Next Article in Journal
Pathogenicity of Tolypocladium spp. Against Plutella xylostella: Effects on Immune Enzyme Activities and Gene Expression Profile
Previous Article in Journal
Evaluation of Bacterial Strains as a Sustainable Approach for Control of Myzus cerasi (F.) (Hemiptera: Aphididae) Under Laboratory and Field Conditions
Previous Article in Special Issue
Living Control Systems: Exploring a Teleonomic Account of Behavior in Apis mellifera
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Assessing the Productivity of Colonies Headed by Preheated Honeybee Queens

by
Abd Al-Majeed Al-Ghzawi
1,*,
Shahera Talat Zaitoun
2,
Mohammad Nafi Solaiman Al-Sabi
3,
Salem Saleh Mazari
4,
Ilham Mustafa Al-Omari
1 and
Maqbool Saed Altalhi
5
1
Department of Plant Production, Faculty of Agriculture, Jordan University of Science and Technology, P.O. Box 3030, Irbid 22110, Jordan
2
Department of Plant Production & Protection, Faculty of Agricultural Technology, Al-Balqa Applied University, P.O. Box 206, Salt 19117, Jordan
3
Department of Basic Medical Veterinary Sciences, Jordan University of Science and Technology, P.O. Box 3030, Irbid 22110, Jordan
4
Ministry of Agriculture, P.O. Box 2099, Amman 11181, Jordan
5
Taif Beekeepers Cooperative Society, TIDA2375, Taif 26724, Saudi Arabia
*
Author to whom correspondence should be addressed.
Insects 2025, 16(8), 858; https://doi.org/10.3390/insects16080858
Submission received: 19 June 2025 / Revised: 4 August 2025 / Accepted: 15 August 2025 / Published: 18 August 2025

Simple Summary

Preheat hardening in the immature stages causes marked changes in the morphology of honeybee workers. In this study, we investigated the effects of such preheat hardening on the reproductive capacity of honeybee queens and the subsequent productivity of the workers. We found that heat-treated queens produced workers that had significantly increased numbers of brood cells and worker adults, especially during the hot summer months. These workers also managed to collect and store more pollen, had less tendency to rear drone brood, and constructed fewer swarm cells than non-heat-treated workers. We therefore propose the use of heat hardening to compensate for the current loss of honeybees globally.

Abstract

This study investigated the effects of preheat hardening on the egg-laying capacity of honeybee queens and the flight performance of their daughter workers. A honeybee queen was confined in a cage with a two-section frame for 12 h. Then, 48 h old eggs from one section were incubated for 15 min at 41 °C and 70% relative humidity (RH). The queens (n = 12) raised in this section were named the pre-heat-treated queens (pH-TQs). Eggs from the second section were exposed to 34.5 °C and 70% RH for 15 min, and the queens raised in this section were named the non-heat-treated queens (nH-TQs) (n = 12). After mating, both groups were introduced to queenless hives in order to produce workers. The results show that, during the study period (2021 and 2022), the colonies headed by the pH-TQs reared significantly more brood cells and worker adults (especially during the summer), collected and stored more pollen, had less tendency to rear drone brood, and constructed fewer swarm cells than the colonies headed by the nH-TQs. Preheat hardening can be a promising method for improving honeybee workers’ reproductive potential and adaptability, allowing for better adaptation to environmental changes, thus compensating for the mass fatalities of honeybees globally.

1. Introduction

In recent decades, heat has been increasingly used for the control of various pests causing economic harm, as well as for the control of food and non-food items in stores [1,2,3], plant diseases [4], human therapy [5], Varroa mites inside hives [6,7], certain honeybee fungal diseases [8], and viral diseases [9]. In a more advanced step of utilizing heat, several studies have demonstrated that the thermal manipulation of honeybee queens with non-lethal heat shock during the egg stage has beneficial effects on the subsequent physiology and behavior of their daughter workers. This is defined as rapid heat hardening and has been practiced to improve the survival of bees [10,11]. Honeybees show a marked response to heat exposure in terms of physiology [12], including changes in antioxidant and detoxification enzymes [13]; adjustments in metabolism and nutrient supply [14,15]; an increase in gene expression levels when exposed to heat, cold, and starvation stress [16,17,18]; and, in queens and workers, even a change in color [19]. In terms of the behavioral responses to heat exposure [20,21], honeybees also show changes in their development [22], immunity [23], phenology [24], ability to learn [20,25], behavioral performance [26,27], disease susceptibility [28], and flight behavior [21,29].
To overcome temperature fluctuations and prevent extremely high temperature levels inside the hive, honeybee workers in the colony strictly keep it within a range of 33–36 °C. This is because the brood is very sensitive to changes in the hive temperature [30]. It has been previously reported that the danger of overheating is mitigated by behavioral changes in the workers, including the activation of fanning behavior, i.e., rapid vibration of the wings [31]; collecting and depositing water inside the hive to allow for evaporative cooling [32]; relocating bees outside the entrance to facilitate continuous ventilation and evaporation inside the hive [33]; and shielding honey and brood combs from sources of external heat [34]. These and other behaviors have allowed the honeybee subspecies to successfully live in a wide range of climates, from hot and dry to tropical and temperate climates.
To the best of our knowledge, the effects of the heat shock treatment of honeybee queens during the developmental stages on brood rearing and worker populations have not yet been investigated. We hypothesized that the exposure of honeybee queens to non-lethal heat shock during the egg stage could improve their viability and workers’ honey production. The results of this study help determine whether exposure to high temperatures during the developmental stages adjusts the queen’s egg-laying capacity. Furthermore, they provide a scientific basis for further exploration of the temperature adaptation mechanism of queen honeybees, ultimately helping to formulate a comprehensive improvement program.

2. Materials and Methods

2.1. Queen Rearing and Thermal Manipulation

The origin of the experimental colonies (n = 24) was healthy honeybees headed by the local race, the Syrian honeybee (Apis mellifera syriaca), selected from a privately owned apiary in northern Jordan. The colony queens were reared in April 2020, which is known to be the prime month for open mating in the Jordan Valley [35]. A queen from a colony was confined in a queen excluder with a two-section frame for 12 h to produce eggs of approximately the same age. Just before egg hatching (48 h old), both sections were taken from the colony after brushing the nurses off, and they were transferred to the lab at Agri-JUST. The first section was incubated at 41 °C and 70% relative humidity (RH) for 15 min and then returned to its mother hive. After egg hatching, the first-instar worker larvae were grafted to queen cups to be raised in a queenless hive, following standard apicultural procedures [36]. The queens raised under this treatment were named the pre-heat-treated queens (pH-TQs). The second section was exposed to 34.5 °C and 70% RH for 15 min and then returned to its mother hive. After egg hatching, the same procedure was followed to rear non-heat-treated queens (nH-TQs) as the control. Just before pupal emergence, plastic mesh cages were fitted over the occupied pupal queen cells of both groups to retain the emerging virgin queens. The emerging virgin queens in both groups were removed from the plastic mesh cages and introduced to queenless mating mini-hives. These hives were inspected two weeks later to ensure the success of the introduction and the onset of oviposition. From each treatment group, 12 queens were introduced to queenless experimental colonies following standard procedures [36]. Six months later, the experimental colonies were well established, occupying 8–10 frames. Before the commencement of the study in November, each colony was treated with amitraz against Varroa mites, and all experimental colonies were equalized to include a similar amount/number of stored food, brood, and adult bees.
During the investigation, the colonies were subjected to various apiculture practices, including shading, feeding, supering, and external pest control, as needed. The same procedure was repeated to produce new colonies headed by new queens treated in the same manner as above for use in the second year of the study.

