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23 November 2009

Raoiella indica (red palm mite)

Datasheet Types: Pest, Natural enemy, Invasive species

Abstract

This datasheet on Raoiella indica covers Identity, Overview, Distribution, Dispersal, Hosts/Species Affected, Diagnosis, Biology & Ecology, Environmental Requirements, Natural Enemies, Impacts, Prevention/Control, Further Information.

Identity

Preferred Scientific Name
Raoiella indica Hirst (1924)
Preferred Common Name
red palm mite
International Common Names
English
coconut red mite
frond crimson mite
leaflet false spider mite
red date palm mite
scarlet mite
EPPO code
RAOIIN (Raoiella indica)

Pictures

The red palm mite (Raoiella indica), an invasive species in the Caribbean, may threaten several important palms found in the southern USA. (Original magnified approx. 300x.) Photo by Eric Erbe; Digital colourization by Chris Pooley.
Adult mite
The red palm mite (Raoiella indica), an invasive species in the Caribbean, may threaten several important palms found in the southern USA. (Original magnified approx. 300x.) Photo by Eric Erbe; Digital colourization by Chris Pooley.
USDA-ARS
Colony of red palm mites (Raoiella indica) on coconut leaflet, from India.
Colony of mites
Colony of red palm mites (Raoiella indica) on coconut leaflet, from India.
Bryony Taylor
Close-up of a colony of red palm mites (Raoiella indica) on coconut leaflet, from India.
Colony of mites
Close-up of a colony of red palm mites (Raoiella indica) on coconut leaflet, from India.
Bryony Taylor

Summary of Invasiveness

R. indica was first described in India in 1924 (Hirst) and has since been reported in several Old World countries. The species became of recent significance in 2004 when it was first reported in the Caribbean (Flechtmann and Étienne, 2004). Since then the mite has successfully spread throughout the islands of the Caribbean and has expanded its range into southern Florida (USDA-APHIS, 2007), South America (northern Venezuela, Vásquez et al., 2008; Brazil, Navia et al., 2010; Colombia, Carrillo et al., 2011) and Mexico (Estrada-Venegas et al., 2010). The mite has been reported on a wide range of palm hosts of the family Arecaceae and apparent new associations with members of the order Zingiberales, including the families Musaceae, Heliconiaceae, Zingiberaceae and Strelitziaceae have been reported. The success of the mite in the invasive range may be attributed to its ability to colonize many different host plant species, its apparent lack of co-evolved natural enemies in its new habitat and its rapid dispersal in its new range.

Taxonomic Tree

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Notes on Taxonomy and Nomenclature

R. indica was first described in the district of Coimbatore (India) by Hirst in 1924 on coconut leaflets [Cocos nucifera]. A comprehensive taxonomic review of the genus and species was carried out by Mesa et al. (2009), which lists all suspected junior synonyms of R. indica, including Raoiella camur (Chaudhri and Akbar), Raoiella empedos (Chaudhri and Akbar), Raoiella obelias (Hasan and Akbar), Raoiella pandanae (Mohanasundaram), Raoiella phoenica (Meyer) and Raoiella rahii (Akbar and Chaudhri). The review also highlighted synonymy with Rarosiella cocosae found on coconut in the Philippines. The review by Mesa et al. (2009) also lists the redescriptions by several authors.

Description

R. indica is a small red mite, which is characterized by the presence of long spatulate setae on its dorsum, often with a drop of liquid on the end. The body shape is oval and flattened and the male can be distinguished from the female by the distinct triangular abdomen (Kane and Ochoa, 2006; Welbourn, 2006). All stages of the mite are red; however, the adult females often have darkened areas on their abdomen. There are five distinct life stages: egg, larva, protonymph, deutonymph and adult. The original description by Hirst (1924) stated that the length of the adult female (including palpi) is 0.29-0.30 mm and the male is 0.21 mm. Redescriptions have quoted the length of the adult female as between 267-300 µm and the width between 178 and 215 µm (Hirst, 1924; Taher Sayed, 1942; Sadana, 1997). The eggs are approximately 0.117 mm long, red/orange and smooth and shiny in appearance (Moutia, 1958) and are found attached to the leaf by a stipe that is roughly twice as long as the egg (Kane and Ochoa, 2006). Zaher et al. (1969) stated that the length of the larva was 125 µm long and 93 µm wide, the protonymph 210 µm long and 159 µm wide, and the deutonymph 272 µm long and 179 µm wide. Welbourn (2006) stated that the dorsal and lateral setae of nymphs are distinctly shorter than those of the adult, and dorsal setae are not set in tubercules (projecting setal bases).

