The authors warmly thank K. Anderson, J.J. Adamczyk, E. Beren, I Carstensen, M. Giansiracusa B. Mott, N. Holst and A.R. Stilwell for discussions on design and execution and for help in the field.

The protocols described below follow the animal care guidelines of USDA Agricultural Research Service.
1. Full Evaluation
NOTE: A full evaluation is necessary to determine 1) the weights of all hive parts, including the lid, cover, boxes, bottom board, frames, and 2) the amounts of brood and food resources. The weights of all hive parts will be summed and subtracted from the total hive weight when all bees were present to yield the weight of all the adult bees. Data on the weights of hive parts that are largely constant, such as the lid, bottom board and box(es), can be retained and used in future evaluations, thus expediting the evaluations. Conduct a full evaluation at or near the beginning of the study. Wooden parts may change in terms of moisture content24 so repeat full evaluations are recommended after long periods. Weigh a part of the hive, such as the lid, at each evaluation to estimate changes in other hive parts. Place a screened vestibule around the workers and hive during evaluation if other hives are close by and robbing pressure is a concern.
<ol>
	<li>Weigh all hive parts. Use a scale with a precision of 1 g or less.
	<ol>
		<li>Weigh the lid, inner cover, queen excluder, syrup feeder, and any other parts on the top of the hive.</li>
		<li>Using a spatula or hive tool, remove, and weigh any food or treatment material, such as protein supplement or grease patty, resting on the tops of the frames. Replace afterward if necessary.</li>
		<li>Place an empty hive box (hereafter the &#34;temporary box&#34;) next to the hive to serve as the transitional location for the frames. Place the temporary box on top of a flat surface, such as a lid or a bottom board, to prevent bees, and particularly the queen, from falling out of the box onto the ground.</li>
		<li>Move the frames rapidly and gently, preferably in groups of two or three to retain parts of the bee cluster, to the temporary box so the frames are in the same order as they were in the original box. Once all the frames have been moved, shake any remaining bees onto the frames in the temporary box and weigh the hive box.</li>
		<li>If the box was the lowest box, weigh the bottom board, entrance reducer, and any other hive parts after shaking the bees into the temporary box. Number frames with an indelible marker before moving them so they can be replaced in their original orientation.</li>
		<li>Reinstall the bottom board, entrance reducer, brood box, and other equipment. Move the frames from the temporary box back to the original brood box in their original order and orientation, again taking care to avoid unnecessary disturbance of the bees.</li>
	</ol>
	</li>
	<li>Remove a frame from one end of the box and visually inspect both sides of the frame for the presence of the queen. If the queen is found, place her gently in a part of the box that has already been evaluated, to avoid further disturbance. Shake worker bees gently but firmly into the box between frames, rather than on top, if possible.</li>
	<li>Weigh the frame and photograph both sides of the entire frame with a digital camera, getting as close as possible to the frame so capped brood and honey cells are easily distinguished, but at a sufficient distance so the entire frame is included. Photograph the frame while another worker holds it.
	<ol>
		<li>Use a &#39;frame holder&#39; (any jig that holds the frame upright while on the scale and does not mar the comb) on the scale. Weigh the within-hive syrup feeders. 
		Note: The size of the frame in the photograph will be used to convert surface areas from relative to absolute measures.</li>
	</ol>
	</li>
	<li>Replace the frame in its original position and orientation in the hive box. Remove the next frame prior to reinstalling the previous frame to provide more space to safely shake bees within the box. Check for the presence of the queen, shake to remove bees, weigh, photograph, and replace each subsequent frame until all frames have been processed.</li>
	<li>If the hive has two or more boxes, weigh and photograph frames from the lowest box first.
	<ol>
		<li>Remove the upper box or boxes sequentially, stacking them next to the hive in reverse to their original order. Once the bottom box has been evaluated, place the next box to be evaluated on top of the bottom box, place the temporary box on top of the remaining unevaluated boxes, and move frames from the second box to the temporary box, as above. Move the frames back to their original box, in their original orientation. 
		NOTE: By inspecting the lower boxes first, shaken bees will fall into a hive box that will no longer be disturbed.</li>
	</ol>
	</li>
	<li>Obtain the total hive weight during a recent period of inactivity, such as the night or the early morning before the bees are flying on the day of the evaluation. This weight represents the entire colony including the foragers.</li>
	<li>Calculate the adult bee mass by summing the weights of all the hive parts (woodenware, frames, bee feed, etc.) and then subtracting that sum from the &#34;total hive weight&#34; value obtained in the previous step. The difference between the two is an estimate of the adult bee mass. 
	NOTE: Once the full evaluation is conducted, subsequent evaluations can be conducted on a partial basis, assuming the non-frame hive parts, such as the boxes and the bottom board, have not changed appreciably in weight. Partial evaluations take less time.</li>
	<li>To conduct a partial evaluation for a hive with a single box, remove, photograph, weigh, and replace the frames without moving frames to a temporary box. In a hive with multiple boxes, the follow the procedure as described above (step 1.5), but without weighing the hive boxes.</li>
</ol>
2. Installation of Hives on Scales
NOTE: The hive scales used in this study are outdoor electronic bench scales with a maximum capacity of at least 100 kg, a load cell precision of about one part in 5000 with temperature compensation, and a pan size of 460 mm x 610 mm. These scales are connected to a 24 VDC indicator and a 12-bit datalogger. Indicator output may be digital or analog; scale systems used here had output in mA and required calibration curves to convert data to kg.
<ol>
	<li>Install scales on a firm, level surface. 
	NOTE: Elevating the scales from the ground using concrete or ceramic blocks, or pieces of kiln-dried wood, will keep the scale and electrical connections from coming into contact with soil or water.</li>
	<li>Cover the scale pan on top with plastic, cloth, cardboard, or other material to prevent excessive light reflection and heating of the hive entrance.</li>
	<li>Ensure that entrances to hives that are close together face different directions to reduce drift among colonies.</li>
	<li>Calibrate hive scales upon installation and periodically thereafter, particularly if the scales are moved.
	<ol>
		<li>Place scale calibration weights on the weighing pan and record the scale output. Ensure that the total weights exceed 50% of the maximum capacity of the scale. 
		NOTE: If the scale output is voltage or current units, rather than mass units, then use the slope and intercept of the calibration curve (relationship between total known weight on the pan and scale output) to convert scale output to mass units.</li>
	</ol>
	</li>
</ol>
3. Installation of Temperature Sensors
NOTE: Temperature sensors used in this study were of two types: 1) thermocouples attached to cables directly connected to a battery-powered datalogger (which may be placed inside or outside the hive, if the cable is long enough); and 2) small, battery-powered devices with integrated sensors and dataloggers and which required removal from the hive for data to be downloaded.
<ol>
	<li>Obtain a temperature sensor that can fit between frames, is resistant to the high humidity conditions in the interior of a hive, and has sufficient battery power and memory (or is accessible, via cable or wireless connection).</li>
	<li>Place sensors that might be affected by wax or propolis in a protective container, such as a tissue embedding cassette (small, disposable plastic box with a snap-shut lid and with ventilation slots). The protective container reduces wax and propolis build-up that can clog sensor access ports of sensors or otherwise affect data download.</li>