2.2. Apicultural Practices

As usually practiced by beekeepers in Jordan, from November to April, the experimental colonies were placed on a designated farm in Shuna North in the Jordan Valley (32°37′′ N, 35°36′′ E), which is 200 m below sea level. Throughout this period, warm weather conditions prevailed in the Jordan Valley, together with the early flowering of cultivated and wild plants. As the temperatures increased and the wild and cultivated plants dried out in the Jordan Valley, the experimental colonies were relocated to the highlands in an apiary located in the Karak district (31°16′′ N, 35°28′′ E), with an elevation of 920 m above sea level. The same practices were repeated in the second year of the study. To reduce bee drifting, the locations of the hives were selected to ensure good protection from the wind. A total of 24 hives headed by pH-TQs and nH-TQs (n = 12 each) were randomly placed in each location in two rows; the rows were spaced four meters apart, while the hives in each row were spaced two meters apart.

2.3. Measurement of Worker and Drone Brood Areas

To estimate the cumulative worker and drone production and emergence patterns in a colony, the sealed brood area of each caste was measured throughout the season. This was carried out by placing a clear plastic grid marked out in 5 × 5 cm squares over the brood on one side of each frame and estimating the number of sealed cells in each quadrat [37].

2.4. Count of Adult Workers

The numbers of worker bees in the pH-TQ and nH-TQ colonies were counted at 21-day intervals throughout the experiment using the procedures described by Gerig [37]. The same counting method was employed in visual estimations of the numbers of brood, drone brood, and stored pollen cells and adult workers per unit area. When two counts were recorded in the same month, the average was calculated.

2.5. Count of Swarm Queen Cells

All pH-TQ and nH-TQ colonies were inspected at 10-day intervals throughout the swarming period. Queen cups and swarm queen cells with laid eggs or larvae in brood chambers were counted and destroyed. This was carried out between February and May during the study period from 2021 to 2022.

2.6. Reporting Pollen Foraging Percentage per Hour

The number of foragers returning to the entrance of each experimental colony was counted for a one-minute duration on an hourly basis between 06.00 AM and 4.00 PM for one day every two weeks. Pollen foragers were defined as workers returning to their colonies with a pollen load, while non-pollen foragers were defined as workers returning with no pollen load [38]. The pollen foraging percentage of a colony was calculated by dividing the number of returning bees with a pollen load by the total number of returning worker foragers to their hives and multiplying by 100.

2.7. Count of Stored Pollen Cells

The amount of pollen stored inside the colonies was measured using the same procedure used for bee and brood counting [37].

2.8. Weight of Pollen Loads

Pollen samples were collected using pollen traps fitted to the entrances of both the pH-TQ and nH-TQ colonies for one day every two weeks. The accumulated pollen was removed, cleaned, and dried at room temperature. Ten pollen loads from each hive were randomly selected from each pollen trap on each sampling date. The weight of each pollen load was obtained to the nearest 0.1 milligram (mg) using a technical balance (Scientech SP 350, Scientech, Boulder, CO, USA).

2.9. Statistical Analysis

All statistical analyses were performed using the R statistical system, Version 4.4.3 [39]. Data are expressed as means ± standard deviation (SD). A repeated-measures ANOVA with a generalized eta-squared test and the F statistic was employed to compare different parameters in all treatment groups. Each treatment was replicated twelve times. Differences were considered significant at p < 0.05.

3. Results

3.1. Brood-Rearing Activities

The colonies headed by the pH-TQs and nH-TQs showed a triple cycle of brood cell numbers within the two study years of 2021 and 2022 (Figure 1). Both colony groups started brood rearing based on the availability of nectar and pollen plants and the suitability of weather conditions in the Jordan Valley, reaching the entire season’s maximum peak in March (35,700 and 27,512 cells, respectively). The pH-TQ colonies reared significantly more brood areas (p < 0.001) than the nH-TQ colonies during the steep rise in brood rearing between February and March. After the colonies migrated to the highlands, where the air temperature and wildflowers were suitable, the pH-TQ colonies showed a significantly higher (p < 0.001) second brood peak than the nH-TQ colonies in May (28,454 and 22,454 cells, respectively). The critical period for beekeeping started with the increase in air temperature and the drying of wildflowers by June, and, thereafter, both colony groups showed a decrease in brood-rearing activities. The pH-TQ colonies were less affected by high-temperature stress, and they reared significantly larger (p < 0.001) brood areas than the nH-TQ colonies from May to the end of the season. In the autumn, when the air temperature was suitable and certain fruit trees began to flower, the pH-TQ colonies showed a third brood peak with a significantly larger (p < 0.001) brood area than the nH-TQ colonies (20,191 and 10,891 cells, respectively). A repeated-measures ANOVA showed a significant difference in the number of brood cells between the pH-MQ and nH-MQ groups (F (1, 574) = 147.10, p < 0.001).

3.2. Honeybee Worker Population

The annual cycle of the bees corresponded to the rate of brood rearing, and the maximum number of adults lagged behind the maximum rate of brood rearing. Both groups (the pH-TQ and nH-TQ colonies) showed a triple cycle of the worker population during the two study years of 2021 and 2022 (Figure 2). The pH-TQ colonies produced a significantly larger (p < 0.001) worker population than the nH-TQ colonies in April (35,033 and 28,366 workers, respectively) and in June (31,466 and 25,866 workers, respectively). During the summer, the pH-TQ colonies showed a steep reduction in worker numbers, while the nH-TQ colonies showed a sharp reduction in their worker numbers. The pH-TQ colonies showed a higher heat tolerance during the summer months and maintained significantly higher (p < 0.001) worker numbers throughout the period from June to the end of the year. After the cessation of the hot summer months, both groups of honeybee colonies, headed by the pH-TQs and nH-TQs, showed a triple peak in the worker population, with a significantly larger (p < 0.001) population in the pH-TQ colonies than in the nH-TQ colonies (22,625 and 16,600 cells, respectively). The seasonal fluctuations in brood-rearing activities and worker bee populations were fairly constant in terms of both time and relative magnitude throughout the two years of the study. The brood-rearing performance and population dynamics of the adult bees tended to follow the same general cycles in the second year of the study (Figure 2). A repeated-measures ANOVA showed a significant difference in the monthly changes in worker numbers between the pH-MQ and nH-MQ groups (F (1, 574) = 47.68, p < 0.001).

3.3. Drone Brood Rearing

The colonies headed by the pH-TQ and nH-TQ queens showed a single cycle of drone brood cell numbers within the two study years of 2021 and 2022 (Figure 3). In both groups of colonies, drone brood rearing began in February and ceased in June. The nH-TQ colonies reared significantly more (p < 0.001) drone brood cells (310.3 cells) than the pH-TQ colonies (1675.0 cells in 2021). A repeated-measures ANOVA showed a significant difference in the number of drone brood cells between the pH-MQ and nH-MQ groups (F (1, 574) = 102.13, p < 0.001).