Distribution

The majority of literature on R. indica, previous to its introduction into the Caribbean, was published in India, where the mite was first described (Hirst, 1924). R. indica is a well-established pest throughout palm growing areas of India and reported mainly on Cocos nucifera (Hirst, 1924) and Areca catechu (Daniel, 1979; Yadavbabu and Manjunatha 2007). Outside India, older literature reported R. indica in Egypt, UAR, (Taher Sayed, 1942; Zaher et al., 1969), Sudan (Couland, 1938, cited in Pritchard and Baker, 1958) Mauritius (Moutia, 1958) and Saudi Arabia (Soliman and Al-Yousif, 1979). More recently, further countries throughout Asia have been reported (see Distribution table). However, it is unknown how long the mite has been present in these countries. Dowling et al. (2010) have carried out a detailed molecular analysis with the aim to track the phylogenetic history of R. indica. They found the most primitive haplotypes of R. indica were found in the Middle East and these appear to have spread throughout the Old World and eventually to the Caribbean, indicating that perhaps the mite has been present in the Asian region for some time. R. indica was first reported in the New World in Martinique (Flechtmann and Étienne, 2004) and has since spread rapidly throughout the Caribbean archipelago into Southern Florida (Smith and Dixon, 2008) and South America (Vásquez et al., 2008) and has now spread further into Mexico (Estrada-Venegas et al., 2010), Brazil (Navia et al., 2010) and Colombia (Carrillo, 2011). It has become of interest as an invasive in these countries due to the high population numbers and diverse range of host plants the mite has been recorded on.

Distribution Map

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Distribution Table

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History of Introduction and Spread

Although the exact area of origin is unknown for R. indica, the mite is well established in the reported areas in Asia and Africa. Current theories hypothesize that the mite has gradually spread west via natural dispersal and on infested material transported via trading routes. It is believed that the pest was first introduced into the Caribbean via shipping lanes from Africa (most probably Réunion), and since its introduction, the mite has spread widely through the islands of the Caribbean spreading northwards into Florida and southwards into Venezuela. Welbourn (2006) stated that the spread of the mite throughout the islands of the Caribbean may have been facilitated by the transport of infested plants and handicrafts made from palm material. Welbourn also stated that the natural dispersal method of the mite on wind currents may also be aided by tropical storms or hurricanes.

Risk of Introduction

Authorities in the USA and Europe have carried out a risk assessment to identify the potential threat posed by R. indica and to model its future spread throughout palm-growing regions. A USDA risk assessment (Borchert, 2007) indicates that the spread of the mite may be limited by climatic factors, therefore limiting it to tropical and sub-tropical regions. Recommendations from the report were that movement of infested material should be restricted and not distributed to uninfested areas. This includes the transport of palm handicrafts between islands in the Caribbean. The USDA-APHIS and the Florida Department of Agriculture and Consumer Services have carried out surveys throughout Florida and have set up sentinel sites to monitor the spread of R. indica (Smith and Dixon, 2008). Literature was also produced in 2007 outlining the symptoms of infestation and a description of R. indica. In Europe, EPPO has produced a report citing that more data would be required on infestations in Israel and Egypt, and that currently there are no indications of the mite disseminating or causing high levels of damage. Vásquez et al.(2008) stated that quarantine measures have been implemented by SASA to prevent the further spread of R. indica to other parts of Venezuela; however, the mite has since been reported in Brazil (Navia et al., 2010) and Mexico (Estrada-Venegas et al., 2010).

Means of Movement and Dispersal

Natural Dispersal (Non-Biotic)

Welbourn (2006) stated that wind dispersal was the most likely method of natural dispersal, and Hoy et al. (2006) stated that the presence of mites on older palms on islands adjacent to Martinique within a year of introduction, indicate that wind dispersal was the primary dispersal method.

Accidental Introduction

It is believed that R. indica was first accidentally introduced to the Caribbean via infested material imported via shipping lanes from the Old World. No research to date has identified whether this was a single or multiple introduction. Accidental spread to new areas is via the introduction of infested plants or plant material or via palm handicrafts infested with mites or eggs (Welbourn, 2006), which are common tourist souvenirs and readily transported. Quarantine measures are in place to prevent the transfer of mites via palm handicrafts, cut flower and leaf arrangements from host plants and coconut seed.