	<li>Attach the sensor just beneath the top bar in the center of the box to provide informative data on brood rearing (see below). 
	NOTE: A short piece of wire is attached to the container with the sensor and the wire stapled to the top of the frame, so the container hangs down one side. Sensors placed directly on the brood mass may interfere with brood and comb maintenance, and sensors placed on frames near the exterior, or placed on inner covers or lids, may be affected a great deal by external conditions, particularly during cool weather.</li>
</ol>
4. Preparation of Syrup Treatment
NOTE: Make treatment solutions fresh the day of each feeding using analytical-grade imidacloprid. Imidacloprid is highly water soluble and therefore easily incorporated in syrup; some pesticides have low water solubility and should be applied using other means. Formulations of 1 kg of treatment solution were applied using a 1 L plastic bottle as follows:
<ol>
	<li>Mix control (no pesticide) sucrose solution 1:1 w:w (e.g. 500 g sucrose:500 mL distilled water). Dissolve sucrose in distilled water using a large mixing flask with mixing bar on a hot plate heated to no more than 60 &#176;C.</li>
	<li>For solutions that will include imidacloprid, mix sucrose solution as above, but withhold 100 mL (thus &#34;short&#34;) to allow for the added volume of respective imidacloprid &#34;spike&#34; solutions.
	<ol>
		<li>Dissolve 500 g of sugar in 400 mL of distilled water to allow for the addition of a 100 mL spike to achieve 1 kg of treatment solution. For convenience in the field, transfer 900 g of &#34;short&#34; sugar solution to another bottle, then add the spike to each individual bottle.</li>
	</ol>
	</li>
	<li>Prepare a 10 ppm imidacloprid stock solution by measuring 1.0 mg of pesticide on an analytical balance and dissolving it in 100 mL of distilled water using a mixing bar without heat. 
	NOTE: To avoid problems with static electricity, weigh the imidacloprid into small, nonreactive plastic receptacles and place those receptacles directly in the solution. Stir the solution and remove the receptacles after the imidacloprid has dissolved.</li>
	<li>For a 5 ppb solution, mix 0.5 mL of the stock solution into 99.5 mL of distilled water to achieve 100 mL of spike solution. Add this to 900 g of the short sucrose solution to achieve 1 kg of 5 ppb syrup. For the 20 ppb solution, mix 2.0 mL of stock solution into 98.0 mL of distilled water to produce the 100 mL spike solution. For a 100 ppb solution mix, 10.0 mL of stock solution into 90.0 mL of distilled water for the spike solution.</li>
</ol>
5. Preparation of Bee Hives and Application of Treatment
<ol>
	<li>Evaluate colonies to determine the adult bee and brood populations prior to and after application of treatment. Sample material(s) of interest, such as honey, bee bread, bees, or wax, to determine baseline pesticide levels prior to treatment.
	<ol>
		<li>To sample wax, open a 50 mL centrifuge tube, select a section of empty comb, and scrape the open mouth of the tube along the comb until the desired amount of wax has been collected. Avoid touching the wax in the tube. Replace the cap on the tube and label the tube. Replace the frame in the hive.</li>
		<li>To sample honey or nectar, open a centrifuge tube and press the mouth of the tube against the section of comb containing the honey or nectar. Allow the material to flow into the tube, rather than scraping the tube, to reduce the amount of wax in the sample. Replace the cap on the tube and label the tube. Replace the frame in the hive.</li>
		<li>To sample bee bread, select a frame containing bee bread and use a clean metal or plastic spatula to remove the contents of several cells of bee bread and place the material in a centrifuge tube. Replace the frame in the hive. 
		NOTE: Collecting sufficient material will usually take several minutes per frame. A typical sample for pesticide analysis has at least 3 g of material; sample the honey, wax, and bee bread at least 2 or 3 different points in each hive and combine those subsamples for each hive.</li>
	</ol>
	</li>
	<li>Shortly after the evaluation, such as the next day, remove any broodless frames containing honey and nectar and replace those frames with either foundation or empty drawn comb to facilitate syrup storage. 
	NOTE: The objective is to increase both empty storage capacity and demand for nectar. If treatment is to be applied mixed in a protein supplement, removal of food frames may not be necessary.</li>
	<li>Ensure the hive has a feeder. As soon as possible after the pre-treatment evaluation, apply the treatment by pouring the syrup (step 4.4) into the feeder as rapidly as possible. Take care not to spill any syrup outside the hive where bees from other colonies might find it. 
	NOTE: Internal feeders may work best for reducing robbing; some pesticides affect adult bee activity and treated hives may be less vigilant in protecting feeders from robbing bees9.</li>
</ol>
6. Analysis of Hive Frame Photographs
NOTE: Frame photographs are made during each hive evaluation. Information can be extracted from the photographs using the following protocol.
<ol>
	<li>Activate an image analysis software, such as ImageJ, that allows for selecting a shape on a photograph with a tracing tool and measuring the area of the selected shape.</li>
	<li>Retrieve a digital photograph of a frame. Select &#39;File&#39; and click &#39;Open&#39;. Navigate to the folder where the photographs are kept to select a photo for analysis. The image will now be opened within the ImageJ program, and the ImageJ toolbar will be active.</li>
	<li>Select the &#39;Polygon&#39; tool from the toolbar. Use the mouse to click on each corner to define the area of the frame covered with comb. The shape will snap together when the starting corner is reached.</li>
	<li>Once the comb area is defined using the polygon tool, click on &#39;Analyze&#39; and select &#39;Measure&#39;; a new dialog box will pop up with the measurement. Use the column &#39;Area&#39; to measure the pixels within the defined area that was drawn. 
	NOTE: The first time the program is used, define the desired results to be reported.
	<ol>
		<li>Click on &#39;Results&#39; in the Results dialog box, and select &#39;Set Measurements&#39;. Check area, and uncheck all others.</li>
	</ol>
	</li>
	<li>To define the area covered by capped brood, select the &#39;Freehand&#39; tool. Depress the button on the mouse at a starting point and trace around the brood. When the starting point is reached, release the mouse button; the shape will snap into place.
	<ol>
		<li>Click &#39;Analyze&#39; and select &#39;Measure&#39;. If the brood pattern is not solid, due to factors such as disease, use the &#39;Multi-point&#39; selection tool to count the cells instead. Convert cell counts directly to cm2 for ease of comparison; there are typically about 4.01 cells/cm2 20.</li>
	</ol>
	</li>
	<li>Divide the value of the traced brood shape by the value of the interior of the frame to obtain a percent frame coverage of capped brood.</li>
	<li>Measure the interior of representative frames to obtain a standard so the brood surface area can be converted to cm2. 
	NOTE: A typical Langstroth deep frame has a surface area of about 880 cm2 20. For example, if 20% of the interior of a Langstroth deep frame is found to be covered by brood, then the surface area would be 0.20 x 880 cm2 = 176 cm2.</li>
	<li>Sum the brood surface area for the hive. To convert this measure to mass, multiply the surface area by 0.77 g/cm2 20.</li>
	<li>Calculate the surface area of honey, uncapped nectar, and stored pollen, for example, using the method described in steps 6.3 to 6.6. 
	NOTE: If nectar and pollen are considered together as &#34;food stores&#34; this reduces the components of a frame to two (food stores and brood). A typical Langstroth frame with plastic foundation and empty drawn comb weighs about 556 g20, so to calculate the weight of food stores, sum the weight of the frame with empty drawn comb and the weight of the brood mass, and subtract that weight from the observed weight of the frame in question.</li>
</ol>

