Advertisement
Browse Subject Areas
?

Click through the PLOS taxonomy to find articles in your field.

For more information about PLOS Subject Areas, click here.

  • Loading metrics

A Protocol to Assess Insect Resistance to Heat Waves, Applied to Bumblebees (Bombus Latreille, 1802)

  • Baptiste Martinet ,

    Baptiste.martinet@student.umons.ac.be

    Affiliation University of Mons, Research Institute of Biosciences, Laboratory of Zoology, Place du Parc 20, 7000, Mons, Belgium

  • Thomas Lecocq,

    Affiliation University of Mons, Research Institute of Biosciences, Laboratory of Zoology, Place du Parc 20, 7000, Mons, Belgium

  • Jérémy Smet,

    Affiliation University of Mons, Research Institute of Biosciences, Laboratory of Zoology, Place du Parc 20, 7000, Mons, Belgium

  • Pierre Rasmont

    Affiliation University of Mons, Research Institute of Biosciences, Laboratory of Zoology, Place du Parc 20, 7000, Mons, Belgium

A Protocol to Assess Insect Resistance to Heat Waves, Applied to Bumblebees (Bombus Latreille, 1802)

  • Baptiste Martinet, 
  • Thomas Lecocq, 
  • Jérémy Smet, 
  • Pierre Rasmont
PLOS
x

Abstract

Insect decline results from numerous interacting factors including climate change. One of the major phenomena related to climate change is the increase of the frequency of extreme events such as heat waves. Since heat waves are suspected to dramatically increase insect mortality, there is an urgent need to assess their potential impact. Here, we determined and compared the resistance to heat waves of insects under hyperthermic stress through their time before heat stupor (THS) when they are exposed to an extreme temperature (40°C). For this, we used a new experimental standardised device available in the field or in locations close to the field collecting sites. We applied this approach on different Arctic, Boreo-Alpine and Widespread bumblebee species in order to predict consequences of heat waves. Our results show a heat resistance gradient: the heat stress resistance of species with a centred arctic distribution is weaker than the heat resistance of the Boreo-Alpine species with a larger distribution which is itself lower than the heat stress resistance of the ubiquitous species.

Introduction

The current worldwide biodiversity undergoes one of the greatest mass species extinction in earth’s history [1]. The biodiversity decline results from numerous interacting factors including destruction and fragmentation of habitat, urban development, invasive species, pest plants/animals, pesticide use, and climate change. Among these factors, the climate change has been pointed out as one of the major causes of extinction in several groups of organisms [24].

The climate change encompasses modifications in mean temperature and precipitation throughout the year as well as changes in variability among years. Indeed, the current climate change is related to an increase of frequency of extreme event such as heat waves [5,6]. These heat waves have been linked to physiological perturbation (e.g. levels of HSP proteins, fecundity) [7] leading to increased mortality among several species as birds [8,9], flies [10], flying-foxes [11], weevils [12], butterflies [13] or bees [14,15]. Nevertheless, it remains difficult to predict heat wave consequences on species because each taxon has its own specific thermotolerance [12]. This places a premium on accurate determination of thermotholerance of each target species.

Here, we determine and compare the heat stress resistance under hyperthermic stress of small insects with a new experimental standardised device available in the field or in laboratory close to the field collecting sites. We apply this approach on different bumblebee species in order to predict consequences of heat waves.

Materials and Methods

Estimation of Heat stress resistance

Classically, methods to measure heat resistance have been borrowed from Uvarov [16] and Hutchison [17]. For instance, these methods were used to calculate the critical temperature to kill insects and other pathogen agents in foodstuff [16]. Here, we used a new static method [1820] with a portable experimental device. Insects were exposed here to constant conditions: 40°C with constant humidity. The heat stress resistance of specimens has been estimated through their Time before Heat Stupor (THS).

Test case

Bumblebees (Hymenoptera, Apidae, genus Bombus) are robust and hairy heterothermic bees with the ability of strong endothermy [21] that enables them to recolonize areas depopulated by glaciation events [22,23] and to live in some of the highest-elevation and most northern ecosystems. Their species diversity hotspots (mountains, Arctic, Subarctic and Boreal regions) are also regions hardest hit by climate change [2427].