3.4. Swarm Cells

The pH-TQ and nH-TQ colonies showed swarm cell construction between March and May of each year of the study period (Figure 4). In the first year of the investigation, the nH-TQ colonies constructed significantly (p < 0.001) more swarm cells in April (120 cells) than the pH-TQ colonies (74.8 cells). A repeated-measures ANOVA showed a significant difference in the number of swarm queen cells between the pH-MQ and nH-MQ groups (F (1, 574) = 139.81, p < 0.001).

3.5. Pollen Foraging Percentage per Hour

The workers in both colony groups, headed by the pH-TQs and nH-TQs, started foraging very early in the day at six o’clock (Figure 5). The pH-TQ colonies showed a significantly (p < 0.001) higher foraging rate from 8 AM to the end of the day than the nH-TQ colonies. A repeated-measures ANOVA showed a significant difference in the hours of flight time between the pH-MQ and nH-MQ groups (F (1, 574) = 23.96, p < 0.001).

3.6. Stored Pollen Cells

The number of stored pollen cells in both the pH-TQ and nH-TQ colonies fluctuated between the months of the year (Figure 6). The pH-TQ colonies stored significantly (p < 0.001) more pollen cells than the nH-TQ colonies in March (14,350 and 10,100 workers, respectively) and in May (12,167 and 8.275 cells, respectively). The pH-TQ colonies were more tolerant of high-temperature stress than the nH-TQ colonies, showing more active flying outside the hives and storing significantly more pollen cells (p < 0.001) during the summertime between May and August. In the autumn, when the air temperatures were more suitable and certain fruit trees began to flower, the pH-TQ colonies again stored significantly more pollen cells (p < 0.001) than the nH-TQ colonies (6238 and 1638 cells, respectively). In both colony groups, pollen storage was the lowest between December and February, when cold weather prevailed. A repeated-measures ANOVA showed a significant difference in the number of stored pollen cells between the pH-MQ and nH-MQ groups (F (1, 574) = 64.93, p < 0.001).

3.7. Monthly Percentage of Pollen Foragers

Workers in both the pH-TQ and nH-TQ colonies tended to collect pollen throughout the two years of the study (Figure 7). In both colony groups, the highest percentage of returning workers, reflecting the flying activity, was observed in March and June of each year. During the period from May to the end of the year, the average percentage of returning workers loaded with pollen grains in the pH-TQ colonies was significantly (p < 0.001) higher than that in the nH-TQ colonies. The forager percentages in the pH-TQ colonies were significantly (p < 0.001) higher in March, May, and October (76, 67.2, and 31.5%, respectively) than those in the nH-TQ colonies (61.2, 60.1, and 17.0%, respectively). A repeated-measures ANOVA showed a significant difference in the monthly pollen forager percentages between the pH-MQ and nH-MQ groups (F (1, 574) = 31.88, p < 0.001).

3.8. Weight of 10 Pollen Loads

The average weight of 10 pollen loads carried by the workers in the pH-TQ colonies was significantly heavier than that carried by the workers in the nH-TQ colonies between the period from May to the end of the year (Figure 8). The heaviest pollen loads were recorded from March to May for both the pH-TQ and nH-TQ colonies. The workers in the pH-TQ colonies carried significantly (p < 0.001) heavier pollen loads in March, May, and October 2021 (195.1, 195, and 114.2 mg, respectively) than those in the nH-TQ colonies (165.1, 139.5, and 68.3 mg, respectively). A repeated-measures ANOVA showed a significant difference in the pollen load weight between the pH-MQ and nH-MQ groups (F (1, 574) = 48.05, p < 0.001).
In the second year of the study (2022), the trends in brood rearing, worker population, pollen collection and storage, swarm cell construction, and drone brood rearing in the pH-TQ and nH-TQ colonies tended to be the same and were consistent in terms of time (Figure 1, Figure 2, Figure 3, Figure 4, Figure 5, Figure 6, Figure 7 and Figure 8). Supplementary Materials can be found in the link provided at the end of this article.

4. Discussion

4.1. Effect of Preheat Hardening on the Survival of Honeybee Workers

Overall, the results of the current investigation show that the preheat hardening of honeybee queens during one of their immature stages is a promising method for significantly improving the productive potential of honeybee colonies. Rapid heat hardening generally refers to a rapid improvement in survival at high lethal temperatures following brief pre-exposure to a sub-lethal temperature shock [10,11]. This study found that honeybee colonies headed by heat-treated queens (pH-TQs) and non-treated queens (nH-TQs) exhibited a triple cycle of brood rearing and adult populations within a year. The three peaks of the brood cells observed in March, May, and October of each year were comparable to those of the stored pollen inside the experimental colonies. The pollen foraging tendency of honeybee colonies depends on the genotype, seasonal availability, number of larvae, and amount of stored pollen [40,41]. The activity of pollen foragers depends on the flowering time of the plant species and the outside temperature [42]. A previous study found that an ambient temperature of 20 °C stimulated the highest foraging activity, while an ambient temperature of 43 °C resulted in the lowest activity [43]. Flying outside the hive under elevated temperatures may alter foraging behavior [44]. In addition to facing heat stress during their foraging activities, bees might also suffer from problems with their thorax, which is crucial for their ability to fly. Honeybee workers show prolonged flight only with thorax temperatures between 29 and 49 °C [45,46].

4.2. Effect of Preheat Hardening on Brood Numbers

For honeybees to successfully grow, reproduce, and build strong colonies, they must have access to enough flowering plant resources at the right time [47]. Honeybee foragers collect nectar, pollen, and water from flowering plants [48]. Importantly, pollen grains are the sole nitrogenous source of food for brood rearing, normal development, worker longevity, and sustaining the requirements of other members of the hive [49,50]. Here, the observed decline in brood rearing for a short period in April can be explained by the reduced foraging activities of the worker bees, and these can be attributed to the local high temperatures, the seasonal east sandstorm event, the low relative humidity from the end of March to April in the Jordan Valley, and fewer places for egg laying due to the storage of honey in the brood areas inside the hives. The second reduction in brood rearing was recorded starting from June, and it was presumably due to the abundant incoming nectar and pollen deposited in the brood area after transporting the bee colonies to the upland areas of Jordan. This activity may have restricted the number of cells available to the queen for ovipositing. A reasonable gradual decrease in incoming nectar and pollen was expected during the hot, summer period from July to September, with a simultaneous rapid decrease in brood-rearing activities. The third reduction in brood rearing was observed in November with a brood stop; this was probably because of the prevailing ambient cold conditions preventing the workers from flying effectively outside the hives, as well as the reduced flowering of wild and cultivated plants. These observations are in alignment with those previously reported under semiarid conditions in the same study area [51] and in other parts of the world [52].