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G., Holst, N. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Application+of+continuous+monitoring+of+honey+bee+colonies.">Application of continuous monitoring of honey bee colonies.</a> Apidologie. 46, 10-22 (2015).</li><li>De Smet, L., et al. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Stress+indicator+gene+expression+profiles,+colony+dynamics+and+tissue+development+of+honey+bees+exposed+to+sub-lethal+doses+of+imidacloprid+in+laboratory+and+field+experiments.">Stress indicator gene expression profiles, colony dynamics and tissue development of honey bees exposed to sub-lethal doses of imidacloprid in laboratory and field experiments.</a> PLoS ONE. 12 (2), e0171529 (2017).</li><li>Danka, R. G., Rinderer, T. E., Hellmich, R. A., Collins, A. 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D. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=.">.</a> The thermology of wintering honey bee colonies. , (1971).</li><li>Szabo, T. I. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Thermology+of+wintering+honey-bee+colonies+in+4-colony+packs.">Thermology of wintering honey-bee colonies in 4-colony packs.</a> Am. Bee J. 189, 554-555 (1989).</li><li>Human, H., Nicolson, S. W., Dietemann, V. <a target="_blank" href="http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?db=PubMed&cmd=Search&doptcmdl=Citation&defaultField=Title+Word&term=Do+honeybees,+Apis+mellifera+scutellata,+regulate+humidity+in+their+nest?.">Do honeybees, Apis mellifera scutellata, regulate humidity in their nest?.</a> Naturwissenschaften. 93, 397-401 (2006).</li></ol>

The authors have no competing financial interests.

Just as a crop scientist requires accurate and precise data to evaluate the effects of different treatments on plant growth and yield, honey bee researchers require accurate and precise data to evaluate bee colony growth and activity. These kinds of data are particularly important when the treatment effects may be subtle and long term, such as might be expected when bees are exposed to low concentrations of pesticides. 
Continuous hive weight data contain much information on the growth and activity of the colonies being studied, as well as the response of those colonies to exogenous disturbances, such as from robbing bees and from the addition of sugar syrup to a feeder9. However, proper interpretation of continuous weight and temperature data requires some knowledge of the size of the colony on a periodical basis. While the size of the adult bee population can be estimated from the daily amplitudes of detrended hourly data during a nectar flow, due to the increased forager traffic, outside of a nectar flow the relationship does not hold well20. Likewise, colony weight changes due to foraging success, food consumption, and bee population increases and decreases (e.g. bee kills) are partly a function of colony size. Smaller colonies may be healthy but show lower growth rates and less forager mass, for example, simply due a smaller forager population. 
Identifying a consistent and informative fixed position for a temperature sensor within the hive is crucial for producing reproducible results, particularly with overwintering. Previous research has shown that temperature monitoring at the top rail of a central frame in the brood (bottom) box were less correlated with ambient (external) temperatures than several other positions in the hive and were more influenced by the colony itself20. During winter, temperature differences between the colony bee cluster and ambient would expected to be high, and so differences among positions within the hive would likewise be expected to be greater than during warmer months. In addition, the bee cluster will move to different locations within the hive to exploit food resources25,26. The winter study described here showed that temperatures at horizontal positions, from the top middle to top outer frames, were significantly different while vertical differences on the middle frame were not. Horizontal air movement across frames is relatively restricted while vertical movement along a frame is not, so vertical mixing would be expected to be greater. These results confirm that a sensor position on the top rail of the middle frame is likely to be informative with respect to temperature influences from the colony.
Hive evaluations as they are described here resolve some of these issues. By subtracting the sum of the hive parts from the total hive weight measured during inactivity, such as at night, the estimate of the adult bee mass is independent of the number of foraging bees and thus insensitive to the time of evaluation. Recording data from a scale allows little room for subjectivity, and frame photographs provide a permanent record, so analyses of brood or food surface areas can be revisited if necessary, thus reducing the dependence on the training of the person doing the analyses. 
The methods described here are not without sources of error. Hive parts need to be as free of bees as possible, and any significant pieces of comb or other material that is removed should be weighed before discarded. The moisture content of wooden components can change over time and empty hives can exhibit measurable daily oscillations in weight due to daily changes in ambient relative humidity24. A hive containing a colony will probably not change as much because honey bees tend to maintain a relatively constant humidity inside the hive27, which would attenuate the ambient effects. These methods also depend on working rapidly. Once a hive is taken apart, the temperature and gas conditions change drastically and cool temperatures can impact brood health14. Taking apart a hive without a screen to keep out bees from neighboring colonies can promote robbing, particularly in times of nectar dearth. 
Modifications of these procedures are occasionally necessary. While it is in the interest of the researchers to gather as much data as possible, on some occasions, such as when many hives must be inspected, when robbing pressure is high, or when weather conditions are not optimal, workers must move quickly and forgo some data. If data on food reserves are not crucial, frames containing only honey and/or pollen, or frames with only wax or foundation, should be weighed but not photographed. Levels of uncapped larvae and eggs are also of interest to some researchers and they are often detected in frame photographs; however, in order to avoid sampling bias a researcher must be confident in being able to detect them in all photographs. Often only capped brood can be reliably and consistently identified on photographs taken under field conditions. Regarding the application of treatment, some hives, particularly those fed higher doses of imidacloprid, can become lethargic, causing a reduction in both their consumption of syrup and their ability to defend their hive. If a colony fails to consume its syrup after 5-7 d, the syrup should be removed, weighed, and discarded (to avoid contamination due to fermentation) and the colony offered fresh syrup. By weighing the discarded syrup, researchers will have record of how much each colony consumed, and thus can calculate total dosage. Finally, the application of treatments in sugar syrup is most effective when there are few or no alternative nectar sources. Alternative nectar sources would dilute the treatment to an unknown degree. Researchers should bear in mind, as was pointed out in the protocol section, that pesticides such as imidacloprid are associated with reduced activity levels, including hive protection, depending on the concentration. Reduced colony defense may also lead to increased robbing and possible confounding of treatments.
The results presented here show that continuous monitoring of hive weight and internal temperature are sensitive to colony-level behaviors, even with respect to behavioral changes induced by very low (5 ppb) concentrations of a neurotoxic pesticide. Further application of these methods to other neurotoxins and to pesticides with other modes of action, such as insect growth regulators, would increase our understanding of the effects of field-realistic doses on honey bee colonies.

