- Research article
- Open Access
Predatory beetles feed more pest beetles at rising temperature
BMC Ecology volume 16, Article number: 21 (2016)
Climate warming is a challenge for many plants and animals as they have to respond to rising temperature. Rising temperature was observed to affect herbivores and predators. Activity-density of abundant predatory carabid beetles, which are considered important natural control agents of agricultural pests, was observed to increase at rising temperature. The pollen beetle Meligethes aeneus is one of the most important insect pests in European oilseed rape fields, and its larvae were observed to be important prey to carabid beetles. Therefore, we performed a laboratory experiment to detect whether rising temperature affects the number of pollen beetle larvae killed by five abundant carabids, and larval biomass ingested by carabids. In three climate chambers actual temperature (T1) was compared to temperatures increased by 3 °C (T2) and 5 °C (T3). This is the first study investigating the feeding of carabid predators on an arable pest insect spanning a realistic forecasted climate warming scenario of 3 and 5 °C, thus providing basic knowledge on that neglected research area. We hypothesized that carabids kill more pollen beetle larvae at rising temperature, and biomass intake by carabids increases with rising temperature.
Both beetle species and temperature had significant effects on the number of killed Meligethes larvae and larval biomass ingested by carabids. Amara ovata, Harpalus distinguendus and Poecilus cupreus killed significantly more pollen beetle larvae at T2 and T3 compared to T1. Anchomenus dorsalis killed significantly more larvae at T2 than T1, and Harpalus affinis showed no significant differences among temperatures. Biomass intake by A. ovata, H. distinguendus and A. dorsalis was significantly larger at T2 and T3 compared to T1. Biomass intake by H. affinis and P. cupreus did not significantly differ among temperatures. Among the five carabids tested P. cupreus exhibited the highest values for both number of killed larvae and biomass intake.
Our lab results suggest a clear potential for higher feeding of pollen beetle larvae by carabid beetles at rising temperature. As rising temperature leads to increased activity of abundant arable carabids in the field, it may be expected that there is enhanced pest suppression under warmer field conditions.
Despite controversy on whether increased concentrations of atmospheric greenhouse gas lead to rising global temperature , there is an increase in annual-mean global temperature of 0.78 °C since the beginning of the 20th century . Irrespective of contradictory opinions there will be regions with elevated temperature and the present study, which covers scenarios with elevated temperatures, is designed for regions that undergo temperature increases, e.g. Austria .
Where climate warming takes place it is a challenge for many plants and animals as they have to respond to rising temperature . Rising temperature was observed to affect herbivores [5, 6] and predators . In particular Meligethes viridescens, an economically important pest beetle of oilseed rape, was modelled to increase in abundance at rising temperature , and activity-density of abundant predatory carabid beetles was observed to increase in an artificially warmed wheat field . Carabid beetles fed more slugs and seeds at higher temperature [7, 10]. Overall, temperature was observed to be the key climatic variable increasing carabid catches by pitfall traps . This means that activity-density of carabid beetles increases at rising temperature, which enhances encounter probability between carabids and epigeic pest individuals, which in turn may increase the beneficial impact of carabid beetles under warmer field conditions.
Many carabid beetles are polyphagous predators. They are commonly found in arable crops and considered important natural control agents of agricultural pests [12–16]. The carabid beetles Anchomenus dorsalis and Poecilus cupreus were observed to reduce populations of oilseed rape insect pests emerging within winter rape fields, when studied in field exclosure experiments . Moreover, larval abundance of the major oilseed rape insect pests, Meligethes aeneus and Ceutorhynchus napi, was crucial in explaining the condition and density of the carabids Amara similata and P. cupreus under field conditions , which indicates that these pest insects are an important prey to carabid beetles. Oilseed rape is one of the most commonly used crops in Europe and its importance as a source for industrial and nutritional oil has been increasing worldwide during the last decades . The pollen beetle M. aeneus is one of the most important insect pests in European oilseed rape fields [20, 21]. Damage caused by pollen beetles usually results in podless peduncles. The present laboratory study focuses on pest-predator interactions involving larval pollen beetles and five medium to medium-large carabid beetles abundantly found in Central European arable crops in spring, thus being potential major antagonists of oilseed rape pests. Because pollen beetles pupate in the soil they are potentially susceptible to epigeic carabids in the larval developmental stage or as pupae.
The specific aims of the present study were to determine whether rising temperature affects (1) the number of M. aeneus larvae killed by carabids, and (2) M. aeneus larval biomass ingested by carabids. Even though feeding of predatory carabid beetles upon pest insects has generally been explored under laboratory conditions , published works including different temperature regimes span a large range of temperatures of more than 15 °C. The present study is to our knowledge the first one investigating the feeding of carabid predators on an arable pest insect spanning a realistic forecasted climate warming scenario of 3 and 5 °C. We hypothesized that (1) carabids kill more M. aeneus larvae at rising temperature, and (2) biomass intake by carabids increases with rising temperature.
Carabid and pollen beetle sampling
The experiment was performed with the spring breeding carabid beetles Amara ovata (Fabricius), Anchomenus dorsalis (Ponttopidan), Harpalus affinis (Schrank), H. distinguendus (Duftschmid) and Poecilus cupreus (Linnaeus), and the nitidulid pollen beetle Meligethes aeneus (Fabricius). Adult carabid beetles and larval pollen beetles were collected in an oilseed rape field in Raasdorf Lower Austria (16°59´E, 48°23´N), East of Vienna. Beetle sampling and field access were orally arranged with the owner of the field. For carabid sampling 120 pitfall traps (plastic cups, diameter 70 mm, depth 70 mm) were installed on 6 May and emptied on 9, 14 and 17 May 2013. Carabid beetles were brought to the laboratory, kept in 18 × 13 × 4.5 cm plastic boxes at 10 °C and fed with fish food (trademark "Tetra“©) prior to the experiment. On 1, 9, 14 and 21 May 2013 flowering inflorescences of oilseed rape plants were brought to the laboratory and pollen beetle larvae were picked out of the flowers. Prior to the experiment pollen beetle larvae were kept in 20 × 8 × 8 cm plastic boxes at 10 °C and fed with rape pollen.
The experiment was conducted in late May to June 2013 in three climate chambers at three different temperature regimes for each chamber. The basis for the temperatures used in the present work were the mean temperatures in April and May 1961–1990 for the region where beetles were collected (data provided by the Central Institution for Meteorology and Geodynamics Austria, ZAMG). Mean basis temperature (T1) was 11.5 °C, which was continuously increased by 5 °C during the day and continuously decreased by 5 °C during the night, i.e. T1 ranged from 6.5 °C at night to 16.5 °C during the day time, with the mean temperature of 11.5 °C. Mean temperatures of temperature 2 (T2) and temperature 3 (T3) were increased by 3 °C (T2) and 5 °C (T3) with the appropriate continuous alterations of 5 °C during day and night. T2 ranged from 9.5 °C at night to 19.5 °C during the day time, with the mean temperature of 14.5 °C, and T3 ranged from 11.5 °C at night to 21.5 °C during the day time, with the mean temperature of 16.5 °C.
In all three chambers a photoperiod of 14 h light and 10 h dark was used imitating light conditions for that time when pollen beetle larvae occur in the field. The used scenarios of future rising temperatures of 3 and 5 °C are in the range of climate models for Eastern Austria that compare the period 1961–1990 with 2071–2100 .
Before the experiment was started carabids were divided into sexes and only females were used for the experiment because for some species we did not collect enough males. Prior to the experiment female beetles were weighed assuring that weight of carabid beetle species tested did not differ significantly among temperature regimes (A. ovata, T1 35.90 ± 1.27, T2 38.70 ± 0.50, T3: 39.20 ± 1.57, N = 18, P = 0.145; A. dorsalis, T1 13.97 ± 0.49, T2 14.66 ± 0.49, T3 15.58 ± 0.91, N = 30, P = 0.243; H. affinis, T1 66.01 ± 2.66, T2 62.76 ± 2.29, T3 64.68 ± 2.05, N = 36, P = 0.256; H. distinguendus, T1 57.63 ± 3.15, T2 61.40 ± 3.07, T3 60.77 ± 2.66, N = 36, P = 0.805; P. cupreus, T1 99.83 ± 4.72, T2 91.58 ± 3.60, T3 96.02 ± 3.31, N = 36, P = 0.309; mean weight ± SE in mg, ANOVA). Twelve replicates per temperature regime were used, summing up to 36 Petri dishes for H. affinis, H. distinguendus and P. cupreus. Six replicates per temperature regime were used for A. ovata, and ten for A. dorsalis, depending on carabid availability. Female beetles were placed individually in Petri dishes (diameter 60 mm, height 15 mm) and starved for 48 h. To keep humidity in the Petri dishes stable at 100 %, each dish was covered with a 50 mm diameter paper towel which was irrigated with 1 mL water. To prevent the towels from desiccation they were irrigated daily. After 48 h of carabid starvation pollen beetle larvae, which served as food for the carabids, were counted and weighed. Thereafter, they were put in the Petri dishes where they stayed for 72 h. After 72 h, the number of non-killed pollen beetle larvae was counted and the whole remaining larval biomass was weighed enabling to measure both number of killed larvae and biomass intake by carabids over 72 h. For three carabid species ad libitum food availability during 72 h was guaranteed by initially feeding 30 pollen beetle larvae (A. dorsalis) or 40 pollen beetle larvae (A. ovata, H. distinguendus), respectively. These numbers of prey items were based on feeding tests that have been performed for each carabid species in advance under the same conditions as the experiment. Also, H. affinis were offered 40 pollen beetle larvae per Petri dish. As two individuals fed more than expected, ten additional pollen beetle larvae were offered to these two individuals after 48 h. Referring to pre-feeding tests with P. cupreus, 60 pollen beetle larvae were offered per Petri dish. However, as nine individuals fed more than expected additional pollen beetle larvae were offered to them after 48 h (six times ten additional larvae, and once 15, 20 and 30 larvae, respectively), providing ad libitum food availability during 72 h.
Effects of temperature (three temperature regimes) and beetle species (five carabid species) on the number of killed pollen beetle larvae and biomass intake by carabids were analysed with generalized linear models (GLM). The model for killed larvae was analyzed using Poisson distribution. Kruskal–Wallis tests were calculated for killed larvae for single carabid species to test for differences between temperatures, followed by the Nemenyi post hoc test for multiple comparisons. One-way ANOVAs were calculated for biomass intake for single carabid species to test for differences between temperatures, followed by the Tukey post hoc test for multiple comparisons. We checked the data for normality using the Kolmogorov–Smirnov test and diagnostic graphs, and for homogeneity of variances using the Levene test, and found them adequate, thus analyses were performed with untransformed data. As the carabid beetles used vary in size and body mass, we additionally calculated the number of killed pollen beetle larvae mg−1 and intake of larval pollen beetle biomass mg−1 among the five carabid species for all three temperatures together. As these data were not normally distributed one-way ANOVAs followed by the Tukey post hoc test were calculated with box-cox transformed data. Analyses were run with SPSS 21.0 (SPSS Inc., Chicago, IL, USA), and level of significance was defined at P < 0.05.
The factors beetle species and temperature had significant effects on the dependent variables number of killed Meligethes larvae and larval biomass ingested by carabids. The interaction term was significant for number of killed Meligethes larvae but not for biomass intake (Table 1). Because in the GLM both factors beetle species and temperature were significant, for each single species one-way ANOVAs were performed testing for differences among temperatures relative to the dependent variables. A. ovata, H. distinguendus and P. cupreus killed significantly more Meligethes larvae at temperatures 2 (T2) and 3 (T3) compared to temperature 1 (T1). A. dorsalis killed significantly more larvae at T2 than T1, and H. affinis revealed no significant differences among temperatures (Fig. 1). Biomass intake by A. ovata, H. distinguendus and A. dorsalis was significantly larger at T2 and T3 compared to T1, thus showing similar patterns as for killed larvae concerning the first two species. Biomass intake by H. affinis and P. cupreus did not significantly differ among temperatures (Fig. 2). Among the five carabids tested P. cupreus exhibited the highest values for both number of killed larvae and biomass intake. By considering the varying body mass of the five carabid beetles, we observed concurrent patterns for the number of killed pollen beetle larvae mg−1 and intake of larval pollen beetle biomass mg−1. A. dorsalis killed significantly more larvae mg−1 than the other four species, and the same was also true for biomass intake mg−1. Killing rate mg−1 and biomass intake mg−1 by A. ovata and P. cupreus were significantly larger compared to H. affinis and H. distinguendus (Table 2).
Four of five carabid species investigated killed more Meligethes larvae at rising temperature, and three species ingested more Meligethes biomass at higher temperature, thus largely confirming our hypotheses. Thus pollen beetle larvae, being on the way to pupate in the soil, may be killed more by epigeic carabids at higher temperature. This finding sounds promising for biological pest control in regions where climate warming is to be expected.
Our results agree with studies observing that feeding activity and biomass intake by slug feeding carabid beetles increase with rising temperature . Activity of spring breeding carabids, which were tested in the present study, is described to generally increase at higher temperature [24, 25]. This helps to explain the higher killing rate and biomass intake in the present study due to increased energy requirements at T2 and T3, as temperature has long been known to influence metabolism . The metabolic theory of ecology states that higher temperatures lead to higher metabolic rates in ectotherms and this results in higher consumption and digestion. T2 and T3 did never differ significantly. Thus, a further temperature increase (T2 > T3) did not affect carabids additionally. According to existing literature it may be expected that number of killed pollen beetle larvae and biomass intake should significantly increase from T2 to T3. When testing temperatures from 10–28 °C, there was a carabid species whose consumption on seeds increased linearly with increasing temperature, but consumption increase for another carabid was curvilinear and stopped at 20 °C . Such temperature limits might help to explain why a further temperature increase in the present work did not affect carabids additionally.
As A. dorsalis and H. distinguendus, two of the species that killed more Meligethes larvae and ingested more biomass at elevated temperature, are reported as thermophilous [27–30] they appear to be well adapted to higher temperatures. Similarly A. ovata, though reported to feed primarily on seeds , is obviously also insectivorous as it was observed to kill significantly more larvae and ingest more biomass at T2 and T3. Therefore, from the viewpoint of biological control this species was positively affected by increased temperature. P. cupreus killed significantly more Meligethes larvae at T2 and T3, and killed much more larvae than the other four species. The highest killing rate is simply because it was the heaviest species tested, which renders it a particularly promising biocontrol agent of Meligethes larvae. This argument is substantiated because P. cupreus is often observed to be the carabid species with the highest acitvity-density in Central European arable fields . We often observed P. cupreus to kill many Meligethes larvae without consuming them under our experimental conditions. This may explain why there was no significant difference in biomass intake among the three temperature regimes. Thus, P. cupreus did not transfer its increased killing rate at higher temperatures into an increased ingestion of prey biomass. The killing of prey without consuming it, known as "superfluous killing“ or "wasteful killing“, has already been observed for P. cupreus when offered different insect prey in the laboratory . H. affinis was the only species whose killing rate and biomass intake remained unaffected by temperature. It preferably occurs in dry and sunny open habitats [34–36], which may explain its tolerance towards the different temperature regimes investigated.
There was a negative relationship between predation rates of aphids and the community-average value of body size of ground-dwelling spiders and carabids in cereal fields . Laboratory daily consumption of aphids by predatory beetles considering the predator´s body weight was lowest for large carabids and highest for small staphylinids . Consistently, number of killed pollen beetle larvae and intake of larval pollen beetle biomass related to 1 mg body weight of predators were higher for lightweight carabids compared to heavy ones for four out of five species (body weight: A. dorsalis < A. ovata < H. distinguendus < H. affinis). For H. affinis, the heaviest of these four beetles, pollen beetle larvae appeared to be a non-attractive prey, which may explain why both the total killing rate and total biomass intake were not affected by increasing temperature. Killing rate and total biomass intake by P. cupreus were remarkably high in relation to its body weight. This may be because P. cupreus was observed to be particularly active in the Petri dishes, which likely resulted in increased energy requirements.
Climate simulation models suggest several Central European arable pest insects to increase in number of generations per year [39, 40]. Moreover, Meligethes viridescens, which has recently been introduced to Canada, was modelled to increase in abundance for temperature increases between 1 and 7 °C , thus covering the temperature increase range of the present study. As climate warming may also be favourable to M. aeneus potential consequences of our lab experiment for field population development of M. aeneus are not clear so far. Nonetheless our lab results suggest a clear potential for higher feeding of pollen beetle larvae by carabid beetles at rising temperature. As activity-density of carabid beetles in wheat was found to significantly increase when temperature was artificially raised by only 2 °C , it can be expected that carabids encounter more pest individuals at soil surface, which in turn most likely increases pest suppression under warmer field conditions. Laboratory studies revealing that carabid beetles feed more at rising temperature span a large range of temperatures of more than 15 °C [7, 10]. The present study is to our knowledge the first one on pest consumption spanning a realistic forecasted climate warming scenario of 3 and 5 °C, thus providing basic knowledge on that neglected research topic.
generalized linear model
temperature increased by 3 °C
temperature increased by 5 °C
Central Institution for Meteorology and Geodynamics Austria
Kosaka Y, Xie SP. Recent global-warming hiatus tied to equatorial pacific surface cooling. Nature. 2013;501:403–7.
Becker P, Jacob D, Deutschländer T, Imbery F, Namyslo J, Müller-Westermeier G, Roos M. Klimawandel in Deutschland. In: Brasseur G, Mosbrugger V, Schaller M, Stibrny B, editors. Klimawandel und Biodiversitäts-Folgen für Deutschland. Darmstadt: Wissenschaftliche Buchgesellschaft; 2014. p. 23–37.
Kromp-Kolb H, Nakicenovic N, Steininger K, Gobiet A, Formayer H, Köppl A, et al. Austrian Panel on Climate Change (APCC). Austrian Assessment Report 2014 (AAR14). 2014. http://hw.oeaw.ac.at/APPC_AAR2014.pdf. Accessed 8 Oct 2014.
Grimm N, Chapin S, Bierwagen B, Gonzalez P, Groffman PM, Luo Y, et al. The impacts of climate change on ecosystem structure and function. Front Ecol Environ. 2013;11:474–82.
Bale JS, Masters GJ, Hodkinson ID, Awmack C, Bezemer TM, Brown VK, et al. Herbivory in global climate change research: direct effects of rising temperature on insect herbivores. Glob Change Biol. 2002;8:1–16.
Sassi C, Tylianakis JM. Climate change disproportionately increases herbivore over plant or parasitoid biomass. PLoS One. 2012;7:e40557.
Saska P, Martinkova Z, Honek A. Temperature and rate of seed consumption by ground beetles (Carabidae). Biol Control. 2010;52:91–5.
Olfert O, Weiss RM. Impact of climate change on potential distributions and relative abundances of Oulema melanopus, Meligethes viridescens and Ceutorhynchus obstrictus in Canada. Agric Ecosys Environ. 2006;113:295–301.
Berthe SCF, Derocles SAP, Lunt DH, Kimball BA, Evans DM. Simulated climate-warming increases Coleoptera activity-densities and reduces community diversity in a cereal crop. Agric Ecosys Environ. 2015;210:11–4.
Ayre K. Effect of predator size and temperature on the predation of Deroceras reticulatum (Mollusca) by carabid beetles. J Appl Entomol. 2001;125:389–95.
Saska P, van der Werf W, Hemerik L, Luff ML, Hatten TD, Honek A. Temperature effects on pitfall catches of epigeal arthropods: a model and method for bias correction. J Appl Ecol. 2013;50:181–9.
Warner DJ, Allen-Williams LJ, Ferguson AW, Williams IH. Pest-predator spatial relationships in winter rape: implications for integrated crop management. Pest Manag Sc. 2000;56:977–82.
Thomas CFG, Parkinson L, Griffiths GJK, Garcia AF, Marshall EJP. Aggregation and temporal stability of carabid beetle distributions in field and hedgerow habitats. J Appl Ecol. 2001;38:100–16.
Symondson WOC, Glen DM, Ives AR, Langdon CJ, Wiltshire CW. Dynamics of the relationship between a generalist predator and slugs over five years. Ecology. 2002;83:137–47.
Holland JM, Thomas CFG, Birkett T, Southway S, Oaten H. Farm-scale spatiotemporal dynamics of predatory beetles in arable crops. J Appl Ecol. 2005;42:1140–52.
Bommarco R, Firle SO, Ekbom B. Outbreak supression by predators depends on spatial distribution of prey. Ecol Model. 2007;201:163–70.
Zaller JG, Moser D, Drapela T, Frank T. Ground-dwelling predators can affect within-field pest insect emergence in winter oilseed rape fields. BioControl 2009;54:247–53.
Haschek C, Drapela T, Schuller N, Fiedler K, Frank T. Carabid beetle condition, reproduction and density in winter oilseed rape affected by field and landscape parameters. J Appl Entomol. 2012;136:665–74.
FAOSTAT. Food and Agricultural Organization of the United Nations. 2014. http://faostat.fao.org. Accessed 3 Dec 2014.
Zaller JG, Moser D, Drapela T, Schmöger C, Frank T. Effect of within-field and landscape factors on insect damage in winter oilseed rape. Agric Ecosys Environ. 2008;123:233–8.
Williams IH. Biocontrol-based integrated management of oilseed rape pests. Dordrecht: Springer; 2010.
Renkema JM, Manning P, Cutler GC. Predation of lowbush blueberry insect pests by ground beetles (Coleoptera: Carabidae) in the laboratory. J Pest Sci. 2013;86:525–32.
Formayer H, Haas P, Kromp-Kolb H, Hofstätter M, Radanovics S. Räumlich und zeitlich hochaufgelöste Temperaturszenarien für Wien und ausgewählte Analysen bezüglich Adaptionsstrategien. Universität für Bodenkultur, Bericht im Auftrag der Wiener Umweltschutzabteilung MA 22 der Stadt Wien; 2007.
Honek A. The effect of temperature on the activity of Carabidae (Coleoptera) in a fallow field. Eur J Entomol. 1997;94:97–104.
Tuf IH, Dedek P, Veselý M. Does the diurnal activity pattern of carabid beetles depend on season, ground temperature and habitat? Arch Biol Sci. 2012;64:721–32.
Price CA, Weitz JS, Savage VM, Stegen J, Clarke A, Coomes DA, et al. Testing the metabolic theory of ecology. Ecol Lett. 2012;15:1465–74.
Cooper K, Kenneth W. Carabid beetles in their environments A study on habitat selection by adaptations in physiology and behaviour. Q Rev Biol. 1979;54:93–4.
Glück E, Deuschle J. Habitat- und Feuchtepräferenz von Laufkäfern (Coleoptera, Carabidae) in Streuobstwiesen. Bonner Zool Beiträge. 2002;51:51–69.
Haselböck A. 2014. Harpalus distinguendus. 2014. http://www.naturspaziergang.de/Kaefer/Carabidae/Harpalus_distinguendus.htm. Accessed 1 May 2014.
Taboada A, Kotze DJ, Salgado JM, Tárrega R. The influence of habitat type on the distribution of carabid beetles in traditionally managed “dehesa” ecosystems in NW Spain. Entomol Fenn. 2006;17:284–95.
Jørgensen HB, Toft S. Role of granivory and insectivory in the life cycle of the carabid beetle Amara similata. Ecol Entomol. 1997;22:7–15.
Anjum-Zubair M, Entling MH, Bruckner A, Drapela T, Frank T. Differentiation of spring carabid beetle assemblages between semi-natural habitats and adjoining winter wheat. Agric Forest Entomol. 2015;17:355–65.
Lang A, Gsodl S. Superfluous killing of aphids: a potentially beneficial behaviour of the predator Poecilus cupreus (L.) (Coleoptera: Carabidae)? J Plant Dis Prot. 2003;100:583–90.
Heckendorf C, Ruprecht A, Schneider K. Zur Faunenstruktur (Coleoptera-Carabidae) in Wald-Brachland-Habitaten des NSG “Lintbusch”. Hercynia NF. 1986;23:72–82.
Theves F. Laufkäfer (Col., Carabidae) in Feldhecken Südwestdeutschlands. Vergesellschaftung und Biodiversität in Abhängigkeit von der Habitatqualität. Universität Hohenheim; 2013.
Thiele HU. Carabid beetles in their environments. 10th ed. Berlin: Springer; 1977.
Rusch A, Birkhofer K, Bommarco R, Smith HG, Ekbom B. Predator body sizes and habitat preferences predict predation rates in an agroecosystem. Bas Appl Ecol. 2015;16:250–9.
Sopp P, Wratten SD. Rates of consumption of cereal aphids by some polyphagous predators in the laboratory. Entomol Exp Appl. 1986;41:69–73.
Kocmankova E, Trnka M, Eitzinger J, Dubrovsky M, Stepanek P, Semeradova D, et al. Estimating the impact of climate change on the occurrence of selected pests at a high spatial resolution: a novel approach. J Agric Sci. 2011;149:185–95.
Svobodova E, Trnka M, Dubrovsky M, Semeradova D, Eitzinger J, Stepanek P. Determination of areas with the most significant shift in persistence of pests in Europe under climate change. Pest Manag Sci. 2014;70:708–15.
TF designed the experiment, wrote the majority of the manuscript with contributions of MB and made some statistical analyses. MB collected beetles, performed laboratory work and made most statistical analyses. Both authors read and approved the final manuscript.
We are grateful to Norbert Schuller for assistance with collecting beetles and for help in the laboratory.
Availabilitiy of data and materials
Our data are provided in the electronic supplementary material (Additional file 1).
The authors declare that they have no competing interests.
Consent to publish
Carabid beetles used and pollen beetles are not regulated invertebrates. At the end of the experiments carabid beetles were released to the field they have been collected.
No funding was obtained for this study.
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Frank, T., Bramböck, M. Predatory beetles feed more pest beetles at rising temperature. BMC Ecol 16, 21 (2016). https://doi.org/10.1186/s12898-016-0076-x
- Biological pest control
- Biomass intake
- Carabid beetles
- Climate warming
- Feeding activity
- Killing rate
- Meligethes aeneus
- Pollen beetle
- Predator-pest interaction
- Temperature increase