We sampled 144 males belonging to five different species from Eastern Pyrenees and North of Scandinavia (S1 Dataset): two taxa with an arctic distribution: (B.alpinus [n = 16], B.balteatus [n = 22], both belonging to Alpinobombus subgenus, [28]); three Boreo-Alpine (mountainous) taxa (B.(Pyrobombus) monticola scandinavicus [n = 15], B.monticola rondoui [n = 30], B.(Psithyrus) flavidus [n = 31]) and one widespread and ubiquitous species (B. (Bombus sensu stricto) lucorum [n = 30]) (S1 Dataset). Permissions for collection of Swedish samples were obtained via the Länsstyrelsen Norrbotten. No specific permits were required for the other described studies as collection did not occur in privately-owned, protected locations or protected species. The bioassay of this study does not require ethic permit as it applies to insects.

We used only males as they display simple and constant behaviour and they normally do not take shelter in thermoregulated underground nests as the females could do [21].

Experimental device and protocol

We collected specimens in the field (S1 Dataset) and placed them in a fridge (WAECO CDF-35, 31L with a 12 V vehicle power supply) to keep them at 8°C (standby temperature according to Heinrich (1975, 1979) [21,29] in dark with food (i.e. BioGluc available ad libitum, Biobest NV, Westerlo, Belgium) during one day. After 24 hours, insects were placed individually in breakthrough Petri dishes.

The Petri dishes with specimens were placed in the incubator (Herp Nursery II) at 40°C (Fig. 1). This incubator is a portable device where the temperature and humidity were controlled. This device can be used in the field when it is plugged into a 12 V vehicle power supply or other 12 V portable battery. The heating device includes a system of semiconductor thermoelectric Peltier elements (60 W) in an isolated oven of 25 dm3 (27cm x 23cm x 37cm) [30]. The incubator’s fan homogenises the temperature. The humidity of the enclosure is stabilised by free water disposed in the insert at the bottom of the incubator. A psychrometer (Lufft C210) and a datalogger (Voltcraft DL-181 THP USB Ambient Monitoring Data Logger) used to check the humidity. The resulting relative humidity of 50–60% corresponds to a normal rate in daytime (in summer) in the wild [31,32].

thumbnail
Fig 1. Picture of the experimental device.

Picture of the experimental device: A) Incubator Herp Nursery II with its 12 V vehicle power supply, the datalogger (Voltcraft DL-181 THP USB Ambient Monitoring Data Logger), the psychrometer (Lufft C210), the digital thermometer (Zoo Med) and the thermostat (Lucky Reptil ThermoControl Pro II) B) Fridge WAECO CDF to keep bumblebees at 8°C with 12 V vehicle power supply, C) Scale Ace CT-50, D) Petri Dishes with tested bumblebees.

https://doi.org/10.1371/journal.pone.0118591.g001

In order to improve the low accuracy of the air temperature regulation controller embedded in the Herp Nursery II, we added to the device a datalogger and a thermostat (Lucky Reptil ThermoControl Pro II, accuracy ± 0.1°C), including a thermometer, ables to stop and start the Peltier system of the incubator. We also included a digital thermometer (Zoo Med, accuracy ± 0.1°C) to check the stability of the air temperature inside the incubator. The temperature of 40°C was chosen in reference to the hottest temperature observed in 2011 in France [33]. Besides, even for the North of Fennoscandia this choice remains meaningful. Indeed, high air temperature can be measured even in Arctic, e.g. (an air temperature of 34°C has been recorded in Kevo in June 2013, [34]). With this experimental device the temperature remained constant [18]. In the wild, living male bumblebees make their courtship in sunlit open area [35] and they could actually experience harsher heat stress situations.

The individuals placed in the enclosure have been observed and monitored through the window in the door.

Measure of Heat stress resistance

An insect is said to be entering into "dazed heat" or "heat stupor" [16,36] when it falls on its back, is unable to turn, and loses its normal reflexes [37]. The extremities are them shaken by muscle spasms [38] that appear just before death [16,18]. We distinguished the following sequence of activity: (i) normal activity (ii) important excitation, (iii) heat stupor, and (iv) death. The Time before Heat Stupor (THS) is measured for each individual tested with a chronometer (±1 minute). This was the time from insertion into the incubator to heat stupor.