Concerns have been raised recently about the exposure of honey bees to low concentrations of agrochemicals, particularly pesticides. Honey bees in the field may be exposed via direct application on foragers in the field or even the colonies themselves, by contact with treated surfaces, by dust from seed treatments, and by consumption of plant products such as pollen, nectar, and exudate1,2,3,4,5. Acute toxicity is clearly detrimental to honey bees, but the concentrations that causes 50% mortality in test insects (LC50) of many pesticides, including neonicotinoids such as imidacloprid, are far higher than that observed in bee bread and wax6 and higher than what is considered a &#34;field realistic&#34; range7. However, recent work has shown significant effects of sublethal exposure to pesticides on the colony level8, even for concentrations as low as 5 parts per billion (ppb)9.
Honey bee colonies have been referred to as &#34;superorganisms&#34; because many functions associated with an individual animal, including food procurement, reproduction (which honey bee colonies conduct via colony fission), and temperature control, are conducted by groups of adult worker bees10,11,12,13,14. Honey bee colonies, considered as organisms, offer a unique opportunity for study because the structures that support the colonies can be disassembled, examined, and reassembled with, if done carefully, little, or no adverse effects. Beekeepers and researchers take advantage of this by disassembling hives to inspect them for, among other things, the presence and status of the queen, pests, and pathogens, sufficiency of food stores, quantity of brood, and other factors15. Bee colonies have another important characteristic in that, unlike most homeotherms, they are typically stationary and obtain resources by deploying forager bees that can collect food at distances up to 10 km16. Bee hives can thus be maintained indefinitely on electronic scales, and the resulting continuous weight data has been shown to provide information on honey storage, foraging activity, foraging success, swarming, syrup consumption, lethal and sublethal pesticide effects, pest infestation and robbing9,17,18,19,20. Because all parts of the colony, including brood, can be accessed, sensors for temperature, humidity, CO2, sound, and other factors can be installed within the hive and used to obtain continuous data which inform on the health and status of the colony21.
Estimates of the size of the adult bee and brood populations are useful if not critical for interpreting many kinds of continuous data. Visual assessments are fast and widely applied in field studies22 but have shortcomings. Visual inspections are usually conducted during the day and thus do not account for foraging bees, which can compose a significant part of the population23. The precision and accuracy of estimates from visual inspections also depend on the training and experience of the inspector(s). Objectivity is another consideration, particularly if the hive inspectors are aware of which hives are in which treatment groups; assumptions about the distribution of the error of such measures may be difficult to justify.
Rate of hive weight gain, size of the foraging population, and within-hive temperatures, to provide a few examples, would be expected to be quantitatively different between large and small colonies, so measuring and controlling for colony size often greatly facilitates the detection of treatment effects in randomized experiments. For research purposes, a precise and objective measure of the adult bees was developed based in the principle that the difference between the total hive weight during a period of inactivity, such as at night, and the sum of the weight of all the hive parts (including woodenware, wax, honey, and brood) is the weight of the total adult bee mass. By weighing frames and measuring brood mass using frame photographs, food resources can likewise be estimated by subtracting the brood mass from the frame weight, after controlling for the weights of the empty frame and the wax. These methods are intended to improve on the precision expected from visual assessments in the field.

<table><tbody><tr><td>Langstroth hive equipment (box)</td><td>Mann Lake Ltd, Hackensack, MN</td><td>KD-700</td><td></td></tr><tr><td>Langstroth hive equipment (frame)</td><td>Mann Lake Ltd, Hackensack, MN</td><td>WW-900</td><td></td></tr><tr><td>Langstroth hive equipment (lid and cover)</td><td>Mann Lake Ltd, Hackensack, MN</td><td>WW-302&lt;br/&gt; &amp;nbsp;</td><td></td></tr><tr><td>Langstroth hive equipment (base)</td><td>Mann Lake Ltd, Hackensack, MN</td><td>WW-316</td><td></td></tr><tr><td>Langstroth hive equipment (internal feeder)</td><td>Mann Lake Ltd, Hackensack, MN</td><td>FD-505</td><td></td></tr><tr><td>Cordovan Italian queens and bee packages</td><td>C.F. Koehnen &amp;amp; Sons, Glenn, CA</td><td></td><td></td></tr><tr><td>Scale, bench (100 kg max. capacity): model B-2418&amp;nbsp;</td><td>TEKFA, Copenhagen, Denmark</td><td>discontinued</td><td></td></tr><tr><td>Scale, bench (100 kg max. capacity): Diamond Series</td><td>Avery Weigh-Tronix , Fairmont, MN</td><td>1824-200</td><td></td></tr><tr><td>Imidacloprid, analytical-grade CAS # 138261-41-3</td><td>Sigma-Aldrich, St. Louis, MO 63103</td><td>37894</td><td></td></tr><tr><td>Electronic scale, precision (precision = 0.1 mg): Adventurer Pro 260</td><td>Ohaus,&amp;nbsp; Parsippany, NJ</td><td>AV264C</td><td></td></tr><tr><td>Electronic scale, portable (15 kg max. cap.): Ranger Count 3000</td><td>Ohaus, Parsippany, NJ</td><td>RC31P15</td><td></td></tr><tr><td>Thermocouple probe: TMC6-HD</td><td>Onset Computer Corp., Bourne, MA</td><td>TMC6-HD</td><td></td></tr><tr><td>Datalogger, 12-bit: Hobo U-12</td><td>Onset Computer Corp., Bourne, MA</td><td>U12-012</td><td></td></tr><tr><td>Temperature and r.h. datalogger: iButton Hygrochron</td><td>Baulkham Hills, NSW 2153, Australia</td><td>DS1923</td><td></td></tr><tr><td>Temperature datalogger: iButton Thermochron</td><td>Baulkham Hills, NSW 2153, Australia</td><td>DS1922L</td><td></td></tr><tr><td>Nalgene plastic bottle</td><td>Thermo Scientific, Rochester, NY</td><td>2104-0032</td><td></td></tr><tr><td>Tissue embedding cassette</td><td>Thermo Fisher Scientific, Waltham, MA</td><td>B1000731WH</td><td></td></tr><tr><td>Digital camera: Pentax K-01</td><td>Ricoh Imaging Co., Ltd.</td><td>15241</td><td></td></tr><tr><td>ImageJ version 1.47 software</td><td>W. Rasband, National Institutes of Health, USA</td><td></td><td></td></tr><tr><td>Centrifuge tubes, 50 ml</td><td>Fisher Scientific, Asheville, NC</td><td>14-959-49A</td><td></td></tr></tbody></table>

monitoring colony-level effects of sublethal pesticide exposure on honey bees

The effects of sublethal pesticide exposure to honey bee colonies may be significant but difficult to detect in the field using standard visual assessment methods. Here we describe methods to measure the quantities of adult bees, brood, and food resources by weighing hives and hive parts, by photographing frames, and by installing hives on scales and with internal sensors. Data from these periodic evaluations are then combined with running average and daily detrended data on hive weight and internal hive temperature. The resulting datasets have been used to detect colony-level effects of imidacloprid applied in a sugar syrup as low as 5 parts per billion. The methods are objective, require little training, and provide permanent records in the form of sensor output and photographs.

