This standard describes procedures for official control aiming to monitor, contain and eradicate Bactrocera zonata.
This standard describes procedures for official control aiming to monitor, contain and eradicate Bactrocera zonata.
First approved in 2010–09.
Bactrocera zonata (peach fruit fly) is an A1 pest for EPPO and is regulated by many EPPO member countries (often as Dacus zonatus). Details of its biology, distribution and economic importance can be found in EPPO/CABI (1997).
Bactrocera zonata originates from South and South-East Asia (India, Indonesia, Laos, Sri Lanka, Thailand, Vietnam) and has been introduced into Bangladesh, Myanmar, Nepal, Pakistan, Saudi Arabia, Oman, Mauritius and Reunion Island. It is now present throughout Egypt, up to the borders of the Palestinian Territories (Gaza Strip) and Israel. Its presence has also been recorded recently in southern Iran and Lebanon. Experience in Egypt shows that B. zonata has already adapted to climatic conditions different to those in its area of origin. This major economic pest presents a threat to countries in West Asia, but also in North Africa and in Southern Europe.
The main hosts of B. zonata are guava, mango and peach. Secondary hosts include apricot, fig and citrus. This fly has been recorded on over 50 cultivated and wild plant species, mainly those with fleshy fruits. A list of susceptible species is given in Appendix 1. Eggs are laid inside the fruit and larvae feed on the fruit. Transport of infested fruit, either through trade or by travellers, is the main means of movement, and the pest will also spread via fruit packaging material. Its natural means of spread is adult flight.
EPPO member countries with areas at risk are advised to prepare a contingency plan for surveillance, eradication and containment of B. zonata.
This standard presents the basis of a national regulatory control system for the eradication and containment of B. zonata and includes guidance on its surveillance.
Countries where B. zonata is not capable of establishment due to climatic, geographical or other reasons, and where absence is recognized according to the first paragraph of section 3.1.2 of International Standard for Phytosanitary Measures (ISPM) No. 8 (Determination of pest status in an area), may decide that they have no reasons to apply the standard.
The EPPO countries bordering areas of known infestation are at highest risk and are advised to prepare a contingency plan for surveillance and eradication. Attention should be paid to providing sufficient traps, and registering suitable plant protection products for emergency treatments. Facilities should be identified which are suitable for disposal of contaminated wastes, destruction of woody plants and treatment of harvested fruits to ensure freedom from pests. Field inspection staff, including non-permanent workers, should be trained. Laboratories should have specimens of adults, larvae and pupae available and staff suitably trained in determining B. zonata.
This standard has been prepared on the basis of the Peach Fruit Fly Action Plan (FAO/IAEA, 2000), the NAPPO Regional Standards for Phytosanitary Measures No. 10 (NAPPO, 1998) and ISPM No. 26 Establishment of pest free areas for fruit flies (Tephritidae) (IPPC, 2006c).
Monitoring of B. zonata should be conducted in areas in which the risk of spread of this pest has been identified and/or where outbreaks have occurred in the past. Monitoring procedures including in particular trapping scenarios, relevant attractants and trap types for B. zonata are described in Appendix 1 to ISPM No. 26 Establishment of pest free areas for fruit flies (Tephritidae) (in preparation).
The eradication programme for B. zonata is based on the delimitation of an area or areas within the country in which measures are applied to eradicate it. Measures should also be taken to prevent further spread of the pest. These measures are described in Appendix 2.
