Tetranychus urticae (two-spotted spider mite)
Datasheet Types: Pest, Natural enemy, Invasive species
Abstract
This datasheet on Tetranychus urticae covers Identity, Overview, Distribution, Dispersal, Hosts/Species Affected, Diagnosis, Biology & Ecology, Natural Enemies, Impacts, Prevention/Control, Further Information.
Identity
- Preferred Scientific Name
- Tetranychus urticae Koch
- Preferred Common Name
- two-spotted spider mite
- Other Scientific Names
- Eotetranychus scabrisetus
- Epitetranychus althaeae
- Epitetranychus bimaculatus
- Epitetranychus telarius
- Paratetranychus althaeae von Hanstein
- Tetranychus althaeae von Hanstein
- Tetranychus bimaculatus Harvey
- Tetranychus fragariae
- Tetranychus manihotis
- Tetranychus russeolus
- Tetranychus scabrisetus
- Tetranychus telarius *
- International Common Names
- Englishglasshouse red spider mitegreenhouse red spider mitehop red spider mitetwo spotted mitetwo spotted spider mitetwospotted spider mite
- Spanishácaro comúnarañita de las legumbresaranuela de la patata
- Frencharaignée rouge du cotonnierl'acarien jaune communtétranyque à deux pointstétranyque à deux pointstétranyque commun
- Portugueseácaro rajado (Brasil)
- Local Common Names
- Brazilácaro rajado
- Denmarklindespindemideplettet væksthusspindemidevæksthusspindemide
- Finlandlehmuspunkkivihannespunkki
- GermanySpinne, Rote-Spinnmilbe, Blatt-Spinnmilbe, Bohnen-Spinnmilbe, Eibisch-Spinnmilbe, Gemeine
- Israelhaakarit haadumu hamezuya
- ItalyRagnetto giallo dei giardiniRagnetto giallo della vite e dei tiglioRagno rosso della viteRagno rosso tessitore
- JapanNami-hadani
- Netherlandsaardbeispintmijtbonenspintmijtcassave-mijtkina-mijtrode plantenspin
- Norwayflekket veksthusspinnmidelindespinnmidd
- Swedenlindspinnkvalsterväxthysspinnkvalster
- Turkeyiki benekli orumcek
- EPPO code
- TETRUR (Tetranychus urticae)
Pictures

Adult
Tetranychus urticae (two-spotted spider mite); colour enhannced SEM of an adult mite.
Public Domain - Released by the United States Dept of Agrculture/Agricultural Research Service (USDA-ARS)/original image by the Electron and Confocal Microscopy Unit

Adults
Tetranychus urticae (two-spotted spider mite); adult male (smaller individual) and adult female.
©Horticulture Research International

Adult male
Tetranychus urticae (two-spotted spider mite); adult male.
©Horticulture Research International

Adult female
Tetranychus urticae (two-spotted spider mite); adult female with eggs.
©Horticulture Research International

Adult female
Tetranychus urticae (two-spotted spider mite); adult female with eggs and a larva.
©Horticulture Research International

Diapausing females
Tetranychus urticae (two-spotted spider mite); overwintering (diapausing) females around an apple calyx.
©Horticulture Research International

Damage symptoms
Tetranychus urticae (two-spotted spider mite); speckling on a strawberry leaf.
©Horticulture Research International

Damage symptoms
Tetranychus urticae (two-spotted spider mite); speckling on hop leaves.
©Horticulture Research International

Webbing
Tetranychus urticae (two-spotted spider mite); webbing on strawberry leaves.
©Horticulture Research International

Natural enemy
Phytoseiulus persimilis predatory mites (orange-red individuals), in a colony of T. urticae.
©Horticulture Research International
Summary of Invasiveness
T. urticae is a highly polyphagous, cosmopolitan species, which is readily spread on the wind. Under optimum conditions, it reaches a high population density, and its presence can cause a reduction in crop yield.
Taxonomic Tree
Notes on Taxonomy and Nomenclature
Tetranychus urticae is part of a group of very similar species in the genus Tetranychus. At one time, a species complex included about 60 synonyms, each described from different hosts or from different parts of the world, the best known of which were Tetranychus telarius L., Tetranychus bimaculatus Harvey and Tetranychus altheae von Hanstein. The taxonomy of the genus Tetranychus is still problematical, but may be elucidated using molecular techniques.The list of other names used excludes Tetranychus cinnabarinus, which may be the same species (see Similarities to Other Pests and datasheet for Tetranychus cinnabarinus). Additional synonyms are provided in Bolland et al. (1998). T. urticae is also known as the red spider mite.
Description
EggsThe egg is 0.13 mm in diameter, globular and translucent.LarvaThe larva is pale green and has six legs.Nymphal stagesThere are two nymphal instars, protonymph and deutonymph, with a quiescent interval between them and another between the deutonymph and adult. The nymphs are pale green with darker markings and have eight legs.AdultsThe adult female is 0.6 mm long, pale green or greenish-yellow with two darker patches on the body, which is oval with quite long hairs on the dorsal side. Overwintering females are orange-red in colour. The male has a smaller, narrower, more pointed body than the female.
Species Vectored
Distribution
T. urticae occurs in most parts of the world. It has been recorded from most countries in Europe, Asia, Africa, Australasia, the Pacific and Caribbean islands, North, Central and South America.Other reference sources are given in Bolland et al. (1998).
Distribution Map
Distribution Table
Means of Movement and Dispersal
T. urticae disperses by active walking or by passive transport in the wind and on plants, tools and people (Zhang, 2003). Phoretic dispersal of T. urticae mediated by winged insects is thought to be rare in the wild (Yano, 2004).