Honey bee colony growth and phenology, measured using regular hive inspections with continuous weight monitoring, revealed significantly lower brood production among colonies exposed to imidacloprid at 100 ppb. 
Hive inspections showed that adult bee masses were not significantly affected by exposure to both sublethal concentrations of 5 and 100 ppb, but analysis of photographs of brood frames revealed that brood production in the 100 ppb treatment was significantly lower (Figure 1). Continuous hive weight data showed different colony growth rates among groups of hives exposed to different concentrations of imidacloprid. The continuous hive weight data were divided into two parts: the 25 h running average data, which is related to colony growth and foraging success, and difference between the hourly raw data and the 25 h running average, the hourly detrended data. The daily amplitudes of the detrended data are related to foraging activity19,20 (Figure 2). While weighing hives occasionally may have detected average weight differences at some point, continuous weighing provided detrended data for information on colony behavior.
The top rail of the middle frame in a typical commercial hive is an effective location for temperature sensors. 
Adult worker bees in colonies generate and maintain high temperatures (33-36&#176;C) especially in the presence of brood14 and the cluster itself is mobile to take advantage of food stores in different parts of the hive25,26. To reduce heat loss, clusters avoid having a large contact surface with exterior parts of the hive, such as the sides or bottom, so the distance from the top center of the box to the cluster is seldom large. The top center of the brood box has been shown to have reduced temperature variability compared to other locations in the hive, such as the top center of an outer frame and the top of a second box (&#34;super&#34;) in summer and fall conditions20. In winter conditions, in which the difference between the ambient temperature and the cluster would be expected to be the greatest, the same location was found to have the highest temperature and lowest variability compared to ambient conditions, indicating the greatest contribution from the cluster itself (Figures 3 and 4; Table 1). Differences in temperature regimes could not be attributed to differences in the adult bee mass (Table 2).
Amplitudes of sine curves fit to continuous temperature data were significantly higher in the 100 ppb treatment than in the 5 ppb treatment while neither treatment group was significantly different from the control group9. 
Amplitudes are directly proportional to temperature variability, so the higher amplitudes indicate more variable temperatures at that point in the hive. Lower amplitudes reflect the higher brood production in the 5 ppb and control treatment groups compared to the 100 ppb treatment group (Figure 5). These results, combined with those from the hive inspections and continuous hive weight data, confirm that colony-level behavior was significantly affected by exposure to 100 ppb imidacloprid.
<img alt="Figure 1" class="xfigimg" src="/files/ftp_upload/56355/56355fig1.jpg" /> 
Figure 1: Adult bee and brood measures. Hive inspection data from May, 2014, to March, 2015, for colonies exposed to syrup containing 0 (control), 5 and 100 ppb imidacloprid near Tucson, AZ. (A) Average (+ SEM) total adult bee mass; (B) Average (+ SEM) sealed brood surface area. Gray zone indicates treatment period (4-6 kg of treated sucrose syrup per week per hive for 6 weeks). Four colonies per treatment group; one colony in the 100 ppb died during winter. Adult bee masses were not recorded in August. Data here was previously published and is used here with permission9. <a href="https://cloudflare.jove.com/files/ftp_upload/56355/56355fig1large.jpg" target="_blank">Please click here to view a larger version of this figure.</a>
<img alt="Figure 2" class="xfigimg" src="/files/ftp_upload/56355/56355fig2.jpg" /> 
Figure 2: Honey bee hive weight data. Continuous weight data from June to December, 2014, for honey bee colonies exposed to syrup containing 0, 5 and 100 ppb imidacloprid near Tucson, AZ. (A) Total hive weight (&#177; SEM); (B) Amplitudes of sine curves fit to detrended weight data from the same period. Gray zone indicates treatment period (4-6 kg of treated sucrose syrup per week per hive for 6 weeks). Four colonies per treatment group; one colony in the 100 ppb died during winter. Data here was previously published and is used here with permission9. <a href="https://cloudflare.jove.com/files/ftp_upload/56355/56355fig2large.jpg" target="_blank">Please click here to view a larger version of this figure.</a>
<img alt="Figure 3" class="xfigimg" src="/files/ftp_upload/56355/56355fig3.jpg" /> 
Figure 3: Within-hive temperatures at different locations. Daily average (&#177; SEM) temperatures (&#176;C) for 3 sensor locations inside honey bee hives. (A) 4 single-box hives kept at a high altitude site (MLEM: 2412 m); and (B) 3 hives kept at a lower altitude site (SRER: 719 m) near Tucson, AZ from December 2013 to February 2014. Hives were wooden Langstroth deep boxes (43.65 l capacity) fitted with wooden inner covers and metal-lined telescoping lids. Thermocouple temperature probes were attached to the top bars of the frames, and an integrated datalogger/temperature sensor was placed on the bottom rail of the middle frame. These data show that the sensor position at the top of the middle frame was consistently higher than ambient compared to the other sensor positions and thus informative about temperature management by the bee colonies. <a href="https://cloudflare.jove.com/files/ftp_upload/56355/56355fig3large.jpg" target="_blank">Please click here to view a larger version of this figure.</a>
<img alt="Figure 4" class="xfigimg" src="/files/ftp_upload/56355/56355fig4.jpg" /> 
Figure 4: Within-hive temperature variability at different locations. Daily average (&#177; SEM) amplitudes for sine curves fit to hourly detrended temperature data for 3 sensor locations inside honey bee hives. (A) 4 hives kept at at high altitude site (MLEM: 2412 m); and (B) 3 hives kept at a lower altitude site (SRER: 719 m) near Tucson, AZ from December 2013 to February 2014. Hives were wooden Langstroth deep boxes (43.65 l capacity) fitted with wooden inner covers and metal-lined telescoping lids. Thermocouple temperature probes were attached to the top bars of the frames, and an integrated datalogger/temperature sensor was placed on the bottom rail of the middle frame. These data show that the sensor position at the top of the middle frame was consistently lower in variability (here measured as the amplitude of sine curves fit to hourly detrended data) than ambient compared to the other sensor positions and thus informative about temperature management by the bee colonies. Scales for the ambient temperature (solid black line) are on the right of each graph. <a href="https://cloudflare.jove.com/files/ftp_upload/56355/56355fig4large.jpg" target="_blank">Please click here to view a larger version of this figure.</a>
<img alt="Figure 5" class="xfigimg" src="/files/ftp_upload/56355/56355fig5.jpg" /> 
Figure 5: Within-hive temperatures for treated colonies. Continuous temperature data from June to December, 2014, for honey bee colonies exposed to syrup containing 0, 5 and 100 ppb imidacloprid near Tucson, AZ. (A) Average hive temperature (&#177; SEM); (B) Amplitudes of sine curves fit to detrended temperature data from the same period. Gray zone indicates treatment period (4-6 kg of treated sucrose syrup per week per hive for 6 weeks). Four colonies per treatment group; one colony in the 100 ppb died during winter. Data here was previously published and is used here with permission (Meikle et al. 2016a). <a href="https://cloudflare.jove.com/files/ftp_upload/56355/56355fig5large.jpg" target="_blank">Please click here to view a larger version of this figure.</a>
<table border="1" fo:keep-together.within-page="1" fo:keep-with-next.within-page="always">
	<tbody>
		<tr>
			<td>Comparison</td>
			<td>t test</td>
			<td>adj. P</td>
			<td>Site</td>
			<td>Avg. diff. (&#176;C)</td>
		</tr>
		<tr>
			<td>Pos. 2 - Pos. 1</td>
			<td>2.05</td>
			<td>0.0485</td>
			<td>MLEM</td>
			<td>1.00 &#177;0.25</td>
		</tr>
		<tr>
			<td></td>
			<td></td>
			<td></td>
			<td>SRER</td>
			<td>4.38 &#177;0.12</td>
		</tr>
		<tr>
			<td></td>
			<td></td>
			<td></td>
			<td></td>
			<td></td>
		</tr>
		<tr>
			<td>Pos. 2 - Pos. 3</td>
			<td>0.84</td>
			<td>1</td>
			<td>MLEM</td>
			<td>2.05 &#177;0.21</td>
		</tr>
		<tr>
			<td></td>
			<td></td>
			<td></td>
			<td>SRER</td>
			<td>0.12 &#177;0.11</td>
		</tr>
	</tbody>
</table>
Table 1: Average temperature differences and post hoc comparisons among different sensor positions within honey bee hives. Position 1: top outer frame; Position 2: top middle frame; Position 3: bottom middle frame. 4 single-box hives were kept at a high altitude site (MLEM: 2412 m) and 3 hives were kept at a lower altitude site (SRER: 719 m) near Tucson, AZ from December 2013 to February 2014. Hives were wooden Langstroth deep boxes (43.65 l capacity) fitted with wooden inner covers and metal-lined telescoping lids. Thermocouple temperature probes were attached to positions 1 and 2, and an integrated datalogger/temperature sensor was attached to position 3.
<table border="1" fo:keep-together.within-page="1" fo:keep-with-next.within-page="always">
	<tbody>
		<tr>
			<td>Group</td>
			<td>Date</td>
			<td>Average (&#177; SEM) adult bee mass (g)</td>
			<td>Average (&#177; SEM) brood surface area (cm2)</td>
		</tr>
		<tr>
			<td>MLEM</td>
			<td>18 Nov. 2013</td>
			<td>2119 &#177;412</td>
			<td>1372 &#177;396</td>
		</tr>
		<tr>
			<td>SRER</td>
			<td>15 Nov. 2013</td>
			<td>2270 &#177;312</td>
			<td>53 &#177;30</td>
		</tr>
		<tr>
			<td>MLEM</td>
			<td>13 Feb. 2014</td>
			<td>2171 &#177;105</td>
			<td>0</td>
		</tr>
		<tr>
			<td>SRER</td>
			<td>11 Feb. 2014</td>
			<td>2027 &#177;487</td>
			<td>867 &#177; 79</td>
		</tr>
	</tbody>
</table>
Table 2: Average adult bee masses and brood masses, estimated using the protocols described here, for four hives kept at a high altitude site (MLEM: 2412 m); and three hives kept at a lower altitude site (SRER: 719 m) near Tucson, AZ from December 2013 to February 2014. Hives were wooden Langstroth deep boxes (43.65 l capacity) fitted with wooden inner covers and metal-lined telescoping lids. Thermocouple temperature probes were attached to positions 1 and 2, and an integrated datalogger/temperature sensor was attached to position 3.