Pathway Causes

Pathway causeNotesLong distanceLocalReferences
Cut flower trade (pathway cause)Phytosanitary certificates required when transported between Caribbean islands Yes 
Garden waste disposal (pathway cause)Investigated as one of the pathways in Florida Yes 
Nursery trade (pathway cause)PPQ Plant Inspection required for untreated shipments in N. Atlantic/N.Pacific ports, USAYes  
Ornamental purposes (pathway cause)Dept. of Homeland Security Custom and Border Control found palm handicrafts to carry eggs and adults Yes 
Seed trade (pathway cause)Coconut seed found to carry R. indica when transported between regionsYesYes 

Pathway Vectors

Pathway vectorNotesLong distanceLocalReferences
Consumables (pathway vector)On palm handicrafts between islands in the Caribbean Yes 
Mulch, straw, baskets and sod (pathway vector)On palm handicrafts between islands in the Caribbean Yes 
Plants or parts of plants (pathway vector)On palm handicrafts between islands in the Caribbean & on cut flower & host plant leaf arrangementsYesYes 
Wind (pathway vector)Thought to aid dispersal locally or between islands in the CaribbeanYesYes

Plant Trade

Plant parts liable to carry the pest in trade/transportPest stagesBorne internallyBorne externallyVisibility of pest or symptoms
Fruits (inc. pods)  YesPest or symptoms usually visible to the naked eye
Leaves
arthropods/eggs
arthropods/larvae
arthropods/nymphs
arthropods/adults
 YesPest or symptoms usually visible to the naked eye
Seedlings/Micropropagated plants
arthropods/larvae
arthropods/nymphs
arthropods/adults
 YesPest or symptoms usually visible to the naked eye
Stems (above ground)/Shoots/Trunks/Branches
arthropods/larvae
arthropods/nymphs
arthropods/adults
 YesPest or symptoms usually visible to the naked eye
Plant parts not known to carry the pest in trade/transport
Bark
Bulbs/Tubers/Corms/Rhizomes
Flowers/Inflorescences/Cones/Calyx
Growing medium accompanying plants
Roots
True seeds (inc. grain)
Wood

Hosts/Species Affected

The Host Plant list in this datasheet is compiled from Cocco and Hoy (2009) and Goldsmith (2009). It is noted in Cocco and Hoy (2009) that there is often no information on the life stage found on the host plant and therefore the list reflects which host plant species R. indica has been recorded on. Population levels on each of the host plants have not been recorded/published to date; therefore data on the ability of R. indica to complete a full lifecycle on each species is not available currently. In Cocco and Hoy (2009), laboratory assays to ascertain this on several varieties of Musa sp. were carried out and it was found that populations were more easily established on Cocos nucifera. However, reports from the eastern Caribbean confirm that multi-generational colonies do occur in the field on certain varieties of Musa sp. including Dwarf Cavendish, Giant Cavendish, Robusta and Williams, and for plantain varieties: Apem; Cents Livre; Ordinary; Dwarf French; and Horn. The difference between laboratory and field observations warrants further investigation.