Pathway Vectors
Pathway vector | Notes | Long distance | Local | References |
---|---|---|---|---|
Clothing, footwear and possessions (pathway vector) | Yes |
Plant Trade
Plant parts liable to carry the pest in trade/transport | Pest stages | Borne internally | Borne externally | Visibility of pest or symptoms |
---|---|---|---|---|
Flowers/Inflorescences/Cones/Calyx | arthropods/eggs arthropods/nymphs arthropods/adults | Yes | Pest or symptoms usually visible to the naked eye | |
Fruits (inc. pods) | arthropods/eggs arthropods/nymphs arthropods/adults | Yes | Pest or symptoms usually visible to the naked eye | |
Growing medium accompanying plants | arthropods/eggs arthropods/nymphs arthropods/adults | Yes | Pest or symptoms usually visible to the naked eye | |
Leaves | arthropods/eggs arthropods/nymphs arthropods/adults | Yes | Pest or symptoms usually visible to the naked eye | |
Seedlings/Micropropagated plants | arthropods/eggs arthropods/nymphs arthropods/adults | Yes | Pest or symptoms usually visible to the naked eye | |
Stems (above ground)/Shoots/Trunks/Branches | arthropods/eggs arthropods/nymphs arthropods/adults | Yes | Pest or symptoms usually visible to the naked eye |
Plant parts not known to carry the pest in trade/transport |
---|
Bulbs/Tubers/Corms/Rhizomes |
Roots |
True seeds (inc. grain) |
Hosts/Species Affected
T. urticae has a very wide host range. It includes many crops grown in glasshouses such as tomatoes, cucumbers and peppers and flowers such as chrysanthemums and orchids. It is also a problem on protected and unprotected strawberries. In some areas it is a problem on field-grown fruit crops such as apples, pears and on grapevines. Other important crops that are infested include cotton, soyabeans and other legumes. This mite can also live on many non-crop hosts, which can provide a source of infestation. A more exhaustive list of hosts is given by Bolland et al. (1998).
Host Plants and Other Plants Affected
Growth Stages
Post-harvest
Symptoms
Feeding by T. urticae causes pale spots to appear on leaves. As infestations become more severe, leaves appear bronzed or silvery, become brittle, and may fall prematurely. Plants can be killed quite rapidly by this mite.The mites spin webbing, which can cover all the surfaces of the plant.
List of Symptoms/Signs
Symptom or sign | Life stages | Sign or diagnosis | Disease stage |
---|---|---|---|
Plants/Leaves/abnormal colours | |||
Plants/Leaves/abnormal leaf fall | |||
Plants/Leaves/webbing |
Similarities to Other Species/Conditions
Several species of Tetranychus look similar to T. urticae, and have similar biology. Some of the morphological differences between Tetranychus species were described by Boudreaux and Dosse (1963). However, it is difficult to separate some of these species and, more recently, new biochemical and molecular techniques have been used to try and distinguish between them. Enohara and Amano (1996) studied six species of Tetranychus common in Japan, which are difficult to separate: T. urticae, T. kanzawai, T. phaselus, T. ludeni, T. viennensis and T. piercis. They found that esterase patterns showed species specific characteristics and that the morphological characters of the adult females could also be used to distinguish between species. Goka and Takafuji (1997) used polyacrylamide gel electrophoresis to study the differences between two enzymes among seven species of Tetranychus and concluded that these enzymes could be useful markers for classification. Navajas et al. (1997) used nucleotide sequence variation and morphological characters to study the evolutionary relationships among nine tetranychid mite species.The relationship/conspecificity with Tetranychus cinnabarinus is still problematical: molecular techniques seem to show them as conspecifics, for example, Gotoh and Tokioka (1996). More recently, Zhang and Jacobson (2000) reported on the use of adult female morphological characters to differentiate between T. urticae and T. cinnabarinus. They stated that T. cinnabarinus could be readily separated from T. urticae by variation in the number of setae on tibia I in females.
Biology and Ecology
GeneticsImportant economic species of Tetranychidae tend to have a chromosome number of n = 3 (Hussey and Huffaker, 1976). See Overmeer and Harrison (1969) and Mitchell (1972) for reports on genetic variation with respect to factors controlling the sex ratio of T. urticae. Refer to Hussey and Huffaker (1976), and references therein, for further information on the genetics of spider mites.Physiology and phenologyT. urticae has an overwintering or diapause form of the adult female that is initiated by short photoperiod, decreased temperature and unfavourable food supply. The overwintering females stop feeding and egg laying and leave their host plants to hibernate in cracks and crevices in protected places, such as the soil or glasshouse structures. They resume activity in the spring when they lay eggs on leaves. These mites also produce copious amounts of webbing.Reproductive biologyThe development of the mite is rapid, particularly at high temperatures. At 30-32°C, which is the optimum temperature for development, the egg stage lasts 3-5 days, the larval/nymphal stages 4-5 days, and with a pre-oviposition period of 1-2 days, the total life cycle takes only 8-12 days. Each female can lay an average of 90-110 eggs during a lifetime of about 30 days, therefore numbers of mites can increase very rapidly during the summer, or under glass or plastic.There is much additional information available on cytology and sex determination, mating behaviour, sex ratio, genetics, etc. Much of this information is reviewed in the chapters by various authors in the volumes on spider mites edited by Helle and Sabelis (1995a, b).