Watch this Scientific Journal Video about Monitoring Colony-level Effects of Sublethal Pesticide Exposure on Honey Bees at JoVE.com

Monitoring Colony-level Effects of Sublethal Pesticide Exposure on Honey Bees

Sublethal doses of pesticides may affect colonies in ways that are difficult to detect using only periodic or visual methods. Methods to measure total adult bee mass, brood, and food resources by weighing hives and hive parts, photographing frames, and installing sensors, are provided. Data analysis is also addressed.

The effects of sublethal pesticide exposure to honey bee colonies may be significant but difficult to detect in the field using standard visual assessment ...

monitoring-colony-level-effects-sublethal-pesticide-exposure-on-honey

Universidad de Cartagena UDEC

Research

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Biology

9.0K Views.  Carl Hayden Bee Research Center. Sublethal doses of pesticides may affect colonies in ways that are difficult to detect using only periodic or visual methods. Methods to measure total adult bee mass, brood, and food resources by weighing hives and hive parts, photographing frames, and installing sensors, are provided. Data analysis is also addressed.

Video: Monitoring Colony-level Effects of Sublethal Pesticide Exposure on Honey Bees

Empirical, Metagenomic, and Computational Techniques Illuminate the Mechanisms by which Fungicides Compromise Bee Health

Growers often use fungicide sprays during bloom to protect crops against disease, which exposes bees to fungicide residues. Although considered &#34;bee-safe,&#34; there is mounting evidence that fungicide residues in pollen are associated with bee declines (for both honey and bumble bee species). While the mechanisms remain relatively unknown, researchers have speculated that bee-microbe symbioses are involved. Microbes play a pivotal role in the preservation and/or processing of pollen, which serves as nutrition for larval bees. By altering the microbial community, it is likely that fungicides disrupt these microbe-mediated services, and thereby compromise bee health. This manuscript describes the protocols used to investigate the indirect mechanism(s) by which fungicides may be causing colony decline. Cage experiments exposing bees to fungicide-treated flowers have already provided the first evidence that fungicides cause profound colony losses in a native bumble bee (Bombus impatiens). Using field-relevant doses of fungicides, a series of experiments have been developed to provide a finer description of microbial community dynamics of fungicide-exposed pollen. Shifts in the structural composition of fungal and bacterial assemblages within the pollen microbiome are investigated by next-generation sequencing and metagenomic analysis. Experiments developed herein have been designed to provide a mechanistic understanding of how fungicides affect the microbiome of pollen-provisions. Ultimately, these findings should shed light on the indirect pathway through which fungicides may be causing colony declines.

Microbial consortia within bumble bee hives enrich and preserve pollen for bee larvae. Using next generation sequencing, along with laboratory and field-based experiments, this manuscript describes protocols used to test the hypothesis that fungicide residues alter the pollen microbiome, and colony demographics, ultimately leading to colony loss.

Growers often use fungicide sprays during bloom to protect crops against disease, which exposes bees to fungicide residues. Although considered ...

Environment

Evaluating the Effect of Environmental Chemicals on Honey Bee Development from the Individual to Colony Level

The presence of pesticides in the beekeeping environment is one of the most serious problems that impacts the life of a honey bee. Pesticides can be brought back to the beehive after the bees have foraged on flowers that have been sprayed with pesticides. Pesticide contaminated food can be exchanged between workers which then feed larvae and therefore can potentially affect the development of honey bees. Thus, residual pesticides in the environment can become a chronic damaging factor to honey bee populations and gradually lead to colony collapse. In the presented protocol, honey bee feeding methods are described and applied to either an individual honey bee or to a colony. Here, the insect growth regulator (IGR) pyriproxyfen (PPN), which is widely used to control pest insects and is harmful to the development of honey bee larvae and pupae, is used as the pesticide. The presenting procedure can be applied to other potentially harmful chemicals or honeybee pathogens for further studies.