4.3. Changes Induced by Preheat Hardening on Honeybee Workers

In this study, both experimental honeybee colonies headed by the pH-TQs and nH-TQs were subjected to the same environmental conditions of the mild spring months and hot dry weather conditions prevailing during the summers in Jordan. Similarly to other colonies, the workers in both groups developed mechanisms to regulate their thoracic temperature, prevent overheating, and remain active across wide ranges of air temperatures [53]. During the summer and later months from May to the end of the year, the colonies headed by the pH-TQs built significantly more brood areas, produced more workers, and collected more pollen than the colonies headed by the nH-TQs. These differences could be due to differences in innate mechanisms, such as changes in the expression of heat shock proteins (HSPs), an increased rate of heat loss, and a decreased rate of metabolic heat synthesis to prevent thorax overheating [53,54]. Moreover, the increased productivity of the pH-TQ colonies compared to that of the nH-TQ colonies may be attributed to the rapid synthesis of heat resistance substances, such as mannitol and sorbitol, both of which have been linked to increased heat tolerance in insects [55,56,57]. Any or all of these factors could explain the improvement in the natural foraging activities of the workers in the colonies headed by the preheated queens (pH-TQs), consequently increasing the amounts of nectar and pollen collected during the hot months and until the end of the year. This increased activity of pollen collection probably led to the increase in brood rearing and, subsequently, the increase in the worker population.
Previous studies have shown that rapid heat hardening in animals during the immature stages results in the production of individuals with improved body characteristics, represented by a larger body size, weight, and body organs [58,59,60]. These changes are further expressed in changes in the performance of the subsequent adult stages [61,62]. Examples of the effects of rapid heat hardening on the body morphology of insects are as follows: an increase in the body size of the ground cricket Allonemobius socius, the leafhopper Scaphoideus titanus, and the speckled wood butterfly (Parage aegeria) [62,63]; an increase in the body weight of Harmonia axyridis [64]; and an increase in the wing size of Drosophila mercatorum and the hoverfly Eristalis arbustorum [65,66]. The changes in the body morphology of worker honeybees due to heat hardening are currently under investigation by the authors.
The increase in the body size of insects may contribute to better heat tolerance and therefore increased productivity. In ants, an increase in the body size of workers can significantly improve their heat tolerance [67,68,69]. In bees, larger workers can reach flowering resources more quickly and over a greater distance than their smaller counterparts, thereby resulting in a better foraging scope and a higher pollen load [70,71]. Foraging for long distances with a better adaptability to hot weather conditions can explain the currently observed improved pollen collection of the pH-MQs. Furthermore, such an increased food supply inside the hive can accelerate the queens’ egg-laying activity, thereby resulting in a larger worker population. Moreover, in accordance with metabolic scaling theory [72], the energy efficiency of insect flight increases with body mass [73,74,75], with larger insects exhibiting different flight kinematics expressed in different wingbeat frequencies [74,75]. Another important consideration here is the capacity of individuals to store food. Across insects, the absolute energy demand for flight is generally greater in larger-bodied individuals, which can be compensated for by greater baseline endogenous energy stores. This results in an increased flight endurance capacity with an increasing insect body size [76].
Resistance to extremely high ambient temperatures is achieved by a combination of qualities strongly affected by a prior-experienced environment [77]. Preheat hardening results in the enhanced expression of several heat shock proteins (HSPs) [56,78,79]. The expression of HSPs was found to be significantly associated with improved heat resistance [80,81] and might help prolong life [82], hence rendering the bees more tolerant to heat changes and better adapted to increased ambient temperatures. Additionally, preheat hardening was previously linked to the induction of immune gene expression [83], which might enhance the insects’ responses to parasitic pathogens and stresses or unfavorable conditions [84]. Such an increase in the tolerance of bees might further lead to better flight foraging frequencies outside the hive. Additionally, previous studies showed that preheat hardening induces the expression of oxidative stress genes that diminish the adverse effects of free radicals, such as reactive oxygen species (ROS) [85,86]. The cellular scavenging of ROS was previously linked to a reduction in the oxidative stress imposed on honeybees, which was further linked to an increase in the lifespan of both honeybee workers and queens [87,88].

5. Conclusions

The current results show that exposing mother queens to non-lethal heat shock has positive effects on their reproduction and further improves the resilience of their worker daughters to environmental stressors. The increased ability of honeybee workers to collect nectar and pollen during the hot summer months indicates that they have a higher tolerance to ambient heat and allows them to overcome food shortages, which may compensate for the ongoing decline in bee populations locally and globally. In the context of beekeeping, we recommend that beekeepers expose honeybee queens to preheat hardening in their immature stages as a method to improve their subsequent daughter workers. This could be an effective way to maintain beehives and improve the heat tolerance of treated bees. Future studies examining the impact of preheat hardening on honeybee immunity and other factors involved in improving honeybee tolerance and adaptation to different stress conditions are recommended.

Supplementary Materials

The following supporting information can be downloaded at: https://www.mdpi.com/article/10.3390/insects16080858/s1, Table S1: Repeated Measures ANOVA Results for Hive Parameters (2021–2022). TM: thermally manipulated.

Author Contributions

Conceptualization, resources, visualization, supervision, funding acquisition, A.A.-M.A.-G. and S.T.Z.; methodology, validation, formal analysis, investigation, A.A.-M.A.-G., S.T.Z., I.M.A.-O., and M.S.A.; data curation, A.A.-M.A.-G., S.T.Z., M.N.S.A.-S., S.S.M., I.M.A.-O., and M.S.A.; writing—original draft preparation, writing—review and editing, A.A.-M.A.-G., S.T.Z., M.N.S.A.-S., and I.M.A.-O. All authors have read and agreed to the published version of the manuscript.

Funding

The authors thank the Deanship of Scientific Research at Jordan University of Science and Technology for funding the work through research grant no. 431/2021 and grant no. 386/2023.

Data Availability Statement

The original data presented in the study are openly available in https://drive.google.com/drive/folders/1o62SHEW9xL5OBC6ZxBEIT4BEi5fjOMkh?usp=sharing, (accessed on 22 May 2025).

Acknowledgments

We acknowledge Yousef Al-Ghzawi for performing the statistical analysis. We also acknowledge Al-Balqa Applied University, Salt, for their essential logistical support. We extend our acknowledgement to the reviewers and the editor whom their comments have improved the quality of this article.

Conflicts of Interest

The authors declare no conflicts of interest. The funders had no role in the design of the study; in the collection, analyses, or interpretation of data; in the writing of the manuscript; or in the decision to publish the results.

Abbreviation

The following abbreviations are used in this manuscript:
pH-TQ Pre-heat-treated queens
nH-TQnon-heat-treated queens
RHRelative humidity