Host Plants and Other Plants Affected

HostFamilyHost statusReferences
Acanthophoenix rubraArecaceaeUnknown
Acer (maples)AceraceaeOther 
Acoelorrhaphe wrightii (Everglades palm)ArecaceaeWild host 
Adonidia arecinaArecaceaeWild host 
Adonidia merrillii (Christmas palm)ArecaceaeWild host
Aiphanes Unknown
Aiphanes minimaArecaceaeWild host 
Alpinia purpurata (red ginger)ZingiberaceaeWild host
Alpinia vittataZingiberaceaeWild host 
Alpinia zerumbet (shell ginger)ZingiberaceaeWild host 
Archontophoenix alexandraeArecaceaeWild host 
ArecaArecaceaeUnknown
Areca catechu (betelnut palm)ArecaceaeMain
Arenga australasica Unknown
Arenga engleriArecaceaeUnknown
Arenga microcarpa Unknown
Arenga pinnata (sugar palm)ArecaceaeWild host 
Arenga tremula Unknown
Arenga undulatifolia Unknown
Bactris Unknown
Bactris plumerianaArecaceaeWild host 
Beccariophoenix madagascariensisArecaceaeWild host 
Bismarckia nobilisArecaceaeWild host 
Brahea armataArecaceaeUnknown
Butia capitata (coquinho-azedo)ArecaceaeWild host 
Calathea arundinacea (variegated calatea)MarantaceaeWild host 
Calathea lutea (calathea)MarantaceaeWild host 
Caryota mitisArecaceaeWild host
Caryota urens (fishtail palm)ArecaceaeUnknown
ChamaedoreaArecaceaeWild host
Coccothrinax argentataArecaceaeWild host 
Coccothrinax miraguamaArecaceaeWild host 
Cocos Unknown
Cocos nucifera (coconut)ArecaceaeMain
Corypha umbraculiferaArecaceaeWild host 
Curcuma longa (turmeric)ZingiberaceaeWild host 
CycasCycadaceaeOther 
Cyrtostachys rendaArecaceaeWild host 
Dictyosperma albumArecaceaeMain 
Dypsis decaryi (triangle palm)ArecaceaeWild host 
Dypsis lutescens (yellow butterfly palm)ArecaceaeWild host
Elaeis guineensis (African oil palm)ArecaceaeWild host
Elaeodendron transvaalenseSalaciaWild host 
Etlingera elatior (torch ginger)ZingiberaceaeWild host
Eucalyptus deglupta (rainbow gum)MyrtaceaeWild host 
Eugenia uniflora (Surinam cherry)LithomyrtusWild host 
Gaussia princeps Unknown
HeliconiaHeliconiaceaeMain
Heliconia bihai (macaw flower)HeliconiaceaeWild host 
Heliconia caribaeaHeliconiaceaeWild host 
Heliconia caribaea x bihaiHeliconiaceaeWild host 
Heliconia chartaceaHeliconiaceaeWild host 
Heliconia episcopalisHeliconiaceaeWild host 
Heliconia latispathaHeliconiaceaeWild host 
Heliconia marginataHeliconiaceaeWild host 
Heliconia psittacorumHeliconiaceaeWild host
Heliconia rostrataHeliconiaceaeWild host 
Heterospathe elata var. palauensis Unknown
Heterospathe elmeri Unknown
Heterospathe intermedia Unknown
Heterospathe negrosensis Unknown
Hyophorbe indicaArecaceaeUnknown
Latania lontaroidesArecaceaeWild host 
Licuala grandisArecaceaeWild host 
Licuala spinosaArecaceaeWild host 
Livistona australisArecaceaeUnknown
Livistona carinensisArecaceaeUnknown
Livistona chinensis (Chinese fan palm)ArecaceaeWild host
Livistona fulvaArecaceaeUnknown
Livistona mariaeArecaceaeUnknown
Livistona mariae subsp. rigidaArecaceaeUnknown
Livistona muelleri Unknown
Microcycas calocomaZamiaceaeOther 
Musa (banana)MusaceaeMain
Musa acuminata (wild banana)MusaceaeMain
Musa balbisianaMusaceaeMain
Musa corniculataMusaceaeWild host 
Musa ornata (flowering banana)MusaceaeWild host 
Musa troglodytarumMusaceaeUnknown
Musa uranoscoposMusaceaeWild host 
Musa x paradisiaca (plantain)MusaceaeUnknown
Neoveitchia storckii Unknown
Ocimum basilicum (basil)LamiaceaeWild host 
Pandanus utilis (common screw pine)PandanaceaeWild host 
Phaseolus (beans)FabaceaeWild host 
Phoenix (date palm)ArecaceaeUnknown
Phoenix canariensis (Canary Island date palm)ArecaceaeWild host 
Phoenix dactylifera (date-palm)ArecaceaeMain
Phoenix reclinata (senegal date palm)ArecaceaeWild host
Phoenix roebeleniiArecaceaeWild host
Phoenix rupicolaArecaceaeWild host 
Pritchardia pacificaArecaceaeWild host 
Pritchardia vuylstekeanaArecaceaeWild host 
Pseudophoenix viniferaArecaceaeWild host 
Ptychosperma elegans (solitaire palm)ArecaceaeWild host 
Ptychosperma macarthurii (Macarthur palm)ArecaceaeWild host 
Ravenala madagascariensisStrelitziaceaeWild host 
Renealmia alpiniaZingiberaceaeWild host 
Renealmia aurantiferaZingiberaceaeWild host 
Rhapis excelsaArecaceaeWild host
RoystoneaArecaceaeUnknown
Roystonea borinquenaArecaceaeWild host 
Roystonea oleracea (Caribbean royal palm)ArecaceaeUnknown
Roystonea regia (cuban royal palm)ArecaceaeUnknown
Sabal blackburnianaArecaceaeWild host 
Sabal mauritiiformisArecaceaeWild host
Saribus rotundifoliusArecaceaeUnknown
Schippia concolorArecaceaeWild host 
Schippia concolorArecaceaeWild host 
Strelitzia reginae (Queens bird-of-paradise)StrelitziaceaeWild host 
Syagrus romanzoffiana (queen palm)ArecaceaeUnknown
Syagrus romanzoffianum (queen palm)ArecaceaeWild host 
Syagrus schizophyllaArecaceaeWild host 
Thrinax radiataArecaceaeWild host 
Veitchia arecinaArecaceaeWild host 
Washingtonia filifera (desert fanpalm)ArecaceaeWild host 
Washingtonia robusta (mexican washington-palm)ArecaceaeWild host 
Wodyetia bifurcata (foxtail palm)ArecaceaeWild host
Zingiber (ginger)ZingiberaceaeWild host 