Herein we present a method to feed pesticide contaminated food to both an individual honey bee and a beehive colony. The procedure evaluates the pesticide effect on individual honey bees by in vivo feeding of basic larval diet and also on the natural condition of beehive colony.

The presence of pesticides in the beekeeping environment is one of the most serious problems that impacts the life of a honey bee. Pesticides can be ...

In Vitro Rearing of Solitary Bees: A Tool for Assessing Larval Risk Factors

Although solitary bees provide crucial pollination services for wild and managed crops, this species-rich group has been largely overlooked in pesticide regulation studies. The risk of exposure to fungicide residues is likely to be especially high if the spray occurs on, or near host plants while the bees are collecting pollen to provision their nests. For species of Osmia that consume pollen from a select group of plants (oligolecty), the inability to use pollen from non-host plants can increase their risk factor for fungicide-related toxicity. This manuscript describes protocols used to successfully rear oligolectic mason bees, Osmia ribifloris sensu lato, from egg to prepupal stage within cell culture plates under standardized laboratory conditions. The in vitro-reared bees are subsequently used to investigate the effects of fungicide exposure and pollen source on bee fitness. Based on a 2 &#215; 2 fully crossed factorial design, the experiment examines the main and interactive effects of fungicide exposure and pollen source on larval fitness, quantified by prepupal biomass, larval developmental time, and survivorship. A major advantage of this technique is that using in vitro-reared bees reduces natural background variability and allows the simultaneous manipulation of multiple experimental parameters. The described protocol presents a versatile tool for hypotheses testing involving the suite of factors affecting bee health. For conservation efforts to be met with significant, lasting success, such insights into the complex interplay of physiological and environmental factors driving bee declines will prove to be critical.

In Vitro Rearing of Solitary Bees: A Tool for Assessing Larval Risk Factors

Fungicide sprays on flowering plants may expose solitary bees to high concentrations of pollen-borne fungicide residues. Using laboratory-based experiments involving in vitro-reared bee larvae, this study investigates the interactive effects of consuming fungicide-treated pollen derived from host and non-host plants.

Although solitary bees provide crucial pollination services for wild and managed crops, this species-rich group has been largely overlooked in pesticide ...

Monitoring Acupuncture Effects on Human Brain by fMRI

Functional MRI is used to study the effects of acupuncture on the BOLD response and the functional connectivity of the human brain.  Results demonstrate that acupuncture mobilizes a limbic-paralimbic-neocortical network and its anti-correlated sensorimotor/paralimbic network at multiple levels of the brain and that the hemodynamic response is influenced by the psychophysical response.  Physiological monitoring may be performed to explore the peripheral response of the autonomic nerve function. This video describes the studies performed at LI4 (hegu), ST36 (zusanli) and LV3 (taichong), classical acupoints that are commonly used for modulatory and pain-reducing actions. Some issues that require attention in the applications of fMRI to acupuncture investigation are noted.

FMRI and physiological monitoring is used to study the effects of Acupuncture on the central and peripheral nervous systems. Acupuncture mobilizes a limbic-paralimbic-neocortical network, with great overlap with the default mode network, to modulate neurological activity, possibly related to its autonomic effect in the peripheral nervous system.

Functional MRI is used to study the effects of acupuncture on the BOLD response and the functional connectivity of the human brain.  Results demonstrate ...

Evaluating the Effect of Pesticides on the Larvae of the Solitary Bees

Current ecological risk assessments of pesticides on pollinators have primarily considered only laboratory conditions. For the larvae of solitary bees, ingestion of provisions contaminated with pesticides may increase the mortality rate of the larvae, decrease the collection rate and the population of adult solitary bees in the next year from a demographic perspective. But there are limited studies on the effects of pesticides on the larvae of solitary bees. Therefore, understanding how pesticides influence the larvae of solitary bees should be considered an integral part of pesticide ecological risk assessment. This study presents a method to expose the larvae of solitary bee, Osmia excavata, to lethal or sublethal doses of pesticide, tracking larval weight gain, developmental duration, eclosion ability, and food consumption efficiency conversion of ingested food. To demonstrate the effectiveness of this method, the larvae of O. excavata were fed with provisions containing acute lethal and sublethal doses of chlorpyrifos. Then, the above indexes of the treated larvae were investigated. This technique helps to predict and mitigate the risk of pesticides to pollinators.

The present protocol explains a method to feed pesticide-contaminated provisions to the larvae of the solitary bees, Osmia excavata. The procedure examines the ecotoxicity of the pesticide to the larvae of the solitary bees.

Current ecological risk assessments of pesticides on pollinators have primarily considered only laboratory conditions. For the larvae of solitary bees, ...

Biochemistry

Studying the Effects of Matrix Stiffness on Cellular Function using Acrylamide-based Hydrogels

Tissue stiffness is an important determinant of cellular function, and changes in tissue stiffness are commonly associated with fibrosis, cancer and cardiovascular disease1-11. Traditional cell biological approaches to studying cellular function involve culturing cells on a rigid substratum (plastic dishes or glass coverslips) which cannot account for the effect of an elastic ECM or the variations in ECM stiffness between tissues. To model in vivo tissue compliance conditions in vitro, we and others use ECM-coated hydrogels. In our laboratory, the hydrogels are based on polyacrylamide which can mimic the range of tissue compliances seen biologically12. "Reactive" cover slips are generated by incubation with NaOH followed by addition of 3-APTMS. Glutaraldehyde is used to cross-link the 3-APTMS and the polyacrylamide gel. A solution of acrylamide (AC), bis-acrylamide (Bis-AC) and ammonium persulfate is used for the polymerization of the hydrogel. N-hydroxysuccinimide (NHS) is incorporated into the AC solution to crosslink ECM protein to the hydrogel. Following polymerization of the hydrogel, the gel surface is coated with an ECM protein of choice such as fibronectin, vitronectin, collagen, etc.
The stiffness of a hydrogel can be determined by rheology or atomic force microscopy (AFM) and adjusted by varying the percentage of AC and/or bis-AC in the solution12. In this manner, substratum stiffness can be matched to the stiffness of biological tissues which can also be quantified using rheology or AFM. Cells can then be seeded on these hydrogels and cultured based upon the experimental conditions required. Imaging of the cells and their recovery for molecular analysis is straightforward. For this article, we define soft substrata as those having elastic moduli (E) &lt;3000 Pascal and stiff substrata/tissues as those with E &gt;20,000 Pascal.

The effect of substrata stiffness on cellular function can be modeled in vitro using polyacrylamide hydrogels of varying compliances.

Tissue stiffness is an important determinant of cellular function, and changes in tissue stiffness are commonly associated with fibrosis, cancer and ...

Preparation of Single-cohort Colonies and Hormone Treatment of Worker Honeybees to Analyze Physiology Associated with Role and/or Endocrine System

Honeybee workers are engaged in various tasks related to maintaining colony activity. The tasks of the workers change according to their age (age-related division of labor). Young workers are engaged in nursing the brood (nurse bees), while older workers are engaged in foraging for nectar and pollen (foragers). The physiology of the workers changes in association with this role shift. For example, the main function of the hypopharyngeal glands (HPGs) changes from the secretion of major royal jelly proteins (MRJPs) to the secretion of carbohydrate-metabolizing enzymes. Because worker tasks change as the workers age in typical colonies, it is difficult to discriminate the physiological changes that occur with aging from those that occur with the role shift. To study the physiological changes in worker tissues, including the HPGs, in association with the role shift, it would be useful to manipulate the honeybee colony population by preparing single-cohort colonies in which workers of almost the same age perform different tasks. Here we describe a detailed protocol for preparing single-cohort colonies for this analysis. Six to eight days after single-cohort colony preparation, precocious foragers that perform foraging tasks earlier than usual appear in the colony. Representative results indicated role-associated changes in HPG gene expression, suggesting role-associated HPG function. In addition to manipulating the colony population, analysis of the endocrine system is important for investigating role-associated physiology. Here, we also describe a detailed protocol for treating workers with 20-hydroxyecdysone (20E), an active form of ecdysone, and methoprene, a juvenile hormone analogue. The survival rate of treated bees was sufficient to examine gene expression in the HPGs. Gene expression changes were observed in response to 20E- and/or methoprene-treatment, suggesting that hormone treatments induce physiological changes of the HPGs. The protocol for hormone treatment described here is appropriate for examining hormonal effects on worker physiology.

Here we describe our detailed protocol for the preparation of single-cohort honeybee colonies&#160;&#8211; a useful tool for analyzing the role-associated worker physiology. We also describe detailed protocols for treating workers with juvenile hormone and ecdysone to evaluate the involvement of these hormones in the regulation of worker behavior and/or physiology.

Honeybee workers are engaged in various tasks related to maintaining colony activity. The tasks of the workers change according to their age (age-related ...

Neuroscience

SwarmSight: Real-time Tracking of Insect Antenna Movements and Proboscis Extension Reflex Using a Common Preparation and Conventional Hardware

Many scientifically and agriculturally important insects use antennae to detect the presence of volatile chemical compounds and extend their proboscis during feeding. The ability to rapidly obtain high-resolution measurements of natural antenna and proboscis movements and assess how they change in response to chemical, developmental, and genetic manipulations can aid the understanding of insect behavior. By extending our previous work on assessing aggregate insect swarm or animal group movements from natural and laboratory videos using the video analysis software SwarmSight, we developed a novel, free, and open-source software module, SwarmSight Appendage Tracking (SwarmSight.org) for frame-by-frame tracking of insect antenna and proboscis positions from conventional web camera videos using conventional computers. The software processes frames about 120 times faster than humans, performs at better than human accuracy, and, using 30 frames per second (fps) videos, can capture antennal dynamics up to 15 Hz. The software was used to track the antennal response of honey bees to two odors and found significant mean antennal retractions away from the odor source about 1 s after odor presentation. We observed antenna position density heat map cluster formation and cluster and mean angle dependence on odor concentration.

This protocol describes steps for using the novel software, SwarmSight, for frame-by-frame tracking of insect antenna and proboscis positions from conventional web camera videos using conventional computers. The free, open-source software processes frames about 120 times faster than humans and performs at better than human accuracy.

Many scientifically and agriculturally important insects use antennae to detect the presence of volatile chemical compounds and extend their proboscis ...

Assessing Agrochemical Risk to Mated Honey Bee Queens

Current risk assessment strategies for honey bees rely heavily upon laboratory tests performed on adult or immature worker bees, but these methods may not accurately capture the effects of agrochemical exposure on honey bee queens. As the sole producer of fertilized eggs inside a honeybee colony, the queen is arguably the most important single member of a functioning colony unit. Therefore, understanding how agrochemicals affect queen health and productivity should be considered a critical aspect of pesticide risk assessment. Here, an adapted method is presented to expose honey bee queens and worker queen attendants to agrochemical stressors administered through a worker diet, followed by tracking egg production in the laboratory and assessing first instar eclosion using a specialized cage, referred to as a Queen Monitoring Cage. To illustrate the method&#39;s intended use, results of an experiment in which worker queen attendants were fed diet containing sublethal doses of imidacloprid and effects on queens were monitored are described.

This protocol was developed to enhance the understanding of how agrochemicals affect honey bee (Apis mellifera) reproduction by establishing methods to expose honey bee queens and their worker caretakers to agrochemicals in a controlled, laboratory setting and carefully monitoring their relevant responses.

Current risk assessment strategies for honey bees rely heavily upon laboratory tests performed on adult or immature worker bees, but these methods may not ...

Histology Basics and Cell Death Detection in Honeybee Tissue

Honeybees (Apis mellifera L.) inside the hive (nurse workers and other hive bees) and outside the hive (foragers) are exposed to climate and weather changes, various pesticides, pathogens, and malnutrition, mainly entering through the mouth and primarily affecting the digestive tracts of adult bees. To understand and prevent the effects of such external and internal stressors on honeybees, one useful research method is the immunohistochemical method. A basic protocol is described to prepare the midgut (ventriculus) and hypopharyngeal glands (HPGs) of adult bees for histological analysis. A detailed methodology is described to assess the level of cell damage and distinguish necrosis from programmed cell death (apoptosis) as a natural process of tissue regeneration. The results of adult honeybee treatment with oxalic acid and pesticides (insecticide and acaricide) and the determination of cell death in the ventriculus and HPGs are presented. The pros and cons of the methodology are also discussed.

Immunohistochemical methods are useful in honeybee research to detect and assess the level of apoptosis and necrosis in the midgut and hypopharyngeal glands of adult bees.

Honeybees (Apis mellifera L.) inside the hive (nurse workers and other hive bees) and outside the hive (foragers) are exposed to climate and weather ...

Monitoring Colony-level Effects of Sublethal Pesticide Exposure on Honey Bees

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Empirical, Metagenomic, and Computational Techniques Illuminate the Mechanisms by which Fungicides Compromise Bee Health

Evaluating the Effect of Environmental Chemicals on Honey Bee Development from the Individual to Colony Level

In Vitro Rearing of Solitary Bees: A Tool for Assessing Larval Risk Factors

Monitoring Acupuncture Effects on Human Brain by fMRI

Evaluating the Effect of Pesticides on the Larvae of the Solitary Bees

Studying the Effects of Matrix Stiffness on Cellular Function using Acrylamide-based Hydrogels

Preparation of Single-cohort Colonies and Hormone Treatment of Worker Honeybees to Analyze Physiology Associated with Role and/or Endocrine System

SwarmSight: Real-time Tracking of Insect Antenna Movements and Proboscis Extension Reflex Using a Common Preparation and Conventional Hardware

Assessing Agrochemical Risk to Mated Honey Bee Queens

Histology Basics and Cell Death Detection in Honeybee Tissue