The following host list (Table 1) was developed from literature citations and communication with plant protection officials and research scientists familiar with the peach fruit fly. Fruits that have been found infested with B. zonata larvae are marked with an asterisk. These hosts should be included on any list of regulated hosts for quarantine purposes.
|Scientific name||Common name|
|Aegle marmelos*||Indian bael|
|Annona reticulata*||Custard apple, Annona|
|Annona squamosa*||Custard apple|
|Careya arborea*||Patana oak; Kumbhi|
|Carica papaya*||Papaya, common|
|Citrofortunella japonica||Calamondin orange|
|Citrus aurantilifolia*||Sour lime|
|Citrus aurantium*||Sour orange|
|Citrus limon*||Lemon; Baramasi|
|Citrus nobilis*||King orange; Tangor|
|Citrus reticulata*||Mandarin (tangerine)|
|Citrus sinensis*||Orange, sweet|
|Coccinia grandis*||Gourd, Ivy|
|Cucumis utilissimus*||Melon, long|
|Elaeocarpus angustifolius||Blue marbletree; New Guinea quandong|
|Eriobotrya japonica*||Loquat; Lokat|
|Eugenia brasiliensis||Brazil cherry|
|Eugenia uniflora||Surinam cherry|
|Felijoa sellowiana||Pineapple guava|
|Ficus benghalensis||Banyan fig|
|Ficus carica*||Fig, common|
|Ficus macrophylla||Moreton Bay fig|
|Ficus retusa||Glossy leaf fig|
|Ficus rubiginosa||Port Jackson fig|
|Fortunella japonica*||Chinese orange; Kumquat; Narange|
|Lagenaria siceraria(=L. vulgaris)*||White flower; bottle gourd, calabash gourd|
|Luffa acutangula*||Ribbed or ridged gourd; Kali torai, Jhinga, Luffa|
|Luffa aegyptiaca*||Smooth loofah; sponge gourd; Ghia torai|
|Lycopersicon esculentum*||Tomato; Tamatar|
|Madhuca indica*||(=Bassia latifolia) Mahua; Mohua; Mowra-buttertree|
|Malus(=domestica) sylvestris*||Apple, common|
|Malus pumila||Paradise apple|
|Mangifera foetida||Bachang mango|
|Manilkara hexandra||Balata sapodilla|
|Momordica balsamina||Balsam apple hawthorn|
|Momordica charantia*||Balsam pear, bitter melon; bitter gourd|
|Momordica cochinchinensis||Balsam apple|
|Ochrosia elliptica||Bourbon orange|
|Phoenix dactylifera*||Date palm|
|Prunus americana||American plum|
|Prunus avium||Sweet cherry|
|Prunus cerasifera||Cherry plum|
|Prunus domestica||Garden plum (common European prune)|
|Prunus ilicifolia(ornamental)||Cherry, hollyleaf|
|Prunus lusitanica||Portuguese laurel cherry|
|Prunus lyonii||Cherry, Catalina|
|Prunus persica var. nectarina*||Nectarine|
|Prunus salicina x Prunus cerasifera||Methley plum|
|Prunus salicina||Japanese plum|
|Psidium cattleianum*||Strawberry guava; Chinese guava|
|Psidium cattleianum littorale||Red strawberry guava|
|Psidium cattleianum lucidum||Yellow strawberry guava|
|Putranjiva roxburghii*||Olive, wild; Indian amulet plant|
|Pyrus pyrifolia||Pear, sand|
|Solanum auriculatum*||Wild tobacco; Tabac marron|
|Solanum pseudocapsicum||Jerusalem cherry|
|Solanum seaforthianum||Brazilian nightshade|
|Solanum verbascifolium||Mullein nightshade|
|Syzygium aquea*||Water apple; Watery roseapple; Lal; Jumrool|
|Syzygium cumini*||Java plum; Jambolana|
|Syzygium jambos*||Rose-apple; Jamrosat; Jambos; Malabar-plum|
|Syzygium samarangense*||Java apple; Water apple|
|Terminalia catappa*||Tropical or Indian almond|
|Ziziphus mauritiana*||Chinese date (India jujube); Ber|
In recent years, this insect has expanded its global distribution and host range. The adventive nature of this fly demands that National Plant Protection Organizations give greater attention to its presence in order to take prudent measures for its early detection, containment and elimination. As this pest spreads to new areas, it will be exposed to new hosts suitable for its reproduction, and may attack closely related species within the same genus. For this reason, some closely related species are included below without a star. Since it is not fully known which plants will be suitable hosts for B. zonata should it become established in other parts of the world, any host listed below should be carefully inspected for possible infestation. In fact, it is not known which hosts may be preferred by adult B. zonata and no assumptions have been made in this regard.
This pest is similar to the Oriental fruit fly, Bactrocera dorsalis in terms of its broad host preferences. Bactrocera zonata may be similar to B. dorsalis in other respects. Some scientists believe that B. zonata may be a hybrid or intermediate form resulting from the cross of B. dorsalis with the guava fly, B. correcta (Iwahashi & Routhier, 2001). Hosts are listed first by scientific name followed by common name(s). An attempt has been made to select the most widely recognized common name, although common names vary from location to location. All hosts with asterisks by their names in Table 1 should be regulated for B. zonata.
In order to conduct an eradication programme in an area where B. zonata has been trapped, surveillance should be carried out to determine the extent of the infestation. A quarantine area should be designated in which eradication measures should be implemented. In addition, measures may be put into place to prevent further spread to non-infested areas.
Different areas are defined for eradication and surveillance.
When one or more B. zonata are collected in an area, a delimiting survey should be implemented immediately to determine the extent of the infestation.
Using the site of detection as the epicentre, Jackson traps will be set out in a 10-3-3-3-3 per square kilometre (km²) trap array sequence. This area will constitute the trapping area. Such design may be adapted to local conditions (no trapping is necessary when uncultivated areas such as desert surround the epicentre). In areas with scattered commercial orchards, rural low-population villages with backyard fruit host, and in marginal areas where commercial and wild hosts exist, trap network arrays are normally linear with a distribution pattern that follows roads that provide access to host material. Traps should be controlled every week.
A core area is delimited as the 2.56 km2 area immediately surrounding the epicentre. McPhail traps (See Appendix 1 of ISPM No. 26 for trap information) are to be placed in the core area as well as in the first array around the core area at the same rate as Jackson traps.
The area with a radius 7–40 km from the core should be trapped at a minimum of 1 Jackson trap km−2 (See Appendix 1 of ISPM No. 26 for trap information).
An illustration of trapping setting is given in Fig. 1.
Fruit sampling may be used as a surveillance method in combination with trapping where trapping is less effective. It should be noted that fruit sampling is particularly effective in small-scale delimiting surveys in an outbreak area. However, it is labour-intensive, time consuming and expensive due to the destruction of fruit. It is important that fruit samples are held in suitable conditions to maintain the viability of all immature stages of fruit fly in infested fruit for identification purposes.
Fruit sampling should take into consideration the presence of primary, secondary and occasional hosts of B. zonata. Fruit sampling should also preferably target mature fruit, and take account of apparent signs of infestation in fruit, and commercial practices (e.g. application of insecticides) in the area.
Fruit sampling should be targeted on areas likely to have presence of infested fruits such as:
Fruits should be sampled during the period when the different hosts are likely to be infested by B. zonata.
Factors to be considered include:
Valuable information on the size of samples in relation to the required level of confidence is given in ISPM 31 Methodologies for Sampling of Consignments (IPPC, 2008).
Fruit of preferred host in the trapping area may be cut and examined for larvae. If fruit fly larvae are found, the infested samples are taken in a sealed container for identification.
When two adult flies or one mated female or a larva of B. zonata are detected within one estimated life cycle, within an area of 9 km radius, an infestation of B. zonata is considered to be detected. An eradication programme should then be initiated. It is also necessary to adjust the delimitation of the trapping area accordingly. In addition to eradication measures, other measures are applied to prevent further spread. This requires establishing two types of quarantine area (see Table 2).
|Bactrocera zonata trapping results||Measures implemented|
|2 adult flies|
1 mated female
|Eradication measures in an area of 9 km radius from the epicentre are initiated.|
|within one estimated life cycle, within an area of 9 km radius.|
|>5 adult male flies|
an unmated female and a male
or one mated female,
a single adult fly is found when eradication programme in place.
|Eradication measures in an area of 9 km radius from the epicentre|
Containment measures are initiated in an area of 7.5 km radius from the epicentre maintained until eradication has been declared.
|within one estimated life cycle|
within an area less than 3 km2
The eradication measures are applied in an area of 9 km radius from the epicentre.
In addition to eradication measures, measures to prevent the spread of the pest are applied to commodities leaving an infested area if any of the following are detected, within an area < 3 km2, during one estimated B. zonata life cycle:
Measures to prevent further spread of the pest will be applied in an area of 7.5 km radius from the epicentre and will be maintained until eradication has been declared.
The treatments described below are those applied in countries with fruit fly eradication programmes. Some of these treatments may not be allowed in EPPO countries and attention should be paid to the registering of suitable plant protection products for emergency treatments.
The minimum programme consists of ground-applied male annihilation treatments.
In an urban area, the control programme will be composed of ground-applied male annihilation treatments, soil treatments and fruit stripping. The commercial area may be treated as above with the addition of bait sprays. Eradication treatments recommended in the IAEA Peach fruit fly action plan are presented in Appendix 3.
The male annihilation technique (MAT) is the most suitable method available to date for the eradication/control of B. zonata. The MAT relies on the combined use of sexual attractants (methyl eugenol in the case of B. zonata) and insecticide to eliminate male flies, thus stopping mating. The insecticides used are generally organophosphorus compounds, such as malathion or naled. The lure/insecticide combination is applied as spot treatments. Two treatment options are possible: neutral gel as carrier of a mixture of methyl-eugenol and insecticide (also called Min-U-Gel applications) or lure-and-kill stations (i.e. wooden blocks, caneite blocks or cotton cord impregnated with the mixture methyl-eugenol and insecticide). The first option may result in foliage burn so the second is often preferred. It should be noted that the use of lure-and-kill blocks could interfere with trapping. This technique may be combined with the protein bait application technique (BAT), a widely used technique for controlling fruit flies, in which an insecticide and a protein source are associated. If treatments selected or proposed are not in conformity with current registration of plant protection products, an emergency exemption may be provided.
In areas where eradication is envisaged, B. zonata should be continually monitored using methyl eugenol insecticide baited traps. Eradication treatments should continue for at least two B. zonata life cycles.
When measures to prevent further spread are necessary (see section Quarantine area where measures to prevent further spread are implemented), the following containment measures should be implemented in an area with a 7.5 km radius from the epicentre:
Eradication can be declared when measures have been applied for a minimum of two B. zonata life cycles, and trapping has been negative for at least one additional B. zonata cycle after eradication measures have stopped.
The following is provided only to give some guidance on the type of measures which may be considered. Many of the plant protection products are unavailable in many EPPO member countries and the application techniques are not directly available.
Recommended plant protection products
Spot treatment: Apply the lure/insecticide using a Panama pump gun (available from Forestry Supplies, Mississippi, US) or a hydraulic oil squirt can to localized spots on utility poles, trees, fences, etc. The bait will burn foliage and therefore leaves should not be treated unless no other sites exit. Alternatively, fibre blocks saturated with the attractant and insecticide or cordallitos (short segments of cotton rope or cigarette filters) also can be used effectively as lure-and-kill stations. Fibre blocks can easily be nailed or stapled to a surface temporarily and removed or collected after 90 days.
Apply the mixture at the rate of 3–5 mL per station at a height of about 2 m above the ground out of the reach of children. Apply at least 240 evenly distributed stations per km2 or 60–80 to a city block. This equals about one bait station every 45–50 m. Apply treatment every 2 weeks. The area of coverage will be 25 km2 around each fly find.
Treatment or retreatment should not be considered if weather reports indicate a 50% or greater chance of precipitation within 48 h.
The objectives are to eradicate the pest and minimize environmental contamination. Any treatment or retreatment recommendations must consider these objectives.