Growth Stages

Flowering stage
Fruiting stage
Seedling stage
Vegetative growing stage

Symptoms

The presence of colonies of R. indica on leaflets or leaves initially causes localized yellowing, which may spread to form larger chlorotic patches. This can result in yellowing of the leaflet and potentially necrosis. In general, lower leaflets of palms are more severely affected and may appear yellow in colour. Infestations on bananas [Musa paradisiaca] and plantain often cause yellowing along the margins of the leaf (USDA-APHIS, 2007). On coconuts [Cocos nucifera] in the Caribbean it has been reported that flowers and small nuts may abort following the yellowing of the leaflets. Young seedlings appear to be most affected and the fronds most affected by the mite are generally in the lower third of the canopy (Hoy et al., 2006). Peña et al. (2009) stated that heavy infestations may result in death of young plants.

List of Symptoms/Signs

Symptom or signLife stagesSign or diagnosisDisease stage
Plants/Fruit/premature drop   
Plants/Leaves/abnormal colours   
Plants/Leaves/external feeding   
Plants/Leaves/necrotic areas   
Plants/Leaves/yellowed or dead   
Plants/Whole plant/discoloration   
Plants/Whole plant/external feeding   

Similarities to Other Species/Conditions

R. indica may be distinguished from other red mites on hosts as it is found in colonies that lack the webbing associated with spider mites (Tetranychidae). Other distinguishing features are the presence of white cast skins among the colony, red legs, long dorsal setae (often with droplets of liquid on) and flattened bodies (Kane and Ochoa, 2006; Welbourn, 2006). Couplets may be observed between the male and females in most colonies. Couplets are formed between the male and the female deutonymph as the female moults to adult and R. indica is the only species of Tetranychoid mite to display this behaviour (Welbourn, 2006). Damage symptoms can be confused with nutrient deficiency or the disease, Lethal Yellowing (USDA-APHIS, 2007). Zaher et al. (1969) stated that damage caused by R. indica could be distinguished from that caused by another leaflet infesting mite, Phyllotetranychus aegyptiacus, as R. indica causes ‘dark reddish blotches’ to appear on date palms [Phoenix dactylifera]; whereas the other species cause ‘dirty white’ patches.

Habitat

In literature originating from the Old World prior to the introduction of the mite to the Caribbean, the host plants reported were Cocos nucifera, Areca catechu, Phoenix dactylifera (date palms) and Dictyosperma album. Since the introduction into the Caribbean, the number of host plants reported has increased substantially, most notably bananas [Musa sp.], plantains (Musa sp.) and other members of the order Zingiberales. It is not known whether these plants are unreported hosts in the Old World, or whether the host range has expanded in the invasive range. There are several new associations reported on hosts believed to have origins in the New World.

Habitat List

CategorySub categoryHabitatPresenceStatus
TerrestrialTerrestrial – ManagedManaged forests, plantations and orchardsPresent, no further detailsHarmful (pest or invasive)

Biology and Ecology

Genetics

R. indica is a haplo-diploid bisexual species confirmed by the presence of two classes of eggs; one class containing two chromosomes and one class containing four chromosomes (Helle et al., 1972). Little information is known about the genetic diversity of the species. Dowling et al. (2010) carried out a biogeographical study of R. indica and discovered that the most primitive haplotypes tended to be found in the Middle East.

Reproductive Biology

The life history of R. indica was described by Moutia (1958) and Zaher et al. (1969) on Cocos nucifera (coconut) and Phoenix dactylifera, respectively. The eggs are laid in groups, often near the midrib or depressions in the leaflet, and on hatching, the larvae emerge and start feeding on leaf tissue. The number of eggs laid varies from individual to individual; however, Moutia (1958) recorded that on average, 28.1 eggs were laid on leaf discs during the average adult female life span of 27 days. As the larvae and nymphs pass through each stage, they enter a quiescent stage for 36-48 hours, whereby they enter ecdysis and withdraw posteriorly from the exuviae (Zaher et al., 1969). The duration of each stage on coconut at 24.2°C in Mauritius was egg: 4-6 days; larva: 6-8 days; protonymph: 4-7 days; deutonymph: 4-5 days; however, the duration of stages increases with lower average temperatures (Moutia, 1958). Hoy et al. (2006) highlighted findings by Nageshachandra and ChannaBasavanna (1984), stating that both mated and unmated females lay eggs, with males emerging from the eggs laid by unmated females and the eggs from mated females emerging as female.

Physiology and Phenology

No studies to date (2010) have been carried out on this subject.

Nutrition

Studies on the nutritional requirements of R. indica have not been carried out; however, a study was conducted looking at the correlation of leaf nutrients to R. indica populations. Sarkar and Somchoudhury (1989b) investigated correlations of mite populations in association with crude protein, nitrogen, moisture, calcium and phosphorus content of coconut leaflets. They found that coconut varieties with higher levels of nitrogen and crude protein had higher population densities of the mite; no significant effect of calcium or phosphorus content was found in association with mite incidence. They reported that varieties of coconut with higher moisture content in leaflets were more susceptible to herbivory by R. indica; however, other reports suggest that poorly irrigated host plants are more susceptible to attack by the mite (Devasahayam and Nair, 1982).

Environmental Requirements

The exact range of tolerance of temperature is unknown; however, Sarkar and Somchoudhury (1989a) showed that as temperatures peak toward 40°C in West Bengal, populations of R. indica also peak. Yadavbabu and Manjunatha (2007) also reported that populations on Areca catechu were positively correlated to temperature, with highest average populations recorded alongside the highest maximum temperature at 39.9°C. Data consistently shows that populations build up in hot dry conditions and reduce with the onset of the monsoon in the Old World (Moutia, 1958; Daniel, 1979; Sarkar and Somchoudhury, 1989a; Sathiamma, 1996; Yadavbabu and Manjunatha, 2007). Yadavbabu and Manjunatha (2007) reported a negative correlation between mite populations and rainfall and humidity, and Moutia (1958) noted a decline in populations with the onset of heavy rain. Sarkar and Somchoudhury (1989a) found no relationship between rainfall and mite population size. A recent paper by Carillo et al. (2010) described the successful culture of R. indica at 30°C (±1°C), 60% (± 5%) RH and a 12:12 L:D photophase on the abaxial leaflet of Malayan Dwarf coconut palms [Cocos nucifera].

Climate

Climate typeDescriptionPreferred or toleratedRemarks
Af - Tropical rainforest climate> 60mm precipitation per monthPreferred 
Am - Tropical monsoon climateTropical monsoon climate ( < 60mm precipitation driest month but > (100 - [total annual precipitation(mm}/25]))Preferred 
As - Tropical savanna climate with dry summer< 60mm precipitation driest month (in summer) and < (100 - [total annual precipitation{mm}/25])Preferred 
Aw - Tropical wet and dry savanna climate< 60mm precipitation driest month (in winter) and < (100 - [total annual precipitation{mm}/25])Preferred 
BS - Steppe climate> 430mm and < 860mm annual precipitationPreferred 
BW - Desert climate< 430mm annual precipitationPreferred 

Latitude/Altitude Ranges

Latitude North (°N)Latitude South (°S)Altitude lower (m)Altitude upper (m)
4025  

Natural enemy of

This content is currently unavailable.

Notes on Natural Enemies

Several studies have been conducted to identify natural enemies of R. indica. As a mite, all the natural enemies recorded have been predators including phytoseiid mites, Coccinellids, Staphylinids, Neuropterans, Dipterans and Thysanopterans. Several studies have been carried out in the field to observe the levels of natural enemies in comparison to those of R. indica, as well as laboratory studies to assess the voracity of the predators.
Moutia (1958) carried out a comprehensive survey of natural enemies in Mauritius and recorded that Typhlodromus caudatus was an active predator of R. indica during the study. The mite reportedly predated on the egg stage, feeding on up to five to six mites successively and up to a maximum of 16.9 in a day. The predator was found in high abundance on coconut [Cocos nucifera] leaflets.
Somchoudhury and Sarkar (1989) carried out a study in West Bengal, India, and found the predominant predators to be a staphylinid beetle, Oligota sp. and two predatory mites, Phytoseius sp and Amblyseius sp. Oligota sp. and Phytoseius sp. showed a correlation in population growth with R. indica throughout the season. In Karanataka, India, the predatory mite, Amblyseius channabasavanni and the coccinellid, Stethorus keralicus have been reported to prey upon R. indica and biological studies have shown that S. keralicus can feed and reproduce solely on a diet of R. indica, completing development from egg to adult in 12-14 days, feeding on all stages of the mite (Daniel, 1976).
The most abundant predators of R. indica appear to be phytoseiid mites. A recent study by Taylor et al. (CABI, UK, paper in preparation 2011) in Kerala, India, found that by far the most abundant predators were phytoseiid mites (IDs underway 2009) and from the literature, the most widely reported genus of predator is Amblyseius. Daniel (1981, cited in Gupta, 2003) reported that A. channabasavanni, feeding on R. indica eggs, had a total development time of 84-113hrs (3.5-4.7 days) for adult females, consuming on average 26.5 eggs. Amblyseius largoensis has also frequently been reported in association with R. indica in countries such as Mauritius (MA Hoy, [address available from CABI], personal communication, 2009) and throughout the Caribbean and Florida (Hosein, 2008; Peña et al., 2009).
In Florida, a study has been carried out to assess the response of native natural enemies to the introduction of the mite. Several species have been shown to be associated with R. indica, but by far the most abundant predator was found to be A. largoensis, which accounted for 77.2% of total predators collected in a study by Peña et al. (2009) followed by Aleurodothrips fasciapennis. Subsequent laboratory studies by Carrillo et al. (2010) have shown that  A. largoensis can feed and reproduce solely on R. indica.

Natural enemies

Natural enemyTypeLife stagesSpecificityReferencesBiological control inBiological control on
Aleurodothrips fasciapennisPredator
Adults
Eggs
Nymphs
    
Amblyseius channabasavanniPredator    
Amblyseius largoensisPredator
Adults
Eggs
Nymphs
   
Amblyseius longispinusPredator    
Amblyseius raoiellusPredator    
Armascirus taurusPredator     
Bdella distinctaPredator     
CeraechrysaPredator     
Chrysopa (aphid-lions)Predator    
ChrysoperlaPredator     
CunaxidaePredator     
Cybocephalus semiflavusPredator    
Evorinea indicaPredator     
FeltiellaPredator    
Jauravia sororPredator    
OligotaPredator    
PhytoseiusPredator    
Spilocaria bissellataPredator    
Stethorus keralicusPredator    
Stethorus parcepunctatusPredator    
Stethorus tetranychiPredator    
Stethorus utilisPredator     
Telsimia ephippigerPredator     
Typhlodromus caudatusPredator    

Impact Summary

CategoryImpact
Cultural/amenityNegative
Economic/livelihoodNegative
Environment (generally)Negative

Impact: Economic

Little empirical data has been gathered on the economic impact of the introduction of R. indica to the Caribbean, USA and South America. Peña et al. (2009) quoted that coconut [Cocos nucifera] growers have reported a 70% drop in coconut production since the introduction of the mite and FAO figures have shown a drop to date in coconut production from Caribbean countries since 2004, when the mite was first identified in the region. Empirical studies are required to confirm these figures/correlations; however, officials are concerned that this may lead to job losses and major socio-economic problems. In Florida, it was feared possible economical impacts could come from quarantine restrictions if R. indica was detected in palm nurseries. However, Bronson (2009) stated that R. indica population levels were lower than expected in Florida and quarantine would not to be enforced unless infestation levels were found to be high. Extra costs for implementing regulatory actions in Florida have been quoted to be as much as half a million US dollars extra per year for palm nursery producers (Peña et al., 2009).

Impact: Environmental

Impact on habitats

The amenity value of many ornamental plants and palms is severely affected by the yellowing that the mite causes.

Risk and Impact Factors

Invasiveness

Proved invasive outside its native range
Abundant in its native range
Is a habitat generalist
Tolerant of shade
Capable of securing and ingesting a wide range of food
Fast growing
Has high reproductive potential
Reproduces asexually

Impact outcomes

Host damage
Negatively impacts forestry
Reduced amenity values
Damages animal/plant products
Negatively impacts trade/international relations

Impact mechanisms

Rapid growth

Likelihood of entry/control

Highly likely to be transported internationally accidentally
Difficult to identify/detect as a commodity contaminant
Difficult to identify/detect in the field
Difficult/costly to control

Detection and Inspection

Colonies of R. indica are usually found on the underside of leaves/leaflets of the host plants. Colonies often contain mites of all stages as well as exuvial remains (white cast skins) and can have up to 300 individuals (Kane and Ochoa, 2006). Inspection of the underside of leaflets of host plants using a hand lens, or removal of material and inspection under a dissecting microscope can confirm the presence of mites (Hoy et al., 2006). Affected host plants will generally display symptoms under heavy infestations. Typical damage symptoms include localized yellowing of the leaf, which can spread into larger chlorotic patches. Heavy infestations may be found along the midrib of coconut leaflets and damage may progress from localized yellowing to necrosis (Rodríguez et al., 2007). Infestations on bananas [Musa paradisiaca] and plantain often cause yellowing along the margins of the leaf (USDA-APHIS, 2007). If there are heavy infestations, persons inspecting the host plant may find they pick up red on their fingers from the mites on the underside of leaves.
A diagnostic Lucid key to 20 species of Raoiella is available in Flat Mites of the World.

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.

Public Awareness

USDA have produced public awareness leaflets (USDA-APHIS, 2007) highlighting the signs and symptoms to look out for and which authorities to contact in the case of the presence of the mite. Red palm mite updates and guidelines are available at http://www.doacs.state.fl.us/pi/enpp/ento/red_palm_mite.html.