References

  1. Vincent, C.; Hallman, G.; Panneton, B.; Fleurat-Lessard, F. Management of agricultural insects with physical control methods. Annu. Rev. Entomol. 2003, 48, 261–281. [Google Scholar] [CrossRef]
  2. Beckett, S.; Fields, P.; Subramanyam, B. Disinfestation of stored products and associated structures using heat. In Heat Treatments for Postharvest Pest Control: Theory and Practice; CABI: Wallingford, UK, 2007; pp. 182–237. [Google Scholar]
  3. Hansen, J.D.; Johnson, J.A.; Winter, D.A. History and use of heat in pest control: A review. Int. J. Pest. Manag. 2011, 57, 267–289. [Google Scholar] [CrossRef]
  4. Grondeau, C.; Samson, R.; Sands, D.C. A Review of Thermotherapy to Free Plant Materials from Pathogens, Especially Seeds from Bacteria. Crit. Rev. Plant Sci. 1994, 13, 57–75. [Google Scholar] [CrossRef]
  5. Wang, Y.; Li, S.; Zhang, Y.; Chen, Y.; Yan, F.; Han, L.; Ma, Y. Heat and cold therapy reduce pain in patients with delayed onset muscle soreness: A systematic review and meta-analysis of 32 randomized controlled trials. Phys. Ther. Sport 2021, 48, 177–187. [Google Scholar] [CrossRef] [PubMed]
  6. Harbo, J.R. Heating adult honeybees to remove Varroa jacobsoni. J. Apic. Res. 2000, 39, 181–182. [Google Scholar] [CrossRef]
  7. Goras, G.; Tananaki, C.; Gounari, S.; Dimou, M.; Lazaridou, E.; Karazafiris, E.; Kanelis, D.; Liolios, V.; El Taj, H.F.; Thrasyvoulou, A. Hyperthermia non-chemical control strategy against varroa. J. Hell. Vet. Med. Soc. 2015, 66, 249–256. [Google Scholar] [CrossRef]
  8. Martin-Hernandez, R.; Meana, A.; Garcia-Palencia, P.; Marin, P.; Botias, C.; Garrido-Bailon, E.; Barrios, L.; Higes, M. Effect of temperature on the biotic potential of honeybee microsporidia. Appl. Environ. Microbiol. 2009, 75, 2554–2557. [Google Scholar] [CrossRef]
  9. McMenamin, A.J.; Daughenbaugh, K.F.; Flenniken, M.L. The Heat Shock Response in the Western Honeybee (Apis mellifera) is Antiviral. Viruses 2020, 12, 245. [Google Scholar] [CrossRef]
  10. Chidawanyika, F.; Terblanche, J.S. Rapid thermal responses and thermal tolerance in adult codling moth Cydia pomonella (Lepidoptera: Tortricidae). J. Insect Physiol. 2011, 57, 108–117. [Google Scholar] [CrossRef]
  11. Mutamiswa, R.; Chidawanyika, F.; Nyamukondiwa, C. Superior basal and plastic thermal responses to environmental heterogeneity in invasive exotic stemborer Chilo partellus Swinhoe over indigenous Busseola fusca (Fuller) and Sesamia calamistis Hampson. Physiol. Entomol. 2018, 43, 108–119. [Google Scholar] [CrossRef]
  12. Dalmon, A.; Peruzzi, M.; Le Conte, Y.; Alaux, C.; Pioz, M. Temperature-driven changes in viral loads in the honey bee Apis mellifera. J. Invertebr. Pathol. 2019, 160, 87–94. [Google Scholar] [CrossRef]
  13. Li, X.; Ma, W.; Shen, J.; Long, D.; Feng, Y.; Su, W.; Xu, K.; Du, Y.; Jiang, Y. Tolerance and response of two honeybee species Apis cerana and Apis mellifera to high temperature and relative humidity. PLoS ONE 2019, 14, e0217921. [Google Scholar] [CrossRef]
  14. Ahamed, M.; Posgai, R.; Gorey, T.J.; Nielsen, M.; Hussain, S.M.; Rowe, J.J. Silver nanoparticles induced heat shock protein 70, oxidative stress and apoptosis in Drosophila melanogaster. Toxicol. Appl. Pharmacol. 2010, 242, 263–269. [Google Scholar] [CrossRef]
  15. Xu, H.; Miao, X.; Wang, W.; Wang, G.; Li, Y. Transcriptome analysis reveals the early resistance of zebrafish larvae to oxidative stress. Fish Physiol. Biochem. 2022, 48, 1075–1089. [Google Scholar] [CrossRef]
  16. Elekonich, M.M. Extreme thermotolerance and behavioral induction of 70-kDa heat shock proteins and their encoding genes in honey bees. Cell Stress Chaperones 2009, 14, 219–226. [Google Scholar] [CrossRef] [PubMed]
  17. Severson, D.W.; Erickson, E.H.; Williamson, J.L., Jr.; Aiken, J.M. Heat stress induced enhancement of heat shock protein gene activity in the honey bee (Apis mellifera). Experientia 1990, 46, 737–739. [Google Scholar] [CrossRef]
  18. Ramirez, L.; Luna, F.; Mucci, C.A.; Lamattina, L. Fast weight recovery, metabolic rate adjustment and gene-expression regulation define responses of cold-stressed honey bee brood. J. Insect Physiol. 2021, 128, 104178. [Google Scholar] [CrossRef] [PubMed]
  19. Degrandi-Hoffman, G.; Spivak, M.; Martin, J.H. Role of thermoregulation by nestmates on the development time of honey bee (Hymenoptera: Apidae) queens. Ann. Entomol. Soc. Am. 1993, 86, 165–172. [Google Scholar] [CrossRef]
  20. Tautz, J.; Maier, S.; Groh, C.; Rössler, W.; Brockmann, A. Behavioral performance in adult honey bees is influenced by the temperature experienced during their pupal development. Proc. Natl. Acad. Sci. USA 2003, 100, 7343–7347. [Google Scholar] [CrossRef]
  21. Abou-Shaara, H.; Owayss, A.A.; Ibrahim, Y.; Basuny, N. A review of the impacts of temperature and relative humidity on various activities of honey bees. Insectes Sociaux 2017, 64, 455–463. [Google Scholar] [CrossRef]
  22. Chuda-Mickiewicz, B.; Samborski, J. The quality of honey bee queens from queen cells incubated at different temperatures. Acta Sci. Pol. Zootech. 2015, 14, 25–32. [Google Scholar]
  23. Medina, R.G.; Paxton, R.J.; Hernandez-Sotomayor, S.M.T.; Pech-Jimenez, C.; Medina-Medina, L.A.; Quezada-Euan, J.J.G. Heat stress during development affects immunocompetence in workers, queens and drones of Africanized honey bees (Apis mellifera L.) (Hymenoptera: Apidae). J. Therm. Biol. 2020, 89, 102541. [Google Scholar] [CrossRef] [PubMed]
  24. Langowska, A.; Zawilak, M.; Sparks, T.H.; Glazaczow, A.; Tomkins, P.W.; Tryjanowski, P. Long-term effect of temperature on honey yield and honeybee phenology. Int. J. Biometeorol. 2017, 61, 1125–1132. [Google Scholar] [CrossRef] [PubMed]
  25. Jones, J.C.; Helliwell, P.; Beekman, M.; Maleszka, R.; Oldroyd, B.P. The effects of rearing temperature on developmental stability and learning and memory in the honey bee, Apis mellifera. J. Comp. Physiol. A Neuroethol. Sens. Neural Behav. Physiol. 2005, 191, 1121–1129. [Google Scholar] [CrossRef]