Each Petri dish was flipped over at regular intervals (1–2 minutes) to check if the specimen was able to flip from up-down to normal position. The temperature loss caused by the opening of the door of the incubator is negligible and was estimated (with a datalogger) at less than 0.5°C. When the specimen became no more able to return in normal position, they have been assumed to be in “heat stupor”. The THS values have been recorded. Once in heat stupor; the insect was removed from the enclosure to recover. The percentage of mortality after experiment has been recorded. The dry weight of each species has been measured with a scale (Ace CT-50 Portable Miligram Scale, precision ± 0.001g) after lyophilisation (Lyovac GT2 LEYBOLD-HERAEUS in the laboratory of Zoology of the University of Mons (Belgium)

Statistical analyses

From the results, Kruskal-Wallis analyses (Kruskal-Wallis test and Multiple comparison test after Kruskal-Wallis, “pgirmess” R-package, [39]) were performed to compare the different species altogether and boxplots were carried out using R (R Development Core Team, 2013) (“graphics” R-package, [40], “stats” R-package, [41]) to detect heat stress resistance differentiations between each species and between the two subspecies of B. monticola ssp. (B. monticola rondoui and B. monticola scandinavicus).

Results

Our bioassays results in the death of 49.7% of individuals, while others recover feeding and flying again. Indeed the death percentage is about 50% in all species except B. lucorum (26%) (Table 1).

thumbnail
Table 1. Values of Time before heat stupor (THS), percentage of males bumblebees survivors (Survivors %) and median dry weight for five bumblebees species (Bombus).

https://doi.org/10.1371/journal.pone.0118591.t001

thumbnail
Fig 2. Boxplots of the time before heat stupor.

Boxplots of the time before heat stupor (THS) for five bumblebee species: Arctic centred species (A): Bombus alpinus and Bombus balteatus; Boreo-Alpine species (B): Bombus flavidus and Bombus monticola; Widespread species (C): Bombus lucorum. Circles = extreme values.

https://doi.org/10.1371/journal.pone.0118591.g002

The Kruskal Wallis test confirms that there are significant differences between species (KW chi2 = 92.78, P < 0.05). Pairwise statistical analysis (Multiple comparison after Kruskal-Wallis test) show that centred arctic species (Alpinobombus) are characterised by a very low similar heat stress resistance (P > 0.05, Table 2) while Boreo-Alpine species (B. monticola and B. flavidus) have a higher heat resistance (P < 0.05, Table 2) than Arctic species but a weaker heat resistance than a widespread and ubiquitous species as B. lucorum (P < 0.05, Table 2).

thumbnail
Table 2. Values of the Multiple comparison after Kruskal-Wallis test (Diff means difference) to compare the heat stress resistance (Time before heat stupor) of different bumblebee species (Bombus).

https://doi.org/10.1371/journal.pone.0118591.t002

Discussion

Test case

The percentage of mortality (Table 1) of male bumblebees suggests that 40°C resembles the approximate lethal temperature 50% (LT50) [16] at least in Arctic centred and Boreo-Alpine bumblebees. However to determine the exact LT50, special experiments are required where the animals are exposed to a set of different temperature with equal exposure times and post-treatment observation intervals for all individuals. Further studies are needed to determine this LT50 for bumblebee species.

Our results show that the heavyweight Arctic species B. alpinus and B. balteatus (Table 1) display a low heat stress resistance (Fig. 2). In contrast, Bombus monticola, a lightweight species (Table 1) with a large boreo-alpine distribution, has a higher heat stress resistance (Table 1, Fig. 2). This observation could reflect the Bergmann’s rule [42,43]. According to this rule, species of warm countries are smaller and have a higher ratio surface/volume than species of cold countries. Thus, according to this rule, Arctic species should be large with a low heat stress resistance. However, this rule is valid for endothermic organisms and it is often questioned for ectothermic or optional endothermic organisms. So, we cannot draw conclusions too hasty concerning if the heat stress resistance could be deduced from size. Further physiological and ecological studies are necessary to validate the Bergmann's rule for bumblebees or to highlight other factor as ambient temperature which appears to be a more important factor.

The similar heat stress resistance between B. alpinus and B. balteatus could result from their closely phylogenetic relationship [44] or from their identical eco-climatic constraints. Bombus flavidus, which is likely the cuckoo species of B. monticola [45,46], does not have a significantly different heat stress resistance compared to its host. For B. monticola, our sampling allows taking into consideration two distinct allopatric populations from different eco-climatic regions (B. monticola rondoui from Pyrenees and B. monticola scandinavicus from Scandinavia). Our results show that there is no difference in heat stress resistance between these allopatric populations (Table 2). This suggests that the heat stress resistance could be similar between allopatric conspecific populations from different eco-climatic areas. Further pieces of evidence in other species are required to assess the intraspecific variation of heat stress resistance.