Movement Control

Quarantine measures are in place to restrict the movement of infested material. For example, the movement of palm handicrafts, cut flowers, etc, in the Caribbean. In Florida, there is no longer mandatory quarantine for infested palms; however, quarantine measures are enforced if population levels increase (Bronson, 2009). Host palms originating from infested countries are not permitted entry into the USA without a phytosanitary certificate. In addition, palm handicrafts are not permitted to enter Florida.

Biological Control

Biological control is seen as the best way to tackle the introduction of the mite, due to its widespread presence throughout the Caribbean and now Florida and South America. Chemical control is difficult as palms can grow incredibly tall and are difficult to treat. Several routes of biological control are being investigated. Peña et al. (2009) have investigated the response of native and commercially-produced predators to the introduction of R. indica into Florida. Predator density was observed to increase 6 months after the introduction of R. indica into Florida with the most common association found to be with Amblyseius largoensis. Laboratory studies by Carrillo et al. (2010) have shown that A. largoensis can play a role in controlling R. indica in Florida, and observations from the field have shown this predator to increase in density on introduction of R. indica to the area (Peña et al., 2009). A. largoensis has been reported in association with R. indica in several of the countries where the mite is invasive, including Puerto Rico, Trinidad and Tobago (Peña et al., 2009), and Cuba (Ramos-Lima et al., 2010).  Interest has arisen in the possibility of classical biological control due to the abundance of predators reported in the Old World. Preliminary investigations by CABI (B Taylor, CABI, 2009, personal observation) into the possibility of classical biological control have been funded by USDA. The study has looked at the abundance of predators associated with R. indica in India, and studies have confirmed that phytoseiid mites are the most commonly-occurring predator associated with the mite (species ID underway). However, suitability as biological control agents has not been investigated and further research is required before the importation of an exotic predator would be possible.

Chemical Control

Several trials have been carried out in India regarding the control of R. indica, the most recent including Nadarajan et al. (1980); Sarkar and Somchoudhury (1988); Jalaluddin and Mohanasundaram (1990); Senapati and Biswas (1990) and Jayaraj et al. (1991). Nadarajan et al. (1980) tested several compounds including the systemic pesticides dimethoate and formothion, which were applied through stem injection; results showed that all treatments significantly reduced R. indica numbers. The most recent trials have been carried out by Peña et al. (2008), and Peña and Rodrigues (2010) in Florida and Puerto Rico. Results showed significant reduction in mite density for several chemicals including spiromesifen, dicofol, acequinocyl and etoxazole. Sarkar and Somchoudhury (1988) reported 69.2% mortality with dicofol in India. Peña and Rodrigues (2010) tested further compounds and found that Sanmite [pyridaben] and Avid [avermectin] + Glacial gave the best results for keeping R. indica densities low on coconut seedlings and on bananas good control was observed using TetraSan [etoxazole] and acequinocyl. However, it is proposed that the best results for the control of R. indica will come from implementing an IPM programme. Acaricides that are currently available do not give 100% control of R. indica and a programme using chemicals to initially suppress high pest populations and the subsequent use of biological control agents to keep populations low is thought to be the best approach for control (Bronson, 2009).

Links to Websites

NameURLComment
Detection & Identification of the red palm mite (Raoiella indica)http://www.sel.barc.usda.gov/acari/PDF/indicaGuide.pdf 
Florida Department of Agriculture & Consumer Services - Division of Plant Industryhttp://www.doacs.state.fl.us 
GISD/IASPMR: Invasive Alien Species Pathway Management Resource and DAISIE European Invasive Alien Species Gatewayhttps://doi.org/10.5061/dryad.m93f6Data source for updated system data added to species habitat list.
USDA Program Aid no. 1935 - Look out for the red palm mitehttp://www.aphis.usda.gov/publications/plant_health/content/printable_version/RedPalmMite_6-20-7.pdf 

Organizations

NameAddressCountryURL
United States Department of Agriculture1400 Independence Avenue
Washingon DC 20250
USAwww.usda.gov

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Published online: 23 November 2009

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  • Predation of Raoiella indica (Acari: Tenuipalpidae) by Stethorus tridens Gordon (Coleoptera: Coccinellidae), Acarologia, 10.24349/1hy9-av19, 64, 1, (202-212), (2024).
  • Presence of Raoiella indica Hirst (Acari: Tenuipalpidae) at an unexpected altitude: in Mexico City., Acarologia, 10.24349/hzhq-damn, 63, 2, (591-595), (2023).
  • The association between the exotic species Raoiella indica Hirst and the predator Amblyseius largoensis (Muma) may cause displacement of the native species Oligonychus pratensis (Banks), Biological Invasions, 10.1007/s10530-023-03205-1, 26, 3, (757-767), (2023).

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