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Cockchafer
Cockchafer
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Common cockchafer
Female
Scientific classification Edit this classification
Kingdom: Animalia
Phylum: Arthropoda
Class: Insecta
Order: Coleoptera
Suborder: Polyphaga
Infraorder: Scarabaeiformia
Family: Scarabaeidae
Genus: Melolontha
Species:
M. melolontha
Binomial name
Melolontha melolontha
Linnaeus, 1758

The common cockchafer (Melolontha melolontha), also colloquially known as the Maybug,[1][a] Maybeetle,[3] or doodlebug,[4] is a species of scarab beetle belonging to the genus Melolontha. It is native to Europe, and it is one of several closely-related and morphologically similar species of Melolontha called cockchafers, alongside Melolontha hippocastani (the forest cockchafer).

The cockchafer develops via metamorphosis, in which the beetle undergoes stages of eggs, larvae, pupae and adults.

The mating behaviour is controlled by pheromones. The males usually swarm during the mating season while the females stay put and feed on leaves.[5] The leaves release green leaf volatiles when they are fed on by females, which the male can sense and thus locate the female for mating opportunity.[6][7] The larvae use both the plant volatiles and CO2 to locate the plant root for food.[8]

This species is an important and nutritious food source for many species. The adults and larvae feed on plants, and are regarded as agricultural pests of crops such as grasses and fruit trees. Adults have harmful effects for the crop when they aggregate in large groups. The larvae can cause severe damage and kill the plant by gnawing the plant roots.[9]

Distribution

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Cockchafers are prevalent across Europe, including in Germany, France, and the United Kingdom. They are particularly prevalent in temperate regions with suitable soil conditions for larval development. However, they have also been reported in parts of Asia, including Turkey and the Caucasus region. Geographical barriers, climatic conditions, and ecological factors may limit their dispersal to other continents.[10]

Description

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Adults

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Close up of a male cockchafer, showing the seven "leaves" on the antennae

Adults of M. melolontha reach sizes of 25 to 30 millimetres (1 to 1+14 inches) in length.[5] Behind their heads they have a black pronotum covered with short hairs. This black coloration distinguishes them from their close relative M. hippocastani, whose pronotum is brown. The top of their bodies have hard, brown elytra and a black thorax, while their underside is black and partly white on the sides. They have a dark head with two antennae with ten segments each. Male cockchafers have seven "leaves" on their antennae, whereas the females have only six.[5]

Larvae

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Larvae have 3 stages of development over the course of 3–4 years. In the first stage, they are 10–20 mm long, then grow to 30–35 mm in the second year of development, and finally reach their full size of 40–46 mm in their final year of development before emerging.[5] In some areas of Eastern Europe the larvae develop for a fourth year. They have white bodies that curve into an arc with a black coloration at the abdomen and long, hairy, and well developed legs.[5] They have large orange heads with strong, grabbing mandibles. On their heads they have 2 small antennae which they use to smell and taste their surroundings while underground.[8]

Food resources

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Cockchafer feeds on deciduous plant and fruit tree leaves, including oaks, maple, sweet chestnut, beech, plum, and walnut trees. The feeding behaviour of larvae can cause severe damage to the plants. They feed on both the small roots of field plants such as grain, grass, tree, beet roots and the large part of crop rootlets. Larvae can gnaw the root for 30 cm each day, which quickly kills the plant.[9]

Life cycle

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Female M. melolontha Beetle.

Adults appear at the end of April or in May and live for about five to seven weeks. After about two weeks, the female begins laying eggs, which she buries about 10 to 20 cm deep in the earth. She may do this several times until she has laid between 60 and 80 eggs. Most typically, the female beetle lays its eggs in fields. The preferred food for adults is oak leaves, but they will also feed on conifer needles.

The larvae, known as "chafer grubs" or "white grubs", hatch four to six weeks after being laid as eggs. They feed on plant roots, for instance potato roots. The grubs develop in the earth for three to four years, in colder climates even five years, and grow continually to a size of about 4–5 cm, before they pupate in early autumn and develop into an adult cockchafer in six weeks.[5]

The cockchafer overwinters in the earth at depths between 20 and 100 cm. They work their way to the surface only in spring.

Because of their long development time as larvae, cockchafers appear in a cycle of every three or four years; the years vary from region to region. There is a larger cycle of around 30 years superimposed, in which they occur (or rather, used to occur) in unusually high numbers (10,000s).

Enemies

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Predators

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The European mole is a natural predator of cockchafers. Moles are known to feed on cockchafer larvae. They can detect them using their keen sense of smell and specialised digging behaviour. This predation can help regulate cockchafer populations in mole-inhabited areas. [11]

M. melolontha adults are predated by ground beetles and ants. Larvae are predated by click beetles while underground. Starlings, crows, and gulls also predate M. melolontha larvae, often after a field has been plowed.[5]

Parasites

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Dexia rustica is a parasitic fly that uses M. melolontha larvae as their hosts. D. rustica eggs hatch underground and look for cockchafer larvae to hibernate within over the winter. Their presence will ultimately kill the beetle larvae in the spring. One to six fly larva can parasitise a single host.[5]

Behaviour

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Mating behaviour

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Male M. melolontha Beetle.

Males leave the soil when the temperature is favourable in April or May. Sexual dimorphism is observed as male beetles, at dusk, will begin to swarm and locate around groups of trees at forest edges.[5] On the other hand, females will stay in place and feed on leaves until they reach sexual maturity. Males primarily fly around the branches looking for females to mate with.[6][7] This behaviour occurs for several hours until darkness for about 10-20 days.[5] These swarms typically have minimal damage to the trees, but they are occasionally harmful in cherry or plum orchards because of their consumption of blossoms. Once the females have matured and mated, they return to the fields to lay their eggs in the soil. Only a third of females will survive this trip, but any survivors will make a second, and occasionally third, swarming trip and return to the field to lay eggs again.[5]

Green leaf volatiles (GLVs) are a series of saturated and monounsaturated six-carbon aldehydes, alcohols, and esters released by vascular plants in response to stresses.[12] GLVs have been found to act as a kairomone, which is a compound released by an organism that only benefits the receiver.[6][7] This enhances the attractiveness of toluquinone, a sex pheromone in scarab beetles. Only male M. melolontha are attracted to GLVs, using its release to identify leaves that female beetles are feeding on. Females have the ability to detect GLV, but any change in behaviour that it may cause is unclear.[6][7] M. melolontha males are more sensitive to lower GLV concentrations, possibly due to the anatomical differences between male and female antennae.[7] Due to this phenomenon, sexual dimorphism can be observed in flight behaviour. During swarming behaviour, males will hover around the foliage while females remain on twigs and branches to feed. Males then use GLVs to identify which leaves have females that they can mate with.[7] GLVs are being investigated as a possible pest control technique to attract males and prevent mating.[5]

Pest behaviour

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Though adults can damage some fruit trees, M. melolontha larvae are the primary agricultural pests.[5] Larva hatch from their eggs 4–6 weeks after being laid and develop into adults over the course of 3–4 years. Immediately after hatching, larvae will gnaw on small roots. It will continue feeding on roots, particularly grasses, cereals, and other crops, during its three larval stages, only pausing to burrow deep into the soil for winter hibernation.[5]

In their first stage, M. melolontha larvae identify roots by CO2 release. They will only do damage at extreme densities.[5] In their second stage, larva will cause the most damage to crops.[8] In their third stage, larva will do less but still severe damage to crops. They most prominently use structures on their antennae called pore plates to smell. This structure is a thin layer of cells that covers a number of sensory units consisting of dendrite bundles. These and other olfactory organs on the head of the larva can identify CO2 and plant volatiles. They've also been found to push their heads into the walls of their burrows and probe with their antennae, likely to taste the soil with bristle-like sensilla.[8]

Pest control and history

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Larva (grub)

Middle Ages

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In the Middle Ages, pest control was rare, and people had no effective means to protect their harvest. This gave rise to events that seem bizarre from a modern perspective. In 1320, for instance, cockchafers were brought to court in Avignon and sentenced to withdraw within three days onto a specially designated area, otherwise they would be outlawed. Subsequently, since they failed to comply, they were collected and killed. Similar animal trials also occurred for many other animals in the Middle Ages.[13]

19th century

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Both the grubs and adults have a voracious appetite and thus have been and sometimes continue to be a major problem in agriculture and forestry. In the pre-industrialised era, the main mechanism to control their numbers was to collect and kill the adult beetles, thereby interrupting the cycle. They were once very abundant: in 1911, more than 20 million individuals were collected in 18 km2 of forest.[1] Collecting adults was an only moderately successful method.

In some areas and times, cockchafers were served as food. A 19th-century recipe from France for cockchafer soup reads: "roast one pound of cockchafers without wings and legs in sizzling butter, then cook them in a chicken soup, add some veal liver and serve with chives on a toast". A German newspaper from Fulda from the 1920s tells of students eating sugar-coated cockchafers. Cockchafer larvae can also be fried or cooked over open flames, although they require some preparation by soaking in vinegar in order to purge them of soil in their digestive tracts.[14] A cockchafer stew is referred to in W. G. Sebald's novel The Emigrants.

In Sweden the peasants looked upon the grub of the cockchafer as furnishing an unfailing prognostic whether the ensuing winter will be mild or severe; if the animal has a bluish hue (a circumstance which arises from its being replete with food), they affirm it will be mild, but if it is white, the weather will be severe: and they carry this so far as to foretell, that if the anterior be white and the posterior blue, the cold will be most severe at the beginning of the winter. Hence they call this grub Bemärkelse-mask—prognostic worm.[15]

Modern times

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Only with the modernisation of agriculture in the 20th century and the invention of chemical pesticides did it become possible to effectively combat the cockchafer. Combined with the transformation of many pastures into agricultural land, this has resulted in a decrease of the cockchafer to near-extinction in some areas in Europe in the 1970s.

Since the 1970s, agriculture has generally reduced its use of pesticides. Because of environmental and public health concerns (pesticides may enter the food chain and thus also the human body) many chemical pesticides have been phased out in the European Union and worldwide. In recent years, the cockchafer's numbers have been increasing again, causing damage to agricultural use of over 1,000 square kilometres (400 sq mi) of land all over Europe (0.001% of land).

Due to legal provisions from the European Union for the sustainable use of pesticides, aerial treatment, which had been used to successfully control M. melolontha populations, is now banned.[16] Light traps have been successful in attracting M. melolontha adults, particularly males, when put at height (4 m). If a peak swarming time can be identified, shaking isolated trees and collecting feeding adults can reduce population, though it is time consuming.[16] Azadirachtin is a chemical that inhibits maturation feeding and egg development, but low persistence and difficulty spraying it high enough in trees prevents widespread use.[16] Soil tilling has been a historically successful method, particularly in early June when larvae are first hatching.[17] Pre-cropping is also a promising possibility, with buckwheat being of particular interest because it can reduce grub weight and population density before the crop of interest is planted.[16] Sex pheromones have been used for mass trapping, mating disruption, and "Attract and Kill" methods. The unlikelihood of developing resistance due to the sex pheromones being produced by the beetles makes this a promising method of pest control.[5]

Entomopathogens

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Entomopathogenic organisms—organisms that produce disease in insects—are an active area of research for the control of M. melolontha grub populations.[18] Entomopathogenic fungi is currently being studied as a way to control M. melolontha grub populations. Beauveria brongniartii has been found to work on the Melolontha species, and B. bassiana has been successful with other agricultural pests. There have been difficulties with determining the best strategy to apply the fungi to the fields.[18] Entomopathogenic nematodes have been found to be particularly successful ways of reducing populations, particularly when larvae are in the first and second stage.[17] entomopathogenic bacteria from the genera Steinernema and Heterorhabditis are also being investigated, but they have been difficult to apply to fields as opposed to laboratory settings.[19] The focus on entomopathogenic bacteria has been on their symbiosis with entomopathogenic nematodes and their ability to act together as a larval control strategy.[17] Poor results with the application of these methods have stemmed intensive research into the gut enzymes and microbiome of M. melolontha to determine if they are acting as defense against entomopathogenic organisms.[19]

Intestinal components and microbiome

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The gut enzymes and microbiota of M. melolontha larvae allow them to exploit a variety of ecological niches unique to their phylogenetic family. These are low energy foods such as grass roots and rotting organic matter in the soil.[20] There are two major compartments in the scarabaeid larvae intestinal tract. The first is a tubular midgut that secretes hydrolytic enzymes for macromolecule breakdown, and the second is a bulbous hindgut used for fermentation. High bacterial diversity between individuals of M. melolontha in the intestinal tract reflects the diversity of food sources.[21]

In the midgut, glucose is broken down and absorbed by the epithelium. It has been shown that proteolytic breakdown of toxins is a common resistance mechanism for agricultural pests.[19] Proteolytic activity of enzymes in the midgut is hypothesised to increase resistance to entomopathogenic bacteria in the beetle larvae. Trypsin-like enzymes from the midgut of M. melolontha have been found to break down certain bacterial toxins and inactivate them.[19]

The hindgut has a high density of bacteria that ferment recalcitrant residues such as cellulose, with the byproducts being absorbed by the beetle.[21] Acetate is a major product of this fermentation, suggesting that much of the bacteria in the hindgut is homoacetogenic. High abundance of species in the bacterial genus Desulfovibrio in the hindgut suggests that sulphate reduction is an important process, but the source of this sulphate in the diet is unknown.[21]

Some research on the M. melolontha microbiome has been focused on increasing the entomopathogenic properties of nematodes used as pest control due to their symbiosis.[20] Bacteria such as Xenorhabdus nematophila are transported by nematodes and released into the insect's midgut. The bacteria will release lytic enzymes and other antimicrobial substances to decrease competition from the beetle's native microbiome. This creates an optimal environment for nematode development. Bacterial species in the midgut of M. melolontha such as Pseudomonas chlororaphis have been found to fight back, acting as antagonists to entomopathogenic bacteria. These bacteria have been identified differentially in different larval stages, with P. chlororaphis usually being found in the third and final larval stage.[20]

Ecological impact

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Environmental factors such as temperature, humidity, and plant type have a considerable impact on the existence and behaviour of cockchafers in wooded environments. It indicates that cockchafer populations are strongly influenced by climatic conditions, with warmer temperatures and higher humidity level favouring their occurrence. Additionally, specific vegetation types, including deciduous trees and shrubs, provide suitable habitats for cockchafers, facilitating their survival and reproduction within forest stands.[11]

Etymology

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The name "cockchafer"[22] derives from the late-17th-century usage of "cock"[23] (in the sense of expressing size or vigour) + "chafer"[24] which simply means an insect of this type, referring to its propensity for gnawing and damaging plants. The term "chafer" has its root in Old English ceafor or cefer, of Germanic origin and is related to the Dutch kever, all of which mean "gnawer" as it relates to the jaw. As such, the name "cockchafer" can be understood to mean "large plant-gnawing beetle" and is applicable to its history as a pest animal.

In culture

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Children since antiquity have played with cockchafers. In ancient Greece, boys caught the insect, tied a linen thread to its feet and set it free, amusing themselves to watch it fly in spirals. English boys in Victorian times played a very similar game by sticking a pin through one of its wings.[25] Nikola Tesla recalls that as a child he made one of his first "inventions", an "engine" made by harnessing four cockchafers in this fashion.[26]

Cockchafers appear in the fairy tales "Thumbelina" by Hans Christian Andersen and "Princess Rosette" by Madame d'Aulnoy.

Max and Moritz shaking cockchafers from a tree

The cockchafer is featured in a German children's song similar to the English Ladybird, Ladybird:

Maikäfer, flieg!
Der Vater ist im Krieg,
die Mutter ist in Pommerland,
Pommerland ist abgebrannt –
Maikäfer flieg!

Cockchafer, fly!
Father is at war,
Mother is in Pomerania,
Pomerania is burned to the ground –
Cockchafer, fly!

The verse dates back to the Thirty Years' War in the first half of the 17th century, in which Pomerania was pillaged and suffered heavily. Since World War II, it is associated in Germany with the closing months of that war as well, when Soviet troops advanced into eastern Germany.

According to one source, the dumbledore in Thomas Hardy's 1899 poem An August Midnight[27] is a cockchafer.[28] However, in his novel The Mayor of Casterbridge, Hardy uses the dialect word dumbledore to mean a bumble bee.[29]

A group of cockchafers in Ukraine

There have been four Royal Navy ships named HMS Cockchafer.

See also

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Explanatory notes

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Citations

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  1. ^ a b c "Common Cockchafer". Bug Life.
  2. ^ Marren, Peter; Mabey, Richard (2010). Bugs Britannica. Chatto & Windus. ISBN 978-0-7011-8180-2.
  3. ^ "Cockchafer | insect". Encyclopedia Britannica. Retrieved 2021-07-01.
  4. ^ "7 things you never knew about the cockchafer". Discover Wildlife. 8 April 2014. Retrieved 4 July 2016.
  5. ^ a b c d e f g h i j k l m n o p Huiting, H. F., Moraal, L. G., Griepink, F. C., & Ester, A. (2006), Biology, control and luring of the cockchafer, Melolontha melolontha: literature report on biology, life cycle and pest incidence, current control possibilities and pheromones, Praktijkonderzoek Plant & Omgeving{{citation}}: CS1 maint: multiple names: authors list (link)
  6. ^ a b c d Reinecke, Andreas; Ruther, Joachim; Tolasch, Till; Francke, Wittko; Hilker, Monika (2002-06-01). "Alcoholism in cockchafers: orientation of male Melolontha melolontha towards green leaf alcohols". Naturwissenschaften. 89 (6): 265–269. Bibcode:2002NW.....89..265R. doi:10.1007/s00114-002-0314-2. ISSN 0028-1042. PMID 12146792. S2CID 25772038.
  7. ^ a b c d e f Reinecke, Andreas; Ruther, Joachim; Hilker, Monika (April 2005). "Electrophysiological and behavioural responses of Melolontha melolontha to saturated and unsaturated aliphatic alcohols". Entomologia Experimentalis et Applicata. 115 (1): 33–40. Bibcode:2005EEApp.115...33R. doi:10.1111/j.1570-7458.2005.00274.x. ISSN 0013-8703. S2CID 84471627.
  8. ^ a b c d Eilers, Elisabeth J.; Talarico, Giovanni; Hansson, Bill S.; Hilker, Monika; Reinecke, Andreas (2012-07-25). "Sensing the Underground – Ultrastructure and Function of Sensory Organs in Root-Feeding Melolontha melolontha (Coleoptera: Scarabaeinae) Larvae". PLOS ONE. 7 (7) e41357. Bibcode:2012PLoSO...741357E. doi:10.1371/journal.pone.0041357. ISSN 1932-6203. PMC 3405142. PMID 22848471.
  9. ^ a b Fraval, A. (1998). "HYPP Zoology".
  10. ^ "Melolontha melolontha (Linnaeus, 1758)". www.gbif.org. Retrieved 2024-03-21.
  11. ^ a b Marzena, Niemczyk (June 2017). "Effect of environmental factors on occurrence of cockchafers (Melolontha spp.) in forest stands".
  12. ^ Matsui, Kenji; Engelberth, Jurgen (2022-10-31). "Green Leaf Volatiles—The Forefront of Plant Responses Against Biotic Attack". Plant and Cell Physiology. 63 (10): 1378–1390. doi:10.1093/pcp/pcac117. ISSN 0032-0781. PMID 35934892.
  13. ^ Barton, K.: Verfluchte Kreaturen: Lichtenbergs "Proben seltsamen Aberglaubens" und die Logik der Hexen- und Insektenverfolgung im "Malleus Maleficarum", in Joost, U.; Neumann, A. (eds): Lichtenberg-Jahrbuch 2004, p. 11ff, Saarbrücken 2004 (SDV Saarländische Druckerei und Verlag), ISBN 3-930843-87-0. In German.
  14. ^ Cooking cockchafer with old-timey Europeans 11 February 2016 www.bugsfeed.com accessed 30 May 2021
  15. ^ De Geer, iv. 275–6. Kirb. and Sp. Introd., i. 33.
  16. ^ a b c d Malusá, Eligio; Tartanus, Małgorzata; Furmanczyk, Ewa M.; Łabanowska, Barbara H. (2020-12-01). "Holistic approach to control Melolontha spp. in organic strawberry plantations". Organic Agriculture. 10 (1): 13–22. Bibcode:2020OrgAg..10S..13M. doi:10.1007/s13165-020-00295-2. ISSN 1879-4246.
  17. ^ a b c Woreta, Danuta (2015-03-01). "Control of cockchafer Melolontha spp. grubs – a review of methods". Folia Forestalia Polonica. 57 (1): 33–41. doi:10.1515/ffp-2015-0005. ISSN 2199-5907.
  18. ^ a b Tartanus, Malgorzata; Furmanczyk, Ewa M.; Canfora, Loredana; Pinzari, Flavia; Tkaczuk, Cezary; Majchrowska-Safaryan, Anna; Malusá, Eligio (February 2021). "Biocontrol of Melolontha spp. Grubs in Organic Strawberry Plantations by Entomopathogenic Fungi as Affected by Environmental and Metabolic Factors and the Interaction with Soil Microbial Biodiversity". Insects. 12 (2): 127. doi:10.3390/insects12020127. ISSN 2075-4450. PMC 7912822. PMID 33540558.
  19. ^ a b c d Wagner, Wolfgang; Möhrlen, Frank; Schnetter, Wolfgang (July 2002). "Characterization of the proteolytic enzymes in the midgut of the European Cockchafer, Melolontha melolontha (Coleoptera: Scarabaeidae)". Insect Biochemistry and Molecular Biology. 32 (7): 803–814. doi:10.1016/S0965-1748(01)00167-9. PMID 12044497.
  20. ^ a b c Skowronek, Marcin; Sajnaga, Ewa; Pleszczyńska, Małgorzata; Kazimierczak, Waldemar; Lis, Magdalena; Wiater, Adrian (2020-01-16). "Bacteria from the Midgut of Common Cockchafer (Melolontha melolontha L.) Larvae Exhibiting Antagonistic Activity Against Bacterial Symbionts of Entomopathogenic Nematodes: Isolation and Molecular Identification". International Journal of Molecular Sciences. 21 (2): 580. doi:10.3390/ijms21020580. ISSN 1422-0067. PMC 7013910. PMID 31963214.
  21. ^ a b c Egert, Markus; Stingl, Ulrich; Dyhrberg Bruun, Lars; Pommerenke, Bianca; Brune, Andreas; Friedrich, Michael W. (August 2005). "Structure and Topology of Microbial Communities in the Major Gut Compartments of Melolontha melolontha Larvae (Coleoptera: Scarabaeidae)". Applied and Environmental Microbiology. 71 (8): 4556–4566. Bibcode:2005ApEnM..71.4556E. doi:10.1128/AEM.71.8.4556-4566.2005. ISSN 0099-2240. PMC 1183286. PMID 16085849.
  22. ^ cockchafer (n.) www.etymonline.com accessed 30 May 2021
  23. ^ cock (n.1) www.etymonline.com accessed 30 May 2021
  24. ^ chafer (n.) www.etymonline.com accessed 30 May 2021
  25. ^ Martin, William (1866). "Peter Parley's annual: A Christmas and New Year's present for young people". Retrieved 2017-05-27.
  26. ^ Tesla, Nikola (1919). "My Inventions". Electrical Experimenter. Retrieved 2023-03-29.--
  27. ^ Collected poems of Thomas Hardy, 1923, p154
  28. ^ Brown, Joanna Cullen, Review of Thomas Hardy: Cent Poèmes. Anthologie bilingue (Les Editions de L'Aire, Vevey, 2008) by Eric Christen, Françoise Baud, The Hardy Society Journal, Vol. 4, No. 3 (Autumn 2008), pp. 87
  29. ^ Cook, John D. (22 September 2011). "Thomas Hardy and Harry Potter". www.johndcook.com. Retrieved 30 May 2024.
[edit]
Revisions and contributorsEdit on WikipediaRead on Wikipedia
from Grokipedia
The cockchafer (Melolontha melolontha), also known as the May bug, is a large scarab beetle species (Scarabaeidae family) endemic to Europe, distinguished by its adult form's clumsy, nocturnal swarming flights and its C-shaped larvae that feed voraciously on plant roots in soil. Adults typically span 20–30 mm in length, with a reddish-brown exoskeleton, clubbed antennae adapted for pheromone detection, and a brief lifespan of about six weeks dedicated primarily to reproduction after emerging in late spring. The life cycle spans three to four years, dominated by larval development underground where grubs damage turf, crops, and forest undergrowth by consuming organic matter and roots, often synchronizing population cycles that amplify periodic outbreaks as agricultural pests. These outbreaks have historically prompted interventions like soil treatments and biological controls targeting larvae, underscoring the beetle's ecological role in nutrient cycling alongside its economic impacts on grassland and arable farming.

Taxonomy and Systematics

Principal Species and Variants

The genus , within the family , encompasses around 20 species of commonly referred to as cockchafers, though the term principally denotes the European species Melolontha melolontha (common cockchafer) and Melolontha hippocastani (forest cockchafer). These two represent the primary species of economic and ecological significance in due to their larval root-feeding habits that can damage forests and . M. melolontha is characterized by a body length of 20-30 mm, light brown coloration, and a slender pygidium, distinguishing it from M. hippocastani, which has a shorter, knob-shaped pygidium. M. melolontha, described by Linnaeus in 1758, is the archetypal cockchafer, widespread across temperate where it emerges in May and June, feeding on tree foliage as adults. Its larvae, known as white grubs, develop over 3-4 years in , consuming and roots. In contrast, M. hippocastani, named by Fabricius in 1801, has a similar life cycle but prefers forest habitats and is noted for outbreaks damaging broadleaf trees. A third European species, Melolontha pectoralis, exists but is less commonly associated with the cockchafer designation and has restricted distribution. No subspecies are recognized for M. melolontha, with morphological variation limited to regional color and size differences attributable to environmental factors rather than . Recent taxonomic additions, such as Melolontha arunachalensis and Melolontha lachungensis described in 2023 from , expand the genus but do not alter the focus on European principals for cockchafer references.

Morphology

Adult Form

The adult cockchafer, Melolontha melolontha, measures 20-34 mm in length, exhibiting a robust, convex body with a heavy-set appearance. The head is dark, often black, and the pronotum is shiny black, covered in short, closely set hairs. The elytra are reddish-brown or dull brown, ribbed, and the abdomen is blackish dorsally. Legs are reddish, adapted for walking, while the antennae are lamellate, forming a fan-like structure with males possessing seven terminal segments (lamellae) and females six, aiding in pheromone detection during mating. Ventrally, the body features fine, short pubescence, denser on the sides and . The overall coloration and pubescence provide among foliage where adults aggregate.

Larval Form

The larvae of the cockchafer (Melolontha melolontha), commonly called grubs, exhibit a characteristic C-shaped posture typical of scarab beetle larvae. They possess a soft, creamy-white to dull white body, a hardened brown head capsule equipped with strong mandibles for root feeding, and three pairs of well-developed thoracic legs that are often yellowish and hairy. The body lacks prolegs, and the raster (anal plate) features two rows of short spines arranged in a V-pattern, aiding identification from similar species. Development proceeds through three instars over 3 to 4 years in the , with first-instar larvae hatching at approximately 5-6 mm in length after a 4- to 6-week stage. Subsequent molts occur in late summer or autumn, with second- and third-instar grubs growing progressively larger, reaching 40-45 mm by maturity; third instars dominate the damage phase due to their size and feeding intensity. Overwintering happens 2-3 times, with grubs burrowing deeper (up to 1 meter) in colder periods to avoid freezing, resuming activity in spring when temperatures rise above 10°C. Grubs primarily feed on decaying organic matter and live roots in the upper soil layers (0-20 cm initially, deeper later), targeting grasses, clover, cereals, and crop seedlings, which can lead to turf wilting and plant death at high densities (e.g., >20 grubs per square meter). Early instars detect roots via carbon dioxide gradients, preferring fine feeder roots, while later stages consume coarser structures, contributing to agricultural losses estimated at significant pasture degradation in outbreak years. Prior to pupation in late summer of the final year, mature grubs cease feeding and form an earthen cell at 20-50 cm depth.

Distribution and Habitat Preferences

Geographic Range

The common cockchafer (Melolontha melolontha) is native to Europe, where it occurs widely across temperate regions suitable for its soil-dwelling larvae. Its distribution spans from the British Isles and Iberian Peninsula in the west to the Ural Mountains in the east, and from southern Scandinavia southward to the northern Mediterranean basin, including countries such as France, Germany, Austria, Poland, and Turkey. This range aligns with Palaearctic patterns for the genus Melolontha, though M. melolontha predominates in European arable and forested landscapes. Populations exhibit synchronized outbreaks in , with documented infestations tied to historical agricultural monitoring since the 19th century, reflecting stable endemic presence rather than recent expansions. No verified established populations exist outside , despite occasional misidentifications with similar scarab beetles like North American June bugs (Phyllophaga spp.). The species' range limits are influenced by climatic factors, with absences in extreme northern or arid southern zones due to unsuitable overwintering conditions for larvae at depths of 20–100 cm.

Environmental Conditions

The common cockchafer (Melolontha melolontha) inhabits temperate regions characterized by mild climatic conditions, particularly valley floors where are favorable for development. Larvae develop in soft, shaded soils with adequate moisture, often in agricultural grasslands or edges, where supports burrowing and root access. Adults emerge from the soil in , typically after the cumulative mean daily air temperature exceeds 355 degree-days, signaling warming conditions above approximately 10–15°C. Soil pH influences grub abundance, with populations observed in acidic conditions ( 4.5–5.0) and a positive correlation between higher values (measured in water or CaCl₂) and grub in some stands. Preferred soils are typically loamy or sandy, providing drainage while retaining essential for larval survival and oviposition; dense layers reduce egg cluster by limiting access. Optimal larval growth occurs at soil temperatures of 20–25°C, with development slowing below 15°C. Humidity and proximity to open spaces also affect occurrence, with enhancing grub presence in habitats.

Life Cycle

Developmental Phases

The cockchafer (Melolontha melolontha) exhibits holometabolous development, progressing through , , , and stages over a 3- to 4-year cycle synchronized across populations in infested areas. Approximately 98% of the life cycle occurs underground as , larva, or pupa. Egg stage. Females deposit 60-80 oval eggs (initially 2 mm long, swelling to 3 mm via water absorption) in soil batches of 10-30 at depths of 5-20 cm, primarily in May to June. Eggs hatch after 4-6 weeks into first-instar larvae, with embryonic development influenced by soil temperature and moisture. Larval stage. Hatched larvae (L1 instar) are C-shaped, whitish grubs 5-10 mm long with brown heads and strong mandibles, initially feeding on soil organic matter before targeting plant roots. Three instars occur over 3-4 years: L1 grows to 10-20 mm by first autumn; L2 to 30-35 mm by second autumn; L3 reaches 40-46 mm by third spring, burrowing deeper (up to 1 m) and causing root damage. Larvae overwinter 2-3 times, resuming activity in spring when soil warms above 10°C. Pupal stage. In late spring or early summer of the final year, third-instar larvae form earthen cells 20-30 cm deep and te; the measures 25-35 mm, initially whitish turning reddish-brown. This stage lasts 1.5-2 months under optimal conditions (soil temperature 15-20°C), though it may extend to 10 months during or cold. Pupae remain immobile and vulnerable to soil disturbance. Adult stage. New adults (25-30 mm long) eclose in summer but remain in pupal cells until the following spring (April-May), emerging en masse when reaches 12-15°C for swarming flights. Adults live 4-8 weeks, feeding minimally on foliage while prioritizing ; post-oviposition, they die, completing the cycle.

Reproductive Processes

Adult Melolontha melolontha engage in mating shortly after emergence in late April to May, with peak activity in late May to early June. Males undertake swarming flights in the evening, orienting toward females in the tree canopy via detection of sex pheromones emitted by females and synergized with green leaf volatiles (such as (Z)-3-hexen-1-ol) released from foliage damaged by female feeding. These cues enable males' large antennae to locate receptive females, facilitating copulation primarily among branches. occurs during this period, after which males cease flying and die within weeks, while females persist briefly for oviposition. Post-mating, gravid females descend at to suitable ground sites, burrowing 10-20 cm into soft, moist soils—preferentially sandy or loamy with adequate —to deposit eggs. Eggs, pearly white and spherical at 2-3 diameter, are laid in batches of 12-30, often in clusters within a small cavity that the female then covers. Oviposition typically spans one or two phases separated by about two weeks, influenced by conditions and female endocrine responses to environmental factors like and . Each female produces 40-100 eggs total across depositions, though actual varies with habitat quality. occurs after 4-6 weeks under favorable conditions ( 10-15°C), yielding C-shaped larvae that initiate the subterranean phase.

Feeding Ecology

Larval Feeding

The larvae of the cockchafer (Melolontha melolontha), commonly referred to as white grubs, are C-shaped, subterranean feeders that primarily consume live plant roots rather than decaying organic matter. They exhibit polyphagous and largely indiscriminate feeding, gnawing on small fibrous roots of grasses, grains, beets, trees, clover, dandelions, meadow herbs, fruit trees, forest trees, and vines. Younger instars (10-20 mm in length) initially target finer roots during the first autumn after hatching, while larger second- and third-instar grubs (up to 40-46 mm) progress to thicker roots, escalating consumption intensity. Feeding occurs actively from mid-April to in the second year of the larval stage, with grubs burrowing through at depths of 0-20 cm during the and up to 60 cm during winter ; they can relocate up to 30 cm per day while foraging on rootlets. Juveniles acquire symbiotic gut for cellulose digestion by ingesting parental excrement shortly after hatching, enabling efficient breakdown of root tissues. This prolonged root herbivory, spanning 3-4 years across three instars, severs vascular tissues, impairs water and nutrient uptake, and causes retarded growth, , or death in affected , with peak damage often manifesting in the year following adult swarming. In agricultural contexts, dense populations can devastate grasslands, cereals, and orchards by depleting systems, weakening trees, and leading to crop failure.

Adult Consumption

Adult cockchafers (Melolontha melolontha) primarily feed on the leaves and flowers of trees and shrubs during their brief adult phase in . Preferred host plants include (Quercus spp.), (Fagus sylvatica), (Acer spp.), sweet (Castanea sativa), (Prunus domestica), (Juglans spp.), and other fruit trees, with occasional consumption of (Larix spp.) needles and leaves. Feeding behavior involves chewing irregular holes or skeletonizing leaves, typically at or night, though damage remains limited compared to larval feeding due to the adults' short lifespan of 4-6 weeks and relatively low population densities. In regions like the , adult defoliation rarely reaches destructive levels, affecting canopy but not threatening tree health. Experimental studies indicate that food source quality influences adult survival, weight gain, and fecundity; and leaves support higher relative weight gains and longer lifespans than lower-quality options like needles, with females showing greater sensitivity to diet variations. For instance, adults fed European needles exhibited intermediate weight gains relative to those on foliage.

Behavioral Patterns

Swarming and Mating

Adult cockchafers (Melolontha melolontha) emerge from the soil in spring, typically from late April to early June in , initiating a brief phase lasting 4–6 weeks focused on . Males exhibit pronounced swarming , forming aggregations and engaging in mass flights primarily at , often near edges, tree canopies, and open meadows, with activity peaking in calm, warm conditions above 15°C.00835-5) These flights can extend up to 2–3 km from emergence sites, driven by orientation toward host plants rather than random dispersal. Swarming is male-biased, with females remaining largely stationary on foliage to feed on , , and other leaves, minimizing their flight activity post-emergence. Male attraction relies on a multimodal cue system: feeding by females induces emission of green leaf volatiles (GLVs) from damaged foliage, such as (Z)-3-hexen-1-ol, functioning as a that simulates host plant signals and draws swarming males. Toluquinone, a compound potentially released from female defensive glands, further enhances this as a sex-specific attractant, eliciting oriented landings and upwind flight in field assays. While some observations suggest supplementary female pheromones during feeding, prioritizes plant-derived volatiles over volatile pheromones for primary mate location.00835-5) Upon arrival at aggregation sites, males perform displays, including wing fanning and tactile interactions, before copulation on leaves or branches; mating duration is typically short, lasting minutes, after which males may seek additional partners. Females, having mated once or multiply, cease feeding soon after and descend to for oviposition, depositing 20–30 eggs in clusters 5–20 cm deep in moist, humus-rich substrates, though this marks the transition from to egg-laying. Swarming intensity correlates with , with historical outbreaks in documenting flights numbering thousands per , amplifying defoliation risks during peak activity.

Dispersal Mechanisms


The primary dispersal mechanism of the cockchafer (Melolontha melolontha) is active flight by adults, which emerge from pupal chambers in spring and take to the air primarily during evening hours to seek mates, foliage for feeding, and suitable oviposition sites. Flight occurs in swarms, producing a distinctive loud buzzing from rapid beats, facilitating aggregation along edges or open areas. This enables short-range relocation, with adults typically covering distances of up to 2-3 kilometers from points before settling.
Larval stages exhibit negligible active dispersal, limited to crawling within the upper layers over distances of mere centimeters to meters during feeding or vertical migration for overwintering. Eggs are laid in clusters near adult aggregation sites, relying on parental mobility rather than independent larval spread. Passive transport via movement or activity occurs rarely and does not significantly contribute to expansion. Genetic analyses reveal moderate across populations, implying occasional dispersal events exceeding typical flight ranges, possibly aided by wind or human-mediated soil translocation, though direct evidence remains sparse. Overall, the ' limited mobility restricts outbreak to local scales, with synchronized life cycles amplifying densities in favorable habitats without widespread migration.

Natural Enemies

Predatory Interactions

The larvae of Melolontha melolontha, known as white grubs, are a primary target for soil-dwelling predators, including moles (Talpa europaea) that tunnel through turf to consume them, often leading to visible surface damage from their foraging. (Meles meles), foxes (Vulpes vulpes), and other mammals such as hedgehogs (Erinaceus europaeus) and martens excavate grubs from the upper soil layers, particularly in grasslands and agricultural fields where larval densities peak. These mammalian predators can exacerbate lawn and crop damage during outbreaks, as their digging disrupts roots while targeting the grubs, with reports noting severe turf disruption from badger activity in infested areas. Avian predators play a significant role in controlling both larval and adult stages; rooks (Corvus frugilegus) and other corvids probe the soil for grubs, while woodpeckers, sparrows, and cuckoos (Cuculus canorus) consume emerging adults during swarming periods in spring. Ground beetles (Carabidae family) and predatory wasps prey on smaller larvae and eggs, contributing to natural population regulation in meadows and woodlands. Bats opportunistically feed on flying adults at dusk, attracted to their erratic flight patterns. Tachinid flies () parasitize adult cockchafers by laying eggs on their bodies, with larvae developing internally and emerging to pupate, thus reducing adult populations in outbreak years; this interaction is documented in European field studies as a density-dependent control mechanism. While these predators collectively limit cockchafer numbers, their efficacy varies with and use, which can diminish predator abundance and allow larval persistence in for 3–4 years.

Parasitic and Pathogenic Controls

Parasitic nematodes, particularly species in the genera Heterorhabditis and Steinernema, serve as natural enemies of cockchafer larvae (Melolontha melolontha) by invading the host's body and releasing symbiotic bacteria that cause septicemia and death. Heterorhabditis bacteriophora targets soil-dwelling grubs effectively under moist conditions, with field applications demonstrating up to 70-90% mortality in third-instar larvae when applied at rates of 2-5 million infective juveniles per square meter. Similarly, Heterorhabditis megidis has been documented to parasitize cockchafer grubs, reducing populations in agricultural soils through targeted inundative releases. A native species, Neoaplectana melolonthae (now classified under Steinernema), was identified parasitizing larvae in Central Europe, indicating endemic parasitic pressure that contributes to natural population regulation. Entomopathogenic fungi represent key pathogenic controls, with Beauveria brongniartii exhibiting high virulence against M. melolontha larvae and adults in European grasslands and orchards. This fungus infects via cuticle penetration, leading to mycosis; clonal populations of B. brongniartii have been isolated from infected cockchafers, supporting its role in epizootics that can suppress outbreaks when humidity exceeds 80%. Metarhizium anisopliae and Beauveria bassiana also demonstrate pathogenicity, with conidial applications achieving 50-80% larval mortality in laboratory bioassays, though field efficacy varies with soil type and temperature (optimal at 15-25°C). These fungi are deployed in biocontrol formulations, often combined with nematodes for synergistic effects, as chemical fungicides can reduce their persistence. Bacterial pathogens, such as those symbionts of nematodes (e.g., Xenorhabdus spp. with Heterorhabditis), indirectly control cockchafers by disseminating within the host , though direct bacterial entomopathogens like Bacillus thuringiensis show limited efficacy against scarab larvae due to interference. Research indicates cockchafer bacteria can confer resistance to some pathogens, complicating control, but no widespread viral pathogens have been established for M. melolontha management as of 2024. Overall, these biological agents prioritize larval stages, exploiting the cockchafer's 3-4 year subterranean cycle for long-term suppression without broad environmental disruption.

Pest Dynamics

Agricultural and Economic Impacts

The larvae of Melolontha melolontha, known as white grubs, primarily damage agricultural crops by feeding on root systems, particularly those of grasses, cereals, potatoes, , fruit trees, and vines, which retards plant growth, causes withering, and can lead to complete crop failure in heavily infested fields. Adult beetles contribute to agricultural losses through on leaves of orchards and field crops, exacerbating yield reductions during emergence periods. In regions like , these impacts are most pronounced in permanent grasslands and horticultural areas, where grub densities can destroy extensive root networks over 3-4 year larval development cycles. In , adult cockchafers cause defoliation of species such as , , and , as well as like , with mass swarms potentially stripping entire canopies and leading to dieback or clear-cutting equivalents in severe outbreaks. Larval feeding further weakens young trees and seedlings, resulting in high mortality rates in plantations, as observed in forests where extensive losses have been documented despite declining beetle abundances. Such damage has historically prompted interventions in countries like and , where cockchafers are classified as major forest pests capable of altering stand composition. Economic consequences arise from cyclical outbreaks synchronized every 3-4 years, with historical mass events in the late 1940s to early 1950s across Europe causing substantial yield losses in agriculture and forestry, necessitating costly control efforts like soil treatments and manual collections. In Germany, these outbreaks have inflicted "huge damages" on croplands and woodlands, while in Czechoslovakia's 1956-1968 outbreak, grubs inflicted peak destruction on orchards and vineyards, underscoring ongoing threats to productivity in affected regions. Although precise monetary valuations vary by outbreak scale, the pest's role in driving control expenditures and reducing harvestable biomass highlights its persistent economic burden in European agrosystems.

Outbreak Patterns

Cockchafers (Melolontha melolontha) display outbreak patterns characterized by periodic mass emergences of adults, synchronized with their 3- to 4-year life cycle, during which larvae develop underground before pupating and emerging to defoliate vegetation en masse. These cycles arise from overlapping but phased larval cohorts, with full in localized populations leading to outbreaks every 3 years in regions like , as evidenced by defoliation-induced narrow tree rings in . Outbreaks typically peak in to , with adults swarming in densities sufficient to strip leaves from trees and crops over several weeks, followed by oviposition that replenishes larval populations. Longer-term dynamics reveal superimposed multi-decadal cycles, with historical records indicating 30- to 40-year intervals between major outbreak phases lasting up to 10 years, potentially influenced by climatic factors such as warming temperatures that enhance larval survival and population buildup. In subfossil tree trunks from sites like Tovacov, Czech Republic, dendrochronological analysis confirms recurring 3- to 5-year outbreak cycles dating back centuries, marked by growth suppressions from larval root feeding and adult defoliation. Regional variations occur; for instance, in the Vosges Mountains of northeastern France, populations reached epidemic levels starting in 2007, persisting due to favorable soil and forest edge conditions that promote high larval densities exceeding economic thresholds. Genetic structuring within populations contributes to outbreak resilience, with low between subpopulations allowing localized booms despite natural enemies, though asynchronous cohorts in some areas mitigate severity by preventing total . Outbreaks are more pronounced in mixed forests and grasslands with open-forest boundaries, where facilitate higher grub occurrence, amplifying damage to regeneration phases in . These patterns underscore the ' capacity for eruptive dynamics, driven primarily by intrinsic life-history traits rather than external perturbations alone.

Control Measures

Historical Interventions

Manual collection of adult cockchafers during their swarming phase constituted a primary historical intervention across Europe, involving shaking beetles from trees onto sheets or using nets to capture them en masse, followed by destruction through burning or crushing. This method was labor-intensive and targeted peak flight periods in spring, often organized at community or governmental levels during outbreaks to mitigate crop defoliation. Effectiveness depended on population density and participation scale, with records from Germany indicating such efforts reduced local swarms but failed to prevent larval establishment in soil. For larval stages, of infested fields exposed white grubs to sunlight, , and predation by birds or other , a practice documented in agricultural treatises from the onward. In the , historical overviews trace interventions back to 1786, where plowing combined with manual grub removal from turned soil addressed outbreaks in arable lands, though grubs' deep burrowing limited success rates to partial reductions in infestation. These cultural methods disrupted life cycles without chemicals but required repeated annual applications over the 3-4 year larval period, often supplemented by fallow periods or to starve populations. Early chemical interventions emerged in the late 19th and early 20th centuries with inorganic poisons like (copper acetoarsenite) applied to foliage against adults or soil for grubs, marking a shift from mechanical reliance in regions like and amid severe plagues. Such treatments, while more potent, proved indiscriminate, harming beneficial and , and were gradually supplanted by organochlorines post-World War II. Historical efficacy varied, with pre-chemical eras seeing recurrent outbreaks due to incomplete eradication, underscoring the pests' resilience tied to 4-year cycles and soil longevity.

Modern Biological and Chemical Strategies

Modern biological control strategies for cockchafer (Melolontha melolontha) primarily target the soil-dwelling larval stage, known as white grubs, which cause the majority of agricultural damage by feeding on plant roots. Entomopathogenic nematodes (EPNs), such as species from the genera Heterorhabditis and Steinernema, have been tested for inundative application against grubs, with laboratory and pot experiments demonstrating mortality rates varying by nematode concentration (e.g., 500–2000 infective juveniles per ) and , achieving up to 80–100% control in controlled settings but lower field efficacy due to factors like and . These nematodes enter grubs via openings, releasing symbiotic bacteria (Xenorhabdus or Photorhabdus spp.) that cause septicemia, offering a targeted alternative to broad-spectrum chemicals with minimal impact on non-target organisms when applied in moist conditions during early larval instars. Entomopathogenic fungi, particularly Beauveria brongniartii, represent another key biological approach, with commercial formulations like Beauveria–Schweizer® (strain BIPESCO 4, introduced in 1990) and Melocont® Pilzgerste (strain BIPESCO 2, since 2000) applied as soil inoculants or baits to infect grubs and adults. Field studies in Alpine regions show these fungi persisting in soil at densities of 10³–10⁴ colony-forming units per gram dry weight, yielding grub prevalences of 4.5–42.9% and reducing populations over multiple seasons through among insects. Similarly, brunneum has shown promise in granular soil applications against related scarab larvae, though efficacy against M. grubs remains variable (50–80% mortality in lab trials), influenced by fungal strain clonality and environmental persistence. These fungal agents integrate well into IPM frameworks, as their and site-specific dispersal limit unintended spread while exploiting grub for contact . Chemical strategies have shifted toward selective insecticides due to regulatory restrictions in , such as the 2018 outdoor ban on neonicotinoids like , which previously targeted adult swarms or early grubs via soil drenches but posed risks to pollinators. For grub control, anthranilic diamides like (e.g., in Acelepryn formulations) provide preventive and curative action by disrupting muscle function in feeding larvae, achieving 70–90% efficacy against white grubs when applied pre-infestation in turf or crops, though specific trials on M. melolontha indicate reduced performance in heavy soils or against later instars. Adult control relies on foliar sprays of (e.g., Mospilan 20 SP at 0.4 kg/ha), registered in some regions for reducing egg-laying, with field reductions of 60–80% in emerging beetles when timed to peak flight in spring. Overall, modern IPM combines these with cultural practices like to expose grubs to natural enemies, prioritizing biological agents to minimize resistance and ecological disruption, as chemical reliance has historically led to inconsistent long-term suppression.

Ecological Consequences

Soil and Plant Interactions

The larvae of the cockchafer (Melolontha melolontha), known as grubs, primarily inhabit the upper layers of in grasslands, forests, and agricultural fields, where they spend 3 to 4 years in development before pupating. These C-shaped larvae through the and feed voraciously on the roots of grasses, herbaceous , and occasionally tree seedlings, consuming fine lateral roots and organic . This root-feeding behavior disrupts plant anchorage and vascular systems, often leading to , reduced , and die-back in affected vegetation, particularly during dry periods when water uptake is impaired. Ecologically, cockchafer larval activity influences plant-soil feedback loops by inducing chemical changes in root exudates and volatiles; for instance, damage to roots by M. melolontha grubs alters belowground volatile profiles, potentially signaling neighboring plants or attracting natural enemies, while aboveground emissions shift to attract parasitoids. In mixed communities, larval performance improves when feeding near plants with pre-damaged roots from conspecifics or competitors, such as Taraxacum officinale alongside Centaurea stoebe, mediated by root volatile interactions that enhance nutrient availability or reduce plant defenses. This selective herbivory can alter plant community composition, favoring resilient species with robust root defenses like increased phenolic production or mycorrhizal associations. Regarding soil dynamics, the burrowing of large grubs (up to 5 cm long) aerates compacted soils and incorporates deeper into profiles, potentially enhancing microbial activity and nutrient cycling akin to other scarabid larvae that process in their guts. However, high densities during outbreaks—exceeding 100 grubs per square meter—predominantly degrade by severing root networks, reducing organic input from aboveground litter and promoting in grasslands. Entomopathogenic fungi applied for control further interact with soil microbiota, indirectly affecting larval gut communities and rates, underscoring the grubs' role in belowground trophic webs.

Broader Ecosystem Effects

The larvae and adults of Melolontha melolontha play a key role as prey in terrestrial food webs, supporting populations of avian, mammalian, and predators. Ground-dwelling larvae are consumed by moles, rooks, woodpeckers, sparrows, and cuckoos, as well as predatory beetles (Carabidae and Staphylinidae) and flies (). Adult cockchafers are targeted by bats and various birds, providing a pulsed resource during emergence swarms that synchronizes with predator breeding cycles. Swarm years of adult cockchafers positively influence chiropteran demographics, as evidenced by a 31-year study of greater horseshoe s (Rhinolophus ferrumequinum) in Italy's , where cockchafer flight abundance correlated with an 81.58% increase in maternity colony size (from 76 to 138 individuals, 2001–2022) and higher pup production (0.56 pups per adult in flight years versus 0.47 in non-flight years), advancing birth timing by five days. This predator-prey linkage underscores cockchafers' contribution to conservation, with researchers advocating limits on chemical controls to sustain prey availability. High larval densities during outbreaks can attract opportunistic mammals such as wild boars and feral pigs, which root extensively for grubs, exacerbating disturbance and potentially altering structure for ground-nesting species or vegetation. Conversely, sustained cockchafer presence enhances overall invertebrate-mediated energy transfer, bolstering in grasslands and woodlands where alternative prey is scarce.

Historical and Cultural Context

Etymological Origins

The English term "cockchafer" emerged in the late , with the earliest recorded use dating to in a translation by George Hartman, combining "cock" in the sense of denoting large size or vigor—similar to its application in ""—with "chafer," an archaic word for . This compound reflects the insect's substantial adult size, reaching up to 3 cm in length, distinguishing it from smaller beetles. The element "chafer" derives from Old English ceafor or cefer, traceable to Proto-Germanic *kabraz-, connoting a "gnawer" due to the beetle's habit of damaging roots and foliage as both and adult. Cognates appear in related , such as Dutch kever (), underscoring a shared Indo-European emphasizing the insect's masticating mandibles and herbivorous impact. By the 1690s, "cockchafer" had become the standard name in English for Melolontha melolontha, the common European species, supplanting earlier descriptive terms like "May-beetle" tied to its spring emergence. Alternative etymological speculations, such as a link between the beetle's feathery antennae and a rooster's coxcomb, lack primary textual support and appear in later conjectures without attestation in usage records. The name's persistence aligns with folk nomenclature prioritizing observable traits like size and destructive gnawing over morphological analogies.

Representations in Culture

The cockchafer occupies a notable place in European children's and games, with records of play dating to , where boys tied threads to the beetles' legs to observe their flight. This tradition continued in , where the insect, called the Maikäfer, was similarly captured and manipulated for amusement during its May emergence. In 19th-century German literature, Wilhelm Busch depicted cockchafers in his 1865 satirical children's book Max and Moritz: A Story of Innocents Whom the Rope Did Not Hang, where the titular boys shake the beetles from a tree and scatter them into Uncle Fritz's bed as a prank, leading to comedic chaos. A prominent cultural element is the German children's song "Maikäfer flieg" (May beetle, fly), documented as early as 1800 in Volkssagen von Ottmar and appearing in songbooks by 1843. Sung while holding a thread-attached beetle, its lyrics—"Maikäfer flieg, dein Vater ist im Krieg, deine Mutter ist in Pommernland, Pommernland ist abgebrannt" (May beetle fly, your father is at war, your mother is in Pomerania, Pomerania has burned down)—employ the melody of Johann Friedrich Reichardt's 1781 lullaby "Schlaf, Kindlein, schlaf" and may allude to wartime devastation, with some interpretations linking it to the Thirty Years' War (1618–1648). The insect's familiarity extended to military nomenclature, as evidenced by the British Royal Navy's Insect-class HMS Cockchafer, ordered on February 9, 1915, launched December 17, 1915, and active in operations on the and rivers before further service in until scrapped in 1949. Early 20th-century postcards from and frequently illustrated the Maikäfer in contexts of rural life and seasonal festivities, underscoring its role in cultural as a of spring renewal amid its pest reputation.

References

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