Our results strongly suggest that heatwaves could quickly lead to fatal consequences for bumblebee species, e.g. Alpinobombus as it has been suggested by Rasmont & Iserbyt [47]. Therefore, the relative importance of heatwaves in the bumblebee decline should be taken into account in future studies on the trigger factor of worldwide bumblebee regression.

Limits of experiment

Heat resistance could be influenced by many natural factors that can not be controlled in this experimental device [48]: (i) all analysed species have a different phenology and thus it could have been that old males are less resistant than young males. However, according to Terblanche et al. [49], age has no influence on the critical temperature of insects. (ii) The uncontrolled health status of the tested specimen can also have an impact on its heat stress resistance. (iii) The duration of habituation (24 hours at 8°C) may influence the survival time [37,50] but in our comparative method, the experimental conditions are standardised thus the duration of habituation’s influence is negligible. (iv) Experiments were conducted at different times during the day, however, the daily cycles would have no influence on survival time [51]. (v) In this experimental device, flying insects do not have the ability to fly, which is normally the primary cause of increased thoracic temperature with the endothermy for brood incubation [21,29,52]. Thus, the present test conditions could be less stressful than some actual heatwaves. (vi) In the field, insects could adapt a behavior to reduce the effect of overheating such as taking refuge in a fresh place as under a rock or under a flower thereby abandoning their nuptial behavior. These two last parameters are very difficult to achieve in bioassays.

To conclude, this experimental device allows estimating easily the interspecific heat stress resistance of insects in the field or locations close to the field. That could be crucial in the context of the current climate changes. This protocol has the advantage of evaluating the heat resistance of insects almost directly without requiring a step of rearing or a sustained maintenance of specimens. This gives us the opportunity to significantly increase the number of replicates.

Supporting Information

S1 Dataset. Table sampling.

Table sampling with all tested specimens and their collection characteristics.

https://doi.org/10.1371/journal.pone.0118591.s001

(XLSX)

Acknowledgments

The authors sincerely thank the Abisko and Tarfala scientific stations (Sweden) and the municipality of Eyne (Pyrenees) for their welcome and their help for material collection. Thomas Lecocq is post-doc in the context of the BELBEES project funded by the Belgian Scientific Politic (BELSPO, BR/132/A1/BELBEES).

Author Contributions

Conceived and designed the experiments: BM TL JS PR. Performed the experiments: BM JS PR. Analyzed the data: BM TL PR. Contributed reagents/materials/analysis tools: BM PR. Wrote the paper: BM TL JS PR.

References

  1. 1. Novacek MJ, Cleland EE. The current biodiversity extinction event: scenarios for mitigation and recovery. Proc Natl Acad Sci U S A. 2001;98: 5466–5470. pmid:11344295
  2. 2. Parmesan C, Root TL, Willig MR. Impacts of extreme weather and climate on terrestrial biota. Bull Am Meteorol Soc. 2000;81: 443–450.
  3. 3. Parmesan C. Ecological and Evolutionary Responses to Recent Climate Change. Annu Rev Ecol Evol Syst. 2006;37: 637–669.
  4. 4. Winfree R. The conservation and restoration of wild bees. Ann N Y Acad Sci. 2010;1195: 169–197. pmid:20536823
  5. 5. Meehl GA, Tebaldi C. More intense, more frequent, and longer lasting heat waves in the 21st century. Science. 2004;305: 994–997. pmid:15310900
  6. 6. McKechnie AE, Wolf BO. Climate change increases the likelihood of catastrophic avian mortality events during extreme heat waves. Biol Lett. 2010;6: 253–256. pmid:19793742
  7. 7. Kingsolver JG, Diamond SE, Buckley LB. Heat stress and the fitness consequences of climate change for terrestrial ectotherms. Funct Ecol. 2013;27: 1415–1423.
  8. 8. Jiguet F, Julliard R, Thomas CD, Dehorter O, Newson SE, Couvet D. Thermal range predicts bird population resilience to extreme high temperatures. Ecol Lett. 2006;9 (12): 1321–1330. pmid:17118006
  9. 9. Albright TP, Pidgeon AM, Rittenhouse CD, Clayton MK, Flather CH, Culbert PD, et al. Heat waves measured with MODIS land surface temperature data predict changes in avian community structure. Remote Sens Environ. 2011;115: 245–254.
  10. 10. Nyamukondiwa C, Weldon CW, Chown SL, le Roux PC, Terblanche JS. Thermal biology, population fluctuations and implications of temperature extremes for the management of two globally significant insect pests. J Insect Physiol. 2013;59: 1199–1211. pmid:24080125
  11. 11. Welbergen JA, Klose SM, Markus N, Eby P. Climate change and the effects of temperature extremes on Australian flying-foxes. Proc Biol Sci. 2008;275: 419–425. pmid:18048286
  12. 12. Klok CJ, Chown SL. Resistance to temperature extremes in sub-Antarctic weevils: interspecific variation, population differentiation and acclimation. Biol J Linn Soc. 2003;78: 401–414.
  13. 13. Jaco Klok C, Chown SL. Critical thermal limits, temperature tolerance and water balance of a sub-Antarctic caterpillar, Pringleophaga marioni (Lepidoptera: Tineidae). J Insect Physiol. 1997;43: 685–694. pmid:12769980
  14. 14. Rasmont P, Iserbyt S. The Bumblebees Scarcity Syndrome: Are heat waves leading to local extinctions of bumblebees (Hymenoptera: Apidae: Bombus). Ann la Société Entomol Fr (n.s.). 2012;48: 275–280.
  15. 15. Franzén M, Molander M. How threatened are alpine environments? a cross taxonomic study. Biodivers Conserv. 2011;21: 517–526.
  16. 16. Uvarov BP. Insects and climate. Trans Entomol Soc London. 1931;79: 1–232.
  17. 17. Hutchison VH. The concept of critical thermal maximum. Am J Physiol. 1979;237 (5): 367–368.
  18. 18. Lutterschmidt WI, Hutchison VH. The critical thermal maximum: History and critique. Can J Zool. 1997;75: 1561–1574.
  19. 19. Brett JR. Some lethal temperature: relations of algonquin park fishes. Toronto: University of Toronto Press; 1944.
  20. 20. Fry FEJ. The lethal temperature as a tool in taxonomy. Année Biol. 1957;33: 205–219.
  21. 21. Heinrich B. Bumblebee economics. Cambridge, Massachussets: Harvard University Press; 1979
  22. 22. Hines HM. Historical biogeography, divergence times, and diversification patterns of bumble bees (Hymenoptera: Apidae: Bombus). Syst Biol. 2008;57: 58–75. pmid:18275002
  23. 23. Lecocq T, Dellicour S, Michez D, Lhomme P, Vanderplanck M, Valterová I, et al. Scent of a break-up: phylogeography and reproductive trait divergences in the red-tailed bumblebee (Bombus lapidarius). BMC Evol Biol. 2013;13: 263. pmid:24295171
  24. 24. Williams PH. Environmental change and the distributions of British bumble bees (Bombus Latr.). Bee World. 1986;67: 50–61.
  25. 25. Core Writing Team, Pachauri RK, Pachauri RA (IPCC). Contribution of Working Groups I, II and III to the Fourth Assessment Report of the Intergovernmental Panel on Climate Change. Geneva. 2007. Available: http://www.ipcc.ch/pdf/assessment-report/ar4/syr/ar4_syr_fr.pdf.
  26. 26. Franzén M, Öckinger E. Climate-driven changes in pollinator assemblages during the last 60 years in an Arctic mountain region in Northern Scandinavia. J Insect Conserv. 2011;16: 227–238.