Natural enemy of
Notes on Natural Enemies
At each separate locality there is a complex of local predators, hence lists of natural enemies are long and of limited value in other locations. The most effective natural enemies of T. urticae are predatory mites from the family Phytoseiidae. These mites, belonging to a number of genera, such as Amblyseius, Euseius, Neoseiulus and Phytoseius, have been shown to regulate populations of T. urticae on a range of crops. Phytoseiulus persimilis successfully controls the mite in greenhouses. It is also sometimes useful outdoors and has been released into the field; usually augmentative releases are required to maintain control.Species of Stethorus, a group of small ladybird beetles (Coccinellidae), are also important predators of spider mites. Other useful predators include anthocorids (mainly Orius spp.), larvae of chrysopids, thrips (e.g. Scolothrips spp.), staphylinids (e.g. Oligota spp.), and larvae of cecidomyiid midges, in particular Feltiella acarisuga (=Therodiplosis persicae).Epidemics of fungal disease sometimes occur, particularly in warm, humid conditions. These epidemics are usually caused by Neozygites spp.
Natural enemies
Natural enemy | Type | Life stages | Specificity | References | Biological control in | Biological control on |
---|---|---|---|---|---|---|
Acaropsellina sollers | Predator | Adults Nymphs | ||||
Aegyptocheyla summersi | Predator | Adults Nymphs | ||||
Aeolothrips intermedius | Predator | Adults Nymphs | Italy | maize; soyabeans | ||
Agistemus cyprius | Predator | Adults Nymphs | ||||
Agistemus exsertus | Predator | Adults Nymphs | Egypt | |||
Allothrombium pulvinus | Parasite | |||||
Amblydromella denmarki | Predator | Adults Nymphs | ||||
Amblydromella rhenanoides | Predator | Adults Nymphs | Italy | Acer campestre | ||
Amblyseiella setosa | Predator | Adults Nymphs | ||||
Amblyseius addoensis | Predator | Adults Nymphs | ||||
Amblyseius agrestis | Predator | Adults Nymphs | ||||
Amblyseius andersoni | Predator | Adults Nymphs | Belgium; Ukraine | |||
Amblyseius barkeri | Predator | Adults Nymphs | Italy | soyabeans; Urtica dioica | ||
Amblyseius bibens | Predator | Adults Nymphs | ||||
Amblyseius bicaudus | Predator | Adults Nymphs | Italy | maize; soyabeans | ||
Amblyseius degenerans | Predator | |||||
Amblyseius eharai | Predator | Adults Nymphs | ||||
Amblyseius herbarius | Predator | Adults Nymphs | Italy | soyabeans; Urtica dioica | ||
Amblyseius herbicolus | Predator | Adults Nymphs | Japan | |||
Amblyseius idaeus | Predator | Adults Nymphs | Sao Paulo | |||
Amblyseius largoensis | Predator | Adults Nymphs | ||||
Amblyseius limonicus | Predator | Adults Nymphs | ||||
Amblyseius mckenziei | Predator | Adults Nymphs | USSR | |||
Amblyseius neolentiginosus | Predator | Adults Nymphs | ||||
Amblyseius nicholsi | Predator | |||||
Amblyseius obtusus | Predator | Adults Nymphs | Italy | Urtica dioica | ||
Amblyseius olivi | Predator | Adults Nymphs | ||||
Amblyseius paraki | Predator | Adults Nymphs | ||||
Amblyseius potentillae | Predator | Adults Nymphs | Italy | Lonicera; maize | ||
Amblyseius potentillae | Predator | Adults Nymphs | ||||
Amblyseius pseudolongispinosus | Predator | Adults Nymphs | ||||
Amblyseius rademacheri | Predator | Adults Nymphs | Italy | soyabeans; Urtica dioica | ||
Amblyseius reductus | Predator | Adults Nymphs | Ukraine; USSR | |||
Amblyseius sessor | Predator | Adults Nymphs | ||||
Amblyseius swirskii | Predator | Adults Nymphs | ||||
Amblyseius victoriensis | Predator | Adults Nymphs | Australia; New South Wales | peachs | ||
Amblyseius vignus | Predator | Adults Nymphs | ||||
Anthoseius caudiglans | Predator | Adults Nymphs | ||||
Anystis baccarum (whirligig mite) | Predator | Adults Nymphs | ||||
Bacillus thuringiensis kurstaki | Pathogen | |||||
Bacillus thuringiensis thuringiensis | Pathogen | |||||
Balaustium putmani | Predator | Adults Nymphs | ||||
Beauveria bassiana (white muscardine fungus) | Pathogen | |||||
Campylomma diversicornis | Predator | Adults Nymphs | ||||
Campylomma verbasci (mullein bug) | Predator | Adults Nymphs | ||||
Cardiastethus nazarenus | Predator | Adults Nymphs | ||||
Cheiracanthium mildei | Predator | Adults Nymphs | ||||
Cheletogenes ornatus | Predator | Adults Nymphs | ||||
Chernes cimicoides | Predator | Adults Nymphs | ||||
Chrysopa orestes | Predator | Adults Nymphs | ||||
Chrysoperla carnea (aphid lion) | Predator | Adults Nymphs | Canada; Ontario; Italy | maize; peaches; soyabeans | ||
Conidiobolus obscurus (parasite of cereal aphids) | Pathogen | |||||
Conidiobolus thromboides (parasite of aphids) | Pathogen | |||||
Coniopteryx esbenpeterseni | Predator | Adults Nymphs | ||||
Conwentzia psociformis | Predator | Adults Nymphs | ||||
Cunliffella panamensis | Predator | Adults Nymphs | ||||