  26. Alqarni, A.S. Tolerance of summer temperature in imported and indigenous honeybee Apis mellifera L. races in central Saudi Arabia. Saudi J. Biol. Sci. 2006, 13, 123–127. [Google Scholar] [CrossRef]
  27. Blažytė-Čereškienė, L.; Vaitkevičienė, G.; Venskutonytė, S.; Būda, V. Honey bee foraging in spring oilseed rape crops under high ambient temperature conditions. Zemdirbyste 2010, 79, 61–70. [Google Scholar]
  28. Le Conte, Y.; Navajas, M. Climate change: Impact on honey bee populations and diseases. Revue Scientif. Techn. 2008, 27, 499–510. [Google Scholar] [CrossRef]
  29. Abou-Shaara, H.F.; Al-Ghamdi, A.A.; Mohamed, A.A. Tolerance of two honeybee races to various temperature and relative humidity gradients. Environ. Exp. Biol. 2012, 10, 133–138. [Google Scholar]
  30. Stabentheiner, A.; Kovac, H.; Brodschneider, R. Honeybee colony thermoregulation–regulatory mechanisms and contribution of individuals in dependence on age, location and thermal stress. PLoS ONE 2010, 5, e8967. [Google Scholar] [CrossRef]
  31. Southwick, E.E.; Moritz, R.F.A. Social control of air ventilation in colonies of honey bees, Apis mellifera. J. Insect Physiol. 1987, 33, 623–626. [Google Scholar] [CrossRef]
  32. Nicolson, S.W. Water homeostasis in bees, with the emphasis on sociality. J. Exp. Biol. 2009, 212, 429–434. [Google Scholar] [CrossRef]
  33. Stabentheiner, A.; Kovac, H.; Mandl, M.; Käfer, H. Coping with the cold and fighting the heat: Thermal homeostasis of a superorganism, the honeybee colony. J. Comp. Physiol. 2021, 207, 337–351. [Google Scholar] [CrossRef]
  34. Starks, P.T.; Gilley, D.C. Heat shielding: A novel method of colonial thermoregulation in honey bees. Naturwissenschaften 1999, 86, 438–440. [Google Scholar] [CrossRef]
  35. Al-Ghzawi, A.A.A.; Zaitoun, S. Origin and Rearing Season of Honeybee Queens Affect Some of Their Physiological and Reproductive Characteristics. Entomol. Res. 2008, 38, 139–148. [Google Scholar] [CrossRef]
  36. Laidlaw, H.H.; Page, R.E., Jr. Queen Rearing and Bee Breeding, 1st ed.; Wicwas Press: Cheshire, CT, USA, 1997; p. 224. [Google Scholar]
  37. Gerig, L. Lehrgang zur erfassung der volksstarke. Schweiz. Bienenztg. 1983, 106, 199–204. [Google Scholar]
  38. Ruttner, H. Technical recommendations for methods of evaluating performance of bee colonies. In Controlled Mating and Selection of the Honey Bee; Ruttner, F., Ed.; Apimondia: Bucharest, Romania, 1972; pp. 87–92. [Google Scholar]
  39. R Core Team. R: A Language and Environment for Statistical Computing (Computer Software); R Foundation for Statistical Computing: Vienna, Austria, 2021. [Google Scholar]
  40. Camazine, S. The regulation of pollen foraging by honey bees: How foragers assess the colony's need for pollen. Behav. Ecol. Sociobiol. 1993, 32, 265–272. [Google Scholar] [CrossRef]
  41. Bilisik, A.; Cakmak, I.; Bicakci, A.; Malyer, H. Seasonal variation of collected pollen loads of honeybees (Apis mellifera L. anatoliaca). Grana 2008, 47, 70–77. [Google Scholar] [CrossRef]
  42. Ghosh, S.; Jeon, H.; Jung, C. Foraging behaviour and preference of pollen sources by honey bee (Apis mellifera) relative to protein contents. J. Ecol. Environ. 2020, 44, 4. [Google Scholar] [CrossRef]
  43. Tan, K.; Yang, S.; Wang, Z.-W.; Radloff, S.E.; Oldroyd, B.P. Differences in foraging and broodnest temperature in the honey bees Apis cerana and A. mellifera. Apidologie 2012, 43, 618–623. [Google Scholar] [CrossRef]
  44. Cooper, P.D.; Schaffer, W.M.; Buchmann, S.L. Temperature Regulation of Honey Bees (Apis mellifera) Foraging in the Sonoran Desert. J. Exp. Biol. 1985, 114, 1–15. [Google Scholar] [CrossRef]
  45. Heinrich, B. Resource heterogeneity and patterns of movement in foraging bumblebees. Oecologia 1979, 40, 235–245. [Google Scholar] [CrossRef] [PubMed]
  46. Coelho, J.R. Heat Transfer and Body Temperature in Honey Bee (Hymenoptera: Apidae) Drones and Workers. Environ. Entomol. 1991, 20, 1627–1635. [Google Scholar] [CrossRef]
  47. Brodschneider, R.; Crailsheim, K. Nutrition and health in honey bees. Apidologie 2010, 41, 278–294. [Google Scholar] [CrossRef]
  48. Thorp, R.W. The collection of pollen by bees. Plant Syst. Evol. 2000, 222, 211–223. [Google Scholar] [CrossRef]
  49. Di Pasquale, G.; Alaux, C.; Le Conte, Y.; Odoux, J.F.; Pioz, M.; Vaissiere, B.E.; Belzunces, L.P.; Decourtye, A. Variations in the Availability of Pollen Resources Affect Honey Bee Health. PLoS ONE 2016, 11, e0162818. [Google Scholar] [CrossRef]
  50. Mattila, H.R.; Otis, G.W. Influence of pollen diet in spring on development of honey bee (Hymenoptera: Apidae) colonies. J. Econ. Entomol. 2006, 99, 604–613. [Google Scholar] [CrossRef]
  51. Zaitoun, S.T.; Al-Ghzawi, A.-M.; Shannag, H.K. Population dynamics of the Syrian Honeybee, Apis mellifera syriaca, under semi-arid Mediterranean conditions. Zool. Middle East 2000, 21, 129–132. [Google Scholar] [CrossRef]
  52. Jeffree, E.P. Observations on the Decline and Growth of Honey Bee Colonies1. J. Econ. Entomol. 1955, 48, 723–726. [Google Scholar] [CrossRef]
  53. Roberts, S.P.; Harrison, J.F. Mechanisms of thermal stability during flight in the honeybee Apis mellifera. J. Exp. Biol. 1999, 202, 1523–1533. [Google Scholar] [CrossRef]
  54. Perez, R.; Aron, S. Adaptations to thermal stress in social insects: Recent advances and future directions. Biol. Rev. Camb. Philos. Soc. 2020, 95, 1535–1553. [Google Scholar] [CrossRef]
  55. Colinet, H.; Lee, S.F.; Hoffmann, A. Temporal expression of heat shock genes during cold stress and recovery from chill coma in adult Drosoph melanogaster. FEBS J. 2010, 277, 174–185. [Google Scholar] [CrossRef]
  56. Al-Ghzawi, A.A.A.; Al-Zghoul, M.B.; Zaitoun, S.; Al-Omary, I.M.; Alahmad, N.A. Dynamics of Heat Shock Proteins and Heat Shock Factor Expression During Heat Stress in Daughter Workers in Pre-Heat-Treated (Rapid Heat Hardening) Apis mellifera Mother Queens. J. Therm. Biol. 2022, 104, 103194. [Google Scholar] [CrossRef]
  57. Zaitoun, S.T.; Al-Ghzawi, A.A.; Al-Zghoul, M.B.; Al-Omary, I.M.; Al-Sabi, M.N.S. Effects of Rapid Heat Hardening of Honeybee Queens (Apis mellifera) During the Larval Stage on the Oxidative Response of Their Workers During Heat Stress. Stresses 2025, 5, 32. [Google Scholar] [CrossRef]