  27. 27. Franzén M, Molander M. How threatened are alpine environments? a cross taxonomic study. Biodivers Conserv. 2011;21: 517–526.
  28. 28. Williams PH, Cameron SA, Hines HM, Cederberg B, Rasmont P. A simplified subgeneric classification of the bumblebees (genus Bombus). Apidologie. 2008;39: 46–74.
  29. 29. Heinrich B. Thermoregulation in bumblebees. J Comp Physiol B. 1975;96: 155–166.
  30. 30. Pottier N. Physique statique hors d’équilibre—Processus irréversibles linéaires. Ulis: EDP Sciences; 2007
  31. 31. Jacq F, Berne C, Pineaud A. Bulletin Climatique Juillet 2012. MeteoFrance.2012. Available: https://donneespubliques.meteofrance.fr/donnees_libres/bulletins/BCM/201207.pdf. Accessed 2014 Sep 5.
  32. 32. Infoclimat. Pourcentage d' Humidité relative. Available: http://www.infoclimat.fr/cartes/observations%20-meteo/temps-reel/humidite-relative/france.html. Accessed 2014 Sep 5.
  33. 33. Infoclimat. Températures maximales Available: http://www.infoclimat.fr/cartes/observations-meteo/archives/temperature-maximale-journaliere/1er/janvier/1881/00h/france.html. Accessed 2014 Sep 5.
  34. 34. Weatheronline Ltd. Climate Data Available: http://www.weatheronline.co.uk/Europe.htm. Accessed 2014 Sep 5.
  35. 35. Svensson BG, Bergström G. Marking pheromones ofAlpinobombus males. J Chem Ecol. 1979;5: 603–615.
  36. 36. Bodenheimer FS, Klein HZ. Über die Temperaturabhangigkeit von Insekten. ii. Die Abhängigkeit der Aktivität bei der Ernteameise Messor semirufus, E. André von Temperatur und anderen Faktoren. Z Vgl Physiol. 1930;11: 345–385.
  37. 37. Huang S-P, Hsu Y, Tu M-C. Thermal tolerance and altitudinal distribution of two Sphenomorphus lizards in Taiwan. J Therm Biol. 2006;31: 378–385.
  38. 38. Martínez-Porchas M, Hernández-Rodríguez M. Critical thermal maxima and minima of Sardinops sagax caeruleus Girard 1854 and the analyses of behavioral responses to establish adequate endpoints. Trop Zool. 2010;23: 139–146.
  39. 39. Siegel S, Castellan NJ. Non parametric statistics for the behavioural sciences. New York: MacGraw Hill Humanities; 1988.
  40. 40. Murrell P. Computer Science and Data Analysis Series: R Graphics. London: Chapman & Hall/CRC Press; 2005.
  41. 41. R Development Core Team. R: a language and environment for statistical computing. R Foundation for Statistical Computing, Vienna, Austria. ISBN 3-900051-07-0; 2011.
  42. 42. Bergmann C. Ueber die Verhältnisse der Wärmeökonomie der Thiere zu ihrer Grösse. Gottinger Stud. 1847;3: 595–708.
  43. 43. Muller P. Aspects of Zoogeography. The Hague: W. Junk; 1974
  44. 44. Cameron SA, Hines HM, Williams PH. A comprehensive phylogeny of the bumble bees (Bombus). Biol J Linn Soc. 2007;91: 161–188.
  45. 45. Rasmont P. Monographie écologique et zoogéographique des Bourdons de France et de Belgique (Hymenoptera, Apidae, Bombinae). PhD.Sc.Thesis Gembloux: Faculté des Sciences agronomiques de l'Etat. 1988. Available: http://www.zoologie.umh.ac.be/hymenoptera/biblio/Rasmont_1988_PhD_compact.pdf.
  46. 46. Rasmont P, Iserbyt S. Tertiary Atlas of the European bees: genus Bombus. STEP Project. Status Trends Eur. Pollinators. 06 Sep 2014. Available: http://www.atlashymenoptera.net. Accessed 12014 Sep 5.
  47. 47. Rasmont P, Iserbyt S. The Bumblebees Scarcity Syndrome: Are heat waves leading to local extinctions of bumblebees (Hymenoptera: Apidae: Bombus). Ann la Soc Entomol Fr. 2012;48: 275–280.
  48. 48. Hutchison VH. Factors influencing thermal tolerances of individual organisms. Proc Therm Ecol. 1976;8: 10–26.
  49. 49. Terblanche JS, Deere JA, Clusella-Trullas S, Janion C, Chown SL. Critical thermal limits depend on methodological context. Proc Biol Sci. 2007;274: 2935–2942. pmid:17878142
  50. 50. Morritt D, Ingólfsson A. Upper thermal tolerances of the beachflea Orchestia gammarellus (Pallas) (Crustacea: Amphipoda: Talitridae) associated with hot springs in Iceland. J Exp Mar Bio Ecol. 2000;255: 215–227. pmid:11108853
  51. 51. Ribeiro PL, Camacho A, Navas CA. Considerations for assessing maximum critical temperatures in small ectothermic animals: insights from leaf-cutting ants. PLoS One. 2012;7: e32083. pmid:22384147
  52. 52. Heinrich B. Energetics of temperature regulation and foraging in a bumblebee,Bombus terricola kirby. J Comp Physiol. 1972;77: 49–64.