Deraeocoris fasciolus | Predator | Adults Nymphs | ||||
Deraeocoris punctulatus | Predator | Adults Nymphs | ||||
Dictyna consulta | Predator | Adults Nymphs | ||||
Erynia radicans (insect pathogen) | Pathogen | |||||
Eupeodes corollae | Predator | Adults Nymphs | ||||
Euseius concordis | Predator | Adults Nymphs | ||||
Euseius fustis | Predator | Adults Nymphs | ||||
Euseius gossipi | Predator | Adults Nymphs | ||||
Euseius gossipi | Predator | Adults Nymphs | Egypt | |||
Euseius mesembrinus | Predator | Adults Nymphs | ||||
Euseius scutalis | Predator | Adults Nymphs | ||||
Euseius stipulatus | Predator | Adults Nymphs | Italy | soyabeans; Urtica dioica | ||
Feltiella acarivora | Predator | Adults Nymphs | ||||
Feltiella macgregori | Predator | Adults Nymphs | ||||
Frankliniella occidentalis (western flower thrips) | Predator | Adults Nymphs | ||||
Frankliniella schultzei (cotton thrips) | Predator | |||||
Galendromus annectens | Predator | Adults Nymphs | ||||
Galendromus helveolus | Predator | Adults Nymphs | ||||
Geocoris pallens (bug, western bigeyed) | Predator | Adults Nymphs | ||||
Geocoris punctipes | Predator | Adults Nymphs | ||||
Haplothrips victoriensis (flower, thrips, black) | Predator | Adults Nymphs | Australia; South Australia | Medicago sativa | ||
Hemicheyletia bakeri | Predator | Adults Nymphs | ||||
Hirsutella thompsonii (parasite: insects) | Pathogen | Adults Nymphs | ||||
Holobus minutus | Predator | Adults Nymphs | ||||
Holoparasitus caesus | Predator | Adults Nymphs | ||||
Holoparasitus pseudoperforatus | Predator | Adults Nymphs | ||||
Hyaliodes vitripennis (glassy-winged soldier bug) | Predator | Adults Nymphs | ||||
Hypoaspis aculeifer | Parasite | |||||
Kampimodromus aberrans | Predator | Adults Nymphs | Switzerland | |||
Lasioseius scapulatus | Predator | Adults Nymphs | ||||
Macrolophus caliginosus | Predator | Adults Nymphs | ||||
Macrolophus nubilus | Predator | Adults Nymphs | ||||
Metaseiulus occidentalis (western predatory mite) | Predator | |||||
Micromus angulatus | Predator | Adults Nymphs | Italy | maize; soyabeans | ||
Micromus tasmaniae (tasmanian lacewing) | Predator | Adults Nymphs | ||||
Mycosphaerella tassiana (antagonist of Botrytis cinerea) | Pathogen | |||||
Nabis kinbergii | Predator | Adults Nymphs | ||||
Nabis palifer | Predator | Adults Nymphs | ||||
Neoseiulella aceri | Predator | Adults Nymphs | Italy | Acer campestre | ||
Neoseiulella tiliarum | Predator | Adults Nymphs | ||||
Neoseiulus alpinus | Predator | |||||
Neoseiulus anonymus | Predator | Adults Nymphs | ||||
Neoseiulus californicus | Predator | Eggs Nymphs | ||||
Neoseiulus chilenensis | Predator | Adults Nymphs | ||||
Neoseiulus cucumeris | Predator | |||||
Neoseiulus fallacis (predaceous, mite) | Predator | |||||
Neoseiulus longispinosus | Predator | Adults Nymphs | Japan | |||
Neoseiulus setulus | Predator | Adults Nymphs | ||||
Neoseiulus teke | Predator | Adults Nymphs | ||||
Neozygites adjarica | Pathogen | |||||
Neozygites floridana | Pathogen | |||||
Neozygites na | Pathogen | |||||
Oligota flavicornis | Predator | Adults Nymphs | Italy | Acer campestre; Carpinus betulus | ||
Oligota kashmirica | Predator | Adults Nymphs | ||||
Oligota kashmirica benefica | Predator | Adults Nymphs | ||||
Oligota oviformis | Predator | Adults Nymphs | ||||
Oligota pygmaea | Predator | Adults Nymphs | ||||
Oligota yasumatsui | Predator | Adults Nymphs | ||||
Orius albidipennis | Predator | Adults Nymphs | ||||
Orius insidiosus | Predator | Adults Nymphs | USA; Virginia | apples | ||
Orius majusculus | Predator | Adults Nymphs | Italy | Acer campestre; Carpinus betulus | ||
Orius minutus | Predator | Adults Nymphs | ||||
Orius niger | Predator | Adults Nymphs | ||||
Orius sauteri | Predator | Adults Nymphs | ||||
Orius tristicolor (minute pirate bug) | Predator | Adults Nymphs | ||||
Orius vicinus | Predator | Adults Nymphs | Italy | Acer campestre; Carpinus betulus | ||
Phalangium opilio (daddy longlegs) | Predator | Adults Nymphs | ||||
Phoenicocoris minusculus | Predator | Adults Nymphs | ||||
Phytoseiulus fallacis | Predator | Adults Nymphs | ||||
Phytoseiulus longipes | Predator | Adults Nymphs | Egypt | |||
Phytoseiulus macropilis | Predator | Adults Nymphs | Florida; Sao Paulo | |||
Phytoseiulus persimilis | Predator | Adults Nymphs | Australia; Australia; Queensland; Australia; South Australia; Australia; Tasmania; Australia; Victoria; Belgium; British Columbia; Bulgaria; California; China; Beijing; China; Shanghai; Czechoslovakia; Denmark; Finland; Florida; France; Germany; India; Irish Republic; Italy; Japan; Latvia; Moldova; Netherlands; New Caledonia; New Zealand; Norway; Ohio; Poland; Romania; Sweden; Switzerland; Taiwan; Tunisia; UK; USA; Texas; USSR; Washington; Egypt | Ageratum conyzoides; Dahlia pinnata; hops; maize; Medicago sativa; Pelargonium lateripes; raspberries; Rosa chinensis; roses; Salvia splendens; strawberries; tomatoes; Zantedeschia aethiopica | ||