  58. Yahav, S.; Plavnik, I. Effect of early-stage thermal conditioning and food restriction on performance and thermotolerance of male broiler chickens. Br. Poult. Sci. 1999, 40, 120–126. [Google Scholar] [CrossRef]
  59. Yahav, S.; McMurtry, J.P. Thermotolerance acquisition in broiler chickens by temperature conditioning early in life--the effect of timing and ambient temperature. Poult. Sci. 2001, 80, 1662–1666. [Google Scholar] [CrossRef]
  60. Jonsson, B.; Jonsson, N.; Finstad, A.G. Linking embryonic temperature with adult reproductive investment in Atlantic salmon Salmo salar. Mar. Ecol. Prog. Ser. 2014, 515, 217–226. [Google Scholar] [CrossRef]
  61. Gray, E.M. Thermal acclimation in a complex life cycle: The effects of larval and adult thermal conditions on metabolic rate and heat resistance in Culex pipiens (Diptera: Culicidae). J. Insect Physiol. 2013, 59, 1001–1007. [Google Scholar] [CrossRef]
  62. Sgro, C.M.; Terblanche, J.S.; Hoffmann, A.A. What Can Plasticity Contribute to Insect Responses to Climate Change? Annu. Rev. Entomol. 2016, 61, 433–451. [Google Scholar] [CrossRef]
  63. Stevens, D.J. Pupal development temperature alters adult phenotype in the speckled wood butterfly, Pararge aegeria. J. Therm. Biol. 2004, 29, 205–210. [Google Scholar] [CrossRef]
  64. Chuche, J.; Thiery, D. Egg incubation temperature differently affects female and male hatching dynamics and larval fitness in a leafhopper. Ecol Evol. 2012, 2, 732–739. [Google Scholar] [CrossRef] [PubMed]
  65. Zhang, S.; Cao, Z.; Wang, Q.; Zhang, F.; Liu, T.-X. Exposing eggs to high temperatures affects the development, survival and reproduction of Harmonia axyridis. J. Therm. Biol. 2014, 39, 40–44. [Google Scholar] [CrossRef]
  66. Ottenheim, M.M.; Volmer, A.D. Wing length plasticity in Eristalis arbustorum (Diptera: Syrphidae). Neth. J. Zool. 1999, 49, 15–27. [Google Scholar] [CrossRef]
  67. Andersen, D.H.; Pertoldi, C.; Scali, V.; Loeschcke, V. Heat stress and age induced maternal effects on wing size and shape in parthenogenetic Drosophila mercatorum. J. Evol. Biol. 2005, 18, 884–892. [Google Scholar] [CrossRef]
  68. Baudier, K.M.; Mudd, A.E.; Erickson, S.C.; O'Donnell, S. Microhabitat and body size effects on heat tolerance: Implications for responses to climate change (army ants: Formicidae, Ecitoninae). J. Anim. Ecol. 2015, 84, 1322–1330. [Google Scholar] [CrossRef]
  69. Wendt, C.F.; Verble-Pearson, R. Critical thermal maxima and body size positively correlate in red imported fire ants, Solenopsis invicta. Southwest. Nat. 2016, 61, 79–83. [Google Scholar] [CrossRef]
  70. Greenleaf, S.S.; Williams, N.M.; Winfree, R.; Kremen, C. Bee foraging ranges and their relationship to body size. Oecologia 2007, 153, 589–596. [Google Scholar] [CrossRef]
  71. Willmer, P.; Finlayson, K. Big bees do a better job: Intraspecific size variation influences pollination effectiveness. J. Pollinat. Ecol. 2014, 14, 244–254. [Google Scholar] [CrossRef]
  72. Brown, J.H.; Gillooly, J.F.; Allen, A.P.; Savage, V.M.; West, G.B. Toward a metabolic theory of ecology. Ecology 2004, 85, 1771–1789. [Google Scholar] [CrossRef]
  73. Skandalis, D.A.; Darveau, C.A. Morphological and physiological idiosyncrasies lead to interindividual variation in flight metabolic rate in worker bumblebees (Bombus impatiens). Physiol. Biochem. Zool. 2012, 85, 657–670. [Google Scholar] [CrossRef]
  74. Billardon, F.; Darveau, C.A. Flight energetics, caste dimorphism and scaling properties in the bumblebee, Bombus impatiens. J. Exp. Biol. 2019, 222, jeb187807. [Google Scholar] [CrossRef]
  75. Darveau, C.A.; Hochachka, P.W.; Welch, K.C.; Roubik, D.W., Jr.; Suarez, R.K. Allometric scaling of flight energetics in Panamanian orchid bees: A comparative phylogenetic approach. J. Exp. Biol. 2005, 208, 3581–3591. [Google Scholar] [CrossRef] [PubMed]
  76. Kaufmann, C.; Reim, C.; Blanckenhorn, W.U. Size-dependent insect flight energetics at different sugar supplies. Biol. J. Linn. Soc. 2013, 108, 565–578. [Google Scholar] [CrossRef]
  77. Wos, G.; Willi, Y. Thermal Acclimation in Arabidopsis lyrata: Genotypic Costs and Transcriptional Changes. J. Evol. Biol. 2018, 31, 123–135. [Google Scholar] [CrossRef] [PubMed]
  78. Chen, P.C.; Lee, R.E.; Denlinger, D.L. Cold shock and heat shock: A comparison of the protection generated by brief pretreatment at less severe temperatures. Physiol. Entomol. 1991, 16, 19–26. [Google Scholar] [CrossRef]
  79. Alqarni, A.S.; Ali, H.; Iqbal, J.; Owayss, A.A.; Smith, B.H. Expression of heat shock proteins in adult honey bee (Apis mellifera L.) workers under hot-arid subtropical ecosystems. Saudi J. Biol. Sci. 2019, 26, 1372–1376. [Google Scholar] [CrossRef]
  80. Malmendal, A.; Overgaard, J.; Bundy, J.G.; Sorensen, J.G.; Nielsen, N.C.; Loeschcke, V.; Holmstrup, M. Metabolomic Profiling of Heat Stress: Hardening and Recovery of Homeostasis in Drosophila. Am. J. Physiol. Regul. Integr. Comp. Physiol. 2006, 291, R205–R212. [Google Scholar] [CrossRef]
  81. Robert, J. Evolution of heat shock protein and immunity. Dev. Comp. Immunol. 2003, 27, 449–464. [Google Scholar] [CrossRef]
  82. Feder, M.E.; Hofmann, G.E. Heat-shock proteins, molecular chaperones, and the stress response: Evolutionary and ecological physiology. Annu. Rev. Physiol. 1999, 61, 243–282. [Google Scholar] [CrossRef] [PubMed]
  83. Blasco-Lavilla, N.; García-Reina, A.; De la Rúa, P. Mild thermal stress does not negatively affect immune gene expression in the bumblebee Bombus terrestris. Apidologie 2021, 52, 163–173. [Google Scholar] [CrossRef]
  84. Larsen, A.; Reynaldi, F.J.; Guzmán-Novoa, E. Fundaments of the honey bee (Apis mellifera) immune system. Review. Rev. Mex. Cienc. Pecu. 2019, 10, 705–728. [Google Scholar] [CrossRef]
  85. Corona, M.; Robinson, G.E. Genes of the Antioxidant System of the Honey Bee: Annotation and Phylogeny. Insect Mol. Biol. 2006, 15, 687–701. [Google Scholar] [CrossRef] [PubMed]
  86. Santos, D.B.; Colle, D.; Moreira, E.L.G.; Santos, A.A.; Hort, M.A.; Santos, K.; Oses, J.P.; Razzera, G.; Farina, M. Probucol Protects Neuronal Cells Against Peroxide-Induced Damage and Directly Activates Glutathione Peroxidase-1. Mol. Neurobiol. 2020, 57, 3245–3257. [Google Scholar] [CrossRef]
  87. Aurori, C.M.; Buttstedt, A.; Dezmirean, D.S.; Marghitas, L.A.; Moritz, R.F.; Erler, S. What Is the Main Driver of Ageing in Long-Lived Winter Honeybees: Antioxidant Enzymes, Innate Immunity, or Vitellogenin? J. Gerontol. A Biol. Sci. Med. Sci. 2014, 69, 633–639. [Google Scholar] [CrossRef] [PubMed]
  88. Paleolog, J.; Wilde, J.; Miszczak, A.; Gancarz, M.; Strachecka, A. Antioxidation Defenses of Apis mellifera Queens and Workers Respond to Imidacloprid in Different Age-Dependent Ways: Old Queens Are Resistant, Foragers Are Not. Animals 2021, 11, 1246. [Google Scholar] [CrossRef] [PubMed]
Figure 1. Number of worker brood cells (±standard deviation) of heat-treated honeybee queens (nH-TQ) and thermally manipulated honeybee queens in their immature stages (pH-TQ) in two consecutive years, 2021 and 2022.
Figure 1. Number of worker brood cells (±standard deviation) of heat-treated honeybee queens (nH-TQ) and thermally manipulated honeybee queens in their immature stages (pH-TQ) in two consecutive years, 2021 and 2022.
Insects 16 00858 g001
Figure 2. Number of honeybee workers (±standard deviation) of non-heat-treated honeybee queens (nH-TQ) and thermally manipulated honeybee queens in their immature stages (pH-TQ) in two consecutive years: 2021 and 2022.
Figure 2. Number of honeybee workers (±standard deviation) of non-heat-treated honeybee queens (nH-TQ) and thermally manipulated honeybee queens in their immature stages (pH-TQ) in two consecutive years: 2021 and 2022.
Insects 16 00858 g002
Figure 3. Drone brood cell numbers (±standard deviation) of non-heat-treated honeybee queens (nH-TQ) and thermally manipulated honeybee queens in their immature stages (pH-TQ) in two consecutive years: 2021 and 2022.
Figure 3. Drone brood cell numbers (±standard deviation) of non-heat-treated honeybee queens (nH-TQ) and thermally manipulated honeybee queens in their immature stages (pH-TQ) in two consecutive years: 2021 and 2022.
Insects 16 00858 g003
Figure 4. Number of swarm cell constructions (±standard deviation) of non-heat-treated honeybee queens (nH-TQ) and thermally manipulated honeybee queens in their immature stages (pH-TQ) (n = 12 colonies for both groups) in two consecutive years: 2021 and 2022.
Figure 4. Number of swarm cell constructions (±standard deviation) of non-heat-treated honeybee queens (nH-TQ) and thermally manipulated honeybee queens in their immature stages (pH-TQ) (n = 12 colonies for both groups) in two consecutive years: 2021 and 2022.
Insects 16 00858 g004
Figure 5. Percentage (%) of pollen loaded workers per hour (±standard deviation) of non-heat-treated honeybee queens (nH-TQ) and thermally manipulated honeybee queens in their immature stages (pH-TQ) in two consecutive years: 2021 and 2022.
Figure 5. Percentage (%) of pollen loaded workers per hour (±standard deviation) of non-heat-treated honeybee queens (nH-TQ) and thermally manipulated honeybee queens in their immature stages (pH-TQ) in two consecutive years: 2021 and 2022.
Insects 16 00858 g005
Figure 6. Number of stored pollen cells (±standard deviation) by non-heat-treated honeybee queens (nH-TQ) and thermally manipulated honeybee queens in their immature stages (pH-TQ) (n = 12 colonies for both groups) in two consecutive years: 2021 and 2022.
Figure 6. Number of stored pollen cells (±standard deviation) by non-heat-treated honeybee queens (nH-TQ) and thermally manipulated honeybee queens in their immature stages (pH-TQ) (n = 12 colonies for both groups) in two consecutive years: 2021 and 2022.
Insects 16 00858 g006
Figure 7. Percentage of returning workers collecting pollen (±standard deviation) in non-heat-treated honeybee queens (nH-TQ) and thermally manipulated honeybee queens in their immature stages (pH-TQ) in two consecutive years: 2021 and 2022.
Figure 7. Percentage of returning workers collecting pollen (±standard deviation) in non-heat-treated honeybee queens (nH-TQ) and thermally manipulated honeybee queens in their immature stages (pH-TQ) in two consecutive years: 2021 and 2022.
Insects 16 00858 g007
Figure 8. Average weight of 10 pollen loads in milligrams (mg) (±standard deviation) carried by workers of non-heat-treated honeybee queens (nH-TQ) and thermally manipulated honeybee queens in their immature stages (pH-TQ) in two consecutive years: 2021 and 2022.
Figure 8. Average weight of 10 pollen loads in milligrams (mg) (±standard deviation) carried by workers of non-heat-treated honeybee queens (nH-TQ) and thermally manipulated honeybee queens in their immature stages (pH-TQ) in two consecutive years: 2021 and 2022.
Insects 16 00858 g008
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Al-Ghzawi, A.A.-M.; Zaitoun, S.T.; Al-Sabi, M.N.S.; Mazari, S.S.; Al-Omari, I.M.; Altalhi, M.S. Assessing the Productivity of Colonies Headed by Preheated Honeybee Queens. Insects 2025, 16, 858. https://doi.org/10.3390/insects16080858

AMA Style

Al-Ghzawi AA-M, Zaitoun ST, Al-Sabi MNS, Mazari SS, Al-Omari IM, Altalhi MS. Assessing the Productivity of Colonies Headed by Preheated Honeybee Queens. Insects. 2025; 16(8):858. https://doi.org/10.3390/insects16080858

Chicago/Turabian Style

Al-Ghzawi, Abd Al-Majeed, Shahera Talat Zaitoun, Mohammad Nafi Solaiman Al-Sabi, Salem Saleh Mazari, Ilham Mustafa Al-Omari, and Maqbool Saed Altalhi. 2025. "Assessing the Productivity of Colonies Headed by Preheated Honeybee Queens" Insects 16, no. 8: 858. https://doi.org/10.3390/insects16080858

APA Style

Al-Ghzawi, A. A.-M., Zaitoun, S. T., Al-Sabi, M. N. S., Mazari, S. S., Al-Omari, I. M., & Altalhi, M. S. (2025). Assessing the Productivity of Colonies Headed by Preheated Honeybee Queens. Insects, 16(8), 858. https://doi.org/10.3390/insects16080858

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop