated for honey bees in a variety of crops. Attractants are designed to increase bee visitation to treated crops with the goal of increasing pollination. Several attractants have been developed and marketed, but most have had a doubtful performance record. One of these attractants, Fruit Boost®, is based upon a specific formulation of a synthetic form of the honey bee queen mandibular pheromone. This product has been tested in Maine lowbush blueberry and it did result in the sprayed bloom attracting more foraging honey bees than the non-sprayed bloom. However, there were no significant increases in yield or berry weights due to the Fruit Boost® spray. One possible use for this attractant that has not been evaluated is to treat fields in bloom when the associated honey bees are visiting non-crop flowering plants. This tactic would be in an attempt to get the bees to switch back to foraging in blueberry bloom, but it must be evaluated by growers. Pollen traps attach to the entrances of hives and harvest pollen from bees returning to the hive. It has been thought that pollen traps induce a pollen deficit in the colony and thus increase the proportion of bees that forage for pollen. The results of this management strategy have been inconsistent and have not been evaluated in lowbush blueberry. The use of a pollen trap for the entire bloom period may also be detrimental to brood rearing. Increased pollen collection is also believed to occur when colonies are fed sugar syrup. This results from a rapid change in the behavior of individual foragers from collecting nectar to collecting pollen. The experiments aimed at documenting this phenomenon are also not consistent and need to be performed in lowbush blueberry fields. Blueberry production practices with negative impacts on bee foraging and pollination are: 1) exposure of bees to irrigation and 2) exposure of bees to pesticides. Irrigation during the day may prohibit bees from foraging on flowers, irrigation water can knock bees out of the air while flying and wet flowers are not usually visited by honey bees. Irrigation during bloom should be restricted to night applications. Of the pesticides used in lowbush blueberry, the insecticides have the potential for major impacts. Insecticides act as repellents, they can disorient the bee so that it can not find its way back to the hive, and insecticides can lead to outright bee mortality or a more insidious weakening of the colony. The University of Maine Cooperative Extension Wild Blueberry Fact Sheet # 209 lists the relative honey bee toxicity of insecticides that are recommended by the University of Maine Cooperative Extension for lowbush blueberry production. Honey bees should be removed from fields when flowering has ceased so as to avoid over-exploitation of the wild flora to the detriment of native bees. Knowing and Understanding the Beekeeper If growers plan to use honey bees, they should have some basic knowledge about honey bees and beekeeping. A better knowledge by the grower of the beekeeper’s viewpoint and some of the problems associated with the rental of bees for pollination improves communication between the grower and the beekeeper leading to better pollination service. The grower usually considers only the fee and the potential value of the bees to the crop, along with associated problems of having the beekeeper, extra vehicles, crew, and the bees in the field. Renting Honey Bee Colonies – the beekeeper’s view The beekeeper usually sees the deal from an entirely different viewpoint. The advantages of renting hives to the beekeeper include:
However, the beekeeper also must consider such disadvantages as:
Some beekeepers operate their colonies in the same location year after year. Others move their colonies between states. Most beekeepers begin their move after nightfall when all the bees are in the hive. The entrance of the colonies may be closed for the period of the move or left open. The entire load is usually covered with a net to prevent the escape of bees. Most beekeepers attempt to deliver colonies at night so that the bees remain inside the hive while it is being positioned in the field. Unfamiliarity with the area combined with poor night visibility can prove hazardous for the beekeeper. A simple, safe and fast method of distributing colonies within the field will greatly reduce the problem of delivering bees. Growers are advised to contribute in this regard by clearly marking where they want to place the colonies in the field. Providing a guide for the bee truck or a tractor and a trailer with driver to aid in distributing the colonies is usually appreciated by the beekeeper. Renting Honey Bee Colonies – the contract Whenever you rent bee colonies for pollination service, obtain a written contract or agreement that covers at least the following points:
An example of a written contract can be found in the book, “The Hive and the Honey Bee”. Bee Stings The stinger is torn from the body of the bee after it is imbedded in the victim because the stinger has barbs on it similar to a fishing hook Figure 7. The worker bee usually dies within an hour after the stinger is lost. The queen does not lose her stinger (but she is not likely to sting), which is used only to destroy other queens and lay eggs. The drone, the male bee, has no stinger. Bee venom is a protein that acts as an antigen in your body resulting in your body’s manufacture of specific immunoglobulin E antibodies. If you have been stung before, the bee venom reacts with the antibodies which are attached to tissue cells called mast cells. These mast cells contain numerous vesicles filled with histamine and other substances that promote inflammation, swelling, burning and itching. If you are not allergic to bee stings your body’s reaction is confined to the area of the sting. If you are hypersensitive to bee venom (allergic) or you receive a lethal dose of bee stings (about 10 bee stings per pound of body weight) a systemic reaction can occur in which large amounts of histamine are released from the mast cells and dilation of blood vessels and the constriction of your respiratory passages can result in death unless the victim receives treatment at a hospital (administration of an antihistamine or adrenaline). Hypersensitive people can be desensitized by seeing an allergist. Preventing Honey Bee Stings
Removing the Stinger Acknowledgement I would like to thank a friend, Vivian Butz Huryn, an experienced commercial beekeeper and queen breeder, for reviewing this fact sheet and making suggestions for its improvement. Additional Reading Some additional references that you might be interested in are: “Crop Pollination by Bees”, by Keith S. Delaplane and Daniel F. Mayer. 2000, CABI Publishing. “Insect Pollination of Crops”, by John B. Free. 1993. Academic Press. “Bees and Crop Pollination – Crisis, Crossroads, Conservation”, edited by Constance Stubbs and Francis Drummond. 2001, Thomas Say Publications in Entomology. “The Biology of the Honey Bee”, by Mark L. Winston. 1987. Harvard University Press. “The Beekeepers Handbook”, by Diana Sammataro and Alphonse Avitabile. 1998. Cornell University Press. “The Hive and the Honey Bee”, edited by Joe M. Graham. 1992. Dadant & Sons.
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