Phytoseius domesticus | Predator | Adults Nymphs | ||||
Phytoseius finitimus | Predator | Adults Nymphs | ||||
Phytoseius fotheringhamiae | Predator | Adults Nymphs | ||||
Phytoseius hawaiiensis | Predator | Adults Nymphs | ||||
Phytoseius plumifer | Predator | Adults Nymphs | ||||
Propriorseiopsis messor | Predator | Adults Nymphs | ||||
Proprioseiopsis jugortus | Predator | |||||
Proprioseiopsis rotundus | Predator | |||||
Scolothrips acariphagus | Predator | Adults Nymphs | ||||
Scolothrips longicornis (six-spotted thrips) | Predator | Adults Nymphs | ||||
Scolothrips sexmaculatus (thrips, sixspotted) | Predator | Adults Nymphs | ||||
Scolothrips takahashii | Predator | Adults Nymphs | ||||
Scymnus gracilis | Predator | Adults Nymphs | ||||
Scymnus interruptus | Predator | Adults Nymphs | ||||
Scymnus rubromaculatus | Predator | Adults Nymphs | Italy | Acer campestre; Carpinus betulus | ||
Scymnus rufipes | Predator | Adults Nymphs | Italy | Acer campestre; Carpinus betulus | ||
Seiulus finlandicus | Predator | Adults Nymphs | Italy | Carpinus betulus; Ligustrum | ||
Stethorus bifidus | Predator | Adults Nymphs | ||||
Stethorus fenestralis | Predator | Adults Nymphs | ||||
Stethorus histrio | Predator | Adults Nymphs | Chile | Phaseolus vulgaris; Ricinus communis | ||
Stethorus loi | Predator | Adults Nymphs | Taiwan | Averrhoa carambola | ||
Stethorus nigripes | Predator | Adults Nymphs | Australia; South Australia | Medicago sativa | ||
Stethorus parapauperculus | Predator | Adults Nymphs | ||||
Stethorus punctillum | Predator | Adults Nymphs | France; Italy | Acer campestre; Carpinus betulus; maize | ||
Stethorus punctum | Predator | Adults Nymphs | Pennsylvania | |||
Stethorus punctum picipes | Predator | Adults Nymphs | Canada; British Columbia | strawberries | ||
Stethorus siphonulus | Predator | Adults Nymphs | ||||
Tapinoma melanocephalum (ghost ant) | Predator | |||||
Therodiplosis persicae | Predator | |||||
Thrips imaginis (plague thrips) | Predator | |||||
Typhlodromalus macrosetosus | Predator | Adults Nymphs | ||||
Typhlodromus athiasae | Predator | Adults Nymphs | Israel | apples | ||
Typhlodromus baccettii | Predator | Adults Nymphs | ||||
Typhlodromus exhilaratus | Predator | Adults Nymphs | ||||
Typhlodromus italicus | Predator | Adults Nymphs | ||||
Typhlodromus longipilus | Predator | Adults Nymphs | ||||
Typhlodromus negevi | Predator | Adults Nymphs | ||||
Typhlodromus phialatus | Predator | Adults Nymphs | ||||
Typhlodromus porresi | Predator | Adults Nymphs | ||||
Typhlodromus pyri | Predator | Adults Nymphs | Australia; Switzerland; Tasmania; UK; Czech Republic | |||
Zetzellia graeciana | Predator | Adults Nymphs | ||||
Zetzellia mali | Predator | Adults Nymphs |
Impact Summary
Category | Impact |
---|---|
Animal/plant collections | Negative |
Animal/plant products | Negative |
Biodiversity (generally) | None |
Crop production | Negative |
Environment (generally) | Negative |
Fisheries / aquaculture | None |
Forestry production | None |
Human health | Negative |
Livestock production | None |
Native fauna | None |
Native flora | Negative |
Rare/protected species | None |
Tourism | None |
Trade/international relations | None |
Transport/travel | None |
Impact
During feeding the mites penetrate the plant foliage/leaves with their mouth stylets and suck out the cell contents. On strawberry, low populations of T. urticae mainly damage the spongy mesophyll tissue but higher densities increase the area of damage and injury to the palisade parenchyma occurs (Sances et al., 1979; Kielkiewicz and Van de Vrie, 1983). The function of the stomatal apparatus is also affected, so that the stomata remain closed.
The result of this damage to leaf tissue is reduced chlorophyll content and reduced photosynthesis, carbon dioxide assimilation and transpiration. Such effects have been shown for cotton (Bondana et al., 1995), tomato (Nihoul et al., 1992), apple and peach (Mobley and Marini, 1990), and strawberry (Sances et al., 1982).
Crop yields are diminished as essential plant processes are affected. This has been demonstrated on maize (Archer and Bynum, 1993), strawberry (Oatman et al., 1982), pear (McNab and Jerie, 1993), cotton (Wilson, 1993), soyabean (Singh, 1988; Suekane et al., 2012) and grapevine (Hluchy and Pospisil, 1992), among others.
The result of this damage to leaf tissue is reduced chlorophyll content and reduced photosynthesis, carbon dioxide assimilation and transpiration. Such effects have been shown for cotton (Bondana et al., 1995), tomato (Nihoul et al., 1992), apple and peach (Mobley and Marini, 1990), and strawberry (Sances et al., 1982).
Crop yields are diminished as essential plant processes are affected. This has been demonstrated on maize (Archer and Bynum, 1993), strawberry (Oatman et al., 1982), pear (McNab and Jerie, 1993), cotton (Wilson, 1993), soyabean (Singh, 1988; Suekane et al., 2012) and grapevine (Hluchy and Pospisil, 1992), among others.
The mites feed directly on tomato fruit, causing gold fleck (discolouration of the fruit), which could have a negative impact on the marketability of the fruit (Meck et al., 2012).
Nyoike and Liburd (2013) studied the impact of the mites on the marketable yield of field grown strawberries in Florida and reported that yield reduction in strawberry was detected when plants had 80 mites per leaf in the 2008/2009 growing season, and 50 mites per leaf in the 2009/2010 growing season. Results like this can be used to determine the timing of control programmes, ensuring maximum yields are attained.
The timing of mite infestation has also been shown to have an impact. For example, Gore et al. (2013) reported that early infestations of T. urticae on cotton in mid-southern USA caused the highest impact on yield (compared with later infestations).
Detection and Inspection
Severely infested plants can be recognized by speckling and bronzing of the leaves and the presence of webbing. However, it is important to detect infestations before they reach this stage by examining the leaves, with a hand lens or under a microscope, to reveal the mites. Some sampling schemes have been developed that use the presence or absence of mites on a sample of leaves, to reduce the time spent counting (Raworth, 1986; Butcher et al., 1987).
Prevention and Control
Due to the variable regulations around (de)registration of pesticides, your national list of registered pesticides or relevant authority should be consulted to determine which products are legally allowed for use in your country when considering chemical control. Pesticides should always be used in a lawful manner, consistent with the product's label.
Biological Control
T. urticae has been the subject of some of the most successful examples of biological control. The predator used most often has been the phytoseiid mite Phytoseiulus persimilis. This species was first used in glasshouses, on various crops, in the 1960s (for example, Hussey et al., 1965), and since then has been used successfully on a wide variety of crops in a range of protected and unprotected environments. Several biological control companies package this predator for distribution on to plants by growers. Suitable release rates and timings vary with the crop. In areas where the mite has been established, augmentative releases are required to maintain control.
T. urticae has been the subject of some of the most successful examples of biological control. The predator used most often has been the phytoseiid mite Phytoseiulus persimilis. This species was first used in glasshouses, on various crops, in the 1960s (for example, Hussey et al., 1965), and since then has been used successfully on a wide variety of crops in a range of protected and unprotected environments. Several biological control companies package this predator for distribution on to plants by growers. Suitable release rates and timings vary with the crop. In areas where the mite has been established, augmentative releases are required to maintain control.
However, P. persimilis is active only under a limited range of conditions (Gorski and Eajfer, 2003), and so other species of phytoseiid mite have also been used against T. urticae. For example, Amblyseius idaeus and Phytoseiulus macropilis have been used on strawberry and cucumber in Brazil (Watanabe et al., 1994). Metwally et al. (2005) investigated life table and prey consumption of the predatory mite Neoseiulus cynodactylon, and concluded that T. urticae was a profitable prey species of this phytoseiid as a facultative predator.
Predators from other insect families have also shown promise as biocontrol agents against T. urticae. For example, the chrysopid Mallada basalis has been used on strawberry in Taiwan (Tzeng and Kao, 1996). Yanagita et al. (2014) reported that the predatory thrip Scolothrips takahashii could be used as an effective control agent against T. urticae in integrated pest management programmes for strawberry plug plants. Other potential predatory biocontrol agents include Orius minutus (Fathi, 2013), Coccinellla septempunctata (Sirvi and Singh, 2014), Stethorus gilvifrons (Ahmad et al., 2010) and Stethorus punctillum (Gorski and Eajfer, 2003).
Neoseiulus californicus has shown promise as an agent in conservation biological control of T. urticae; the natural control of the mite in strawberries was used as the basis for developing an integrated management plan, using acaricide only when necessary (Greco et al., 2011).
Shivaprakash et al. (2004) reported on the natural occurrence of the entomopathogenic fungus Beauveria bassiana on T. urticae in an okra plot grown without the use of chemicals in Bangalore, Karnataka, India. Laboratory tests using entomopathogens against T. urticae have also been carried out (e.g. Simova and Draganova, 2003; Chandler et al., 2005).
Host-Plant Resistance
Research to find sources of resistance to T. urticae has been carried out on a variety of crops, including Impatiens (Al-Abbasi and Weigle, 1982), soyabean (Mohammad and Rodriguez, 1985), Pelargonium (Chang et al., 1972), cucumber (de Ponti, 1980), Vigna angularis (Aguilar et al., 1996), strawberry (Shanks and Moore, 1995; Easterbrook and Simpson, 1998; Olbricht et al., 2014), watermelon (Lopez et al., 2005; El-Saiedy et al., 2011), maize (Mead et al., 2010), tomato (e.g. Saeidi and Mallik, 2012) and citrus (Agut et al., 2014). Several studies have found differences in susceptibility to the mite between different cultivars or selections. However, the resistance may be polygenic in most cases (Easterbrook and Simpson, 1998), and so is difficult to exploit by plant breeders. Even partial resistance is potentially useful in IPM programmes, however, as it slows the rate of population increase of the spider mite, and so makes it easier for predators to gain control.
Shivaprakash et al. (2004) reported on the natural occurrence of the entomopathogenic fungus Beauveria bassiana on T. urticae in an okra plot grown without the use of chemicals in Bangalore, Karnataka, India. Laboratory tests using entomopathogens against T. urticae have also been carried out (e.g. Simova and Draganova, 2003; Chandler et al., 2005).
Host-Plant Resistance
Research to find sources of resistance to T. urticae has been carried out on a variety of crops, including Impatiens (Al-Abbasi and Weigle, 1982), soyabean (Mohammad and Rodriguez, 1985), Pelargonium (Chang et al., 1972), cucumber (de Ponti, 1980), Vigna angularis (Aguilar et al., 1996), strawberry (Shanks and Moore, 1995; Easterbrook and Simpson, 1998; Olbricht et al., 2014), watermelon (Lopez et al., 2005; El-Saiedy et al., 2011), maize (Mead et al., 2010), tomato (e.g. Saeidi and Mallik, 2012) and citrus (Agut et al., 2014). Several studies have found differences in susceptibility to the mite between different cultivars or selections. However, the resistance may be polygenic in most cases (Easterbrook and Simpson, 1998), and so is difficult to exploit by plant breeders. Even partial resistance is potentially useful in IPM programmes, however, as it slows the rate of population increase of the spider mite, and so makes it easier for predators to gain control.
Mechanisms of host-plant resistance to T. urticae have been attributed to flavonoid pathways in citrus (Agut et al., 2014), leaf trichomes on Fragaria (Olbricht et al., 2014) (shown to entrap mites on tomato [Saeidi and Mallik, 2012]), increased peroxidase and polyphenol oxidase activity in melon (Shoorooei et al., 2013), antibiosis and antixenosis in bean (Kamelmanesh et al., 2010), phytochemical compounds in watermelon, where El-Saiedy et al. (2011) reported a negative relationship between mite infestation and tannins, and nitrogen and protein content in maize leaves (Mead et al., 2010).
Chemical Control
T. urticae is very difficult to control with acaricides because most populations developed resistance to chemical groups after a few years of use (Cranham and Helle, 1985). In some cases, cross-resistance to other chemical groups has also developed. For example, resistance to the ovicide clofentezine developed quite rapidly, and cross-resistance to hexythiazox also occurred (Thwaite, 1991). Al-Jboory et al. (2004) reported that a bromopropylate-resistant strain (R) of T. urticae showed strong positive cross-resistance towards dicofol and a mixture of dicofol and tetradifon, moderate positive cross-resistance towards amitraz, and low negative cross-resistance towards chlorpyrifos. No cross-resistance was observed towards abamectin and dinobuton.
Later, control often relied on acaricides from a group that act as inhibitors of mitochondrial respiration in the mite (METIs), such as pyridaben, fenpyroximate, fenazaquin and tebufenpyrad. However, resistance was detected in a relatively short space of time, leading to decreased susceptibility to all the compounds in this group (Bylemans and Meurrens, 1997). This illustrates the importance of anti-resistance strategies, involving restricted acaricide use and rotation of acaricides from different chemical groups, such as that proposed for fruit crops by the Insecticide Resistance Action Committee (IRAC) (Wege and Leonard, 1994).
Increased resistance to acaricides has led to research into alternative sources for control, such as fatty acid derivatives (Silva-Flores et al., 2005), sugar esters (Puterka et al., 2003), plant extracts, including essential oils (e.g. Kawka and Tomczyk, 2002; Mateeva et al., 2003; Aslan et al., 2004, 2005; Hou et al., 2004; Kawka, 2004), such as Elettaria cardamomum (Fatemikia et al., 2014), and botanical insecticides derived from the neem tree (Azadirachta indica) (Pavela, 2003). Of various plant extracts tested for acaricidal activity against T. urticae in Plovdiv, Bulgaria, Mateeva et al. (2003) reported that thornapple (Datura stramonium), wormwood (Artemisia absinthium) and basil (Ocimum basilicum) were toxic to the active stages of this pest. It was stated that extracts of these species could be used to control T. urticae on rose in urban areas. Saber (2004) reported that ethanol extracts of sand wormwood (Artemisia monosperma) were least effective against females of T. urticae compared to petroleum ether, chloroform or ethyl acetate. The acaricidal activity of Australian Lamiaceae extracts has also been tested against T. urticae with varying results (Rasikari et al., 2005). Extracts from the subfamilies Ajugoideae, Scutellarioideae, Chloanthoideae, Viticoideae and Nepetoideae showed acaricidal activity, and 14 species of Plectranthus showed moderate to high contact toxicity against T. urticae. Methanol extracts of Cinnamomum species (family Lauraceae) are potential acaricides (Reddy et al., 2014).
Commercially available Bionatrol (specified emulsion nano-particle soyabean oil) was shown to reduce populations of T. urticae, aphids (Aphis gossypii) and whiteflies (Trialeurodes vaporariorum) on greenhouse-grown English cucumber (Cucumis subsp. kasa) by 88-95% (Lee et al., 2005).
Integrated Pest Management
Management of T. urticae forms an integral part of IPM programmes for many crops. It is important that pesticides used for other pests and diseases are chosen so that they cause minimal disruption to naturally occurring predators or biocontrol agents such as Phytoseiulus persimilis. Also, control agents applied against the same pest must also be chosen carefully so that they do not disrupt each other. Thus, even though P. persimilis and B. bassiana have been shown to be effective in controlling T. urticae, when applied together, an increase in handling time by P. persimilis was reported, leading to a decrease in the rate of feeding by the predatory mite (Seiedy et al., 2012).
It may sometimes be necessary to use a selective acaricide to reduce spider mite numbers and maintain a suitable pest/predator ratio. For example, a selective acaricide may be needed to reduce a large overwintered population of T. urticae in the spring, before a release of P. persimilis later in the year (Easterbrook, 1992).
IPM programmes should minimize the use of acaricides, to delay the onset of resistance and prolong their effective life, but even programmes that do not heavily rely on pesticide use need to be cautious when employing different control strategies. For example, hot-water treatment on strawberry discs has been shown to control T. urticae (Gotoh et al., 2013); however, it was suggested by the authors that the natural enemy, Neoseiulus californicus would have to be replaced following treatment due to its sensitivity to hot water.
Chemical Control
T. urticae is very difficult to control with acaricides because most populations developed resistance to chemical groups after a few years of use (Cranham and Helle, 1985). In some cases, cross-resistance to other chemical groups has also developed. For example, resistance to the ovicide clofentezine developed quite rapidly, and cross-resistance to hexythiazox also occurred (Thwaite, 1991). Al-Jboory et al. (2004) reported that a bromopropylate-resistant strain (R) of T. urticae showed strong positive cross-resistance towards dicofol and a mixture of dicofol and tetradifon, moderate positive cross-resistance towards amitraz, and low negative cross-resistance towards chlorpyrifos. No cross-resistance was observed towards abamectin and dinobuton.
Later, control often relied on acaricides from a group that act as inhibitors of mitochondrial respiration in the mite (METIs), such as pyridaben, fenpyroximate, fenazaquin and tebufenpyrad. However, resistance was detected in a relatively short space of time, leading to decreased susceptibility to all the compounds in this group (Bylemans and Meurrens, 1997). This illustrates the importance of anti-resistance strategies, involving restricted acaricide use and rotation of acaricides from different chemical groups, such as that proposed for fruit crops by the Insecticide Resistance Action Committee (IRAC) (Wege and Leonard, 1994).
Increased resistance to acaricides has led to research into alternative sources for control, such as fatty acid derivatives (Silva-Flores et al., 2005), sugar esters (Puterka et al., 2003), plant extracts, including essential oils (e.g. Kawka and Tomczyk, 2002; Mateeva et al., 2003; Aslan et al., 2004, 2005; Hou et al., 2004; Kawka, 2004), such as Elettaria cardamomum (Fatemikia et al., 2014), and botanical insecticides derived from the neem tree (Azadirachta indica) (Pavela, 2003). Of various plant extracts tested for acaricidal activity against T. urticae in Plovdiv, Bulgaria, Mateeva et al. (2003) reported that thornapple (Datura stramonium), wormwood (Artemisia absinthium) and basil (Ocimum basilicum) were toxic to the active stages of this pest. It was stated that extracts of these species could be used to control T. urticae on rose in urban areas. Saber (2004) reported that ethanol extracts of sand wormwood (Artemisia monosperma) were least effective against females of T. urticae compared to petroleum ether, chloroform or ethyl acetate. The acaricidal activity of Australian Lamiaceae extracts has also been tested against T. urticae with varying results (Rasikari et al., 2005). Extracts from the subfamilies Ajugoideae, Scutellarioideae, Chloanthoideae, Viticoideae and Nepetoideae showed acaricidal activity, and 14 species of Plectranthus showed moderate to high contact toxicity against T. urticae. Methanol extracts of Cinnamomum species (family Lauraceae) are potential acaricides (Reddy et al., 2014).
Commercially available Bionatrol (specified emulsion nano-particle soyabean oil) was shown to reduce populations of T. urticae, aphids (Aphis gossypii) and whiteflies (Trialeurodes vaporariorum) on greenhouse-grown English cucumber (Cucumis subsp. kasa) by 88-95% (Lee et al., 2005).
Integrated Pest Management
Management of T. urticae forms an integral part of IPM programmes for many crops. It is important that pesticides used for other pests and diseases are chosen so that they cause minimal disruption to naturally occurring predators or biocontrol agents such as Phytoseiulus persimilis. Also, control agents applied against the same pest must also be chosen carefully so that they do not disrupt each other. Thus, even though P. persimilis and B. bassiana have been shown to be effective in controlling T. urticae, when applied together, an increase in handling time by P. persimilis was reported, leading to a decrease in the rate of feeding by the predatory mite (Seiedy et al., 2012).
It may sometimes be necessary to use a selective acaricide to reduce spider mite numbers and maintain a suitable pest/predator ratio. For example, a selective acaricide may be needed to reduce a large overwintered population of T. urticae in the spring, before a release of P. persimilis later in the year (Easterbrook, 1992).
IPM programmes should minimize the use of acaricides, to delay the onset of resistance and prolong their effective life, but even programmes that do not heavily rely on pesticide use need to be cautious when employing different control strategies. For example, hot-water treatment on strawberry discs has been shown to control T. urticae (Gotoh et al., 2013); however, it was suggested by the authors that the natural enemy, Neoseiulus californicus would have to be replaced following treatment due to its sensitivity to hot water.
Supplements, such as fertilizers, used in the growing environment must also work synergistically in an IPM programme and several authors have investigated the effect of fertilizer application on pests, such as T. urticae. For example, Zhang and Xiang (2007) reported an increase in the number of T. urticae (and Aphis gossypii) with an increase in organic fertilizer application; however, cucumber yield also increased. In contrast, other studies have shown that application of nitrogen or phosphorous fertilizers had no effect on numbers or activity of T. urticae (e.g. Shabalta et al., 1992, on soyabeans).
Other
In 2006, Donohue et al. reported on atmospheric pressure plasma discharge as (APPD) a non-chemical method of control for insect pests including T. urticae. APPD is used to sterilize medical equipment and was shown to kill T. urticae. However, further reports of its application to control the mite in the scientific literature could not be found after publication of Donahue et al.’s paper in 2006.
Links to Websites
Name | URL | Comment |
---|---|---|
GISD/IASPMR: Invasive Alien Species Pathway Management Resource and DAISIE European Invasive Alien Species Gateway | https://doi.org/10.5061/dryad.m93f6 | Data source for updated system data added to species habitat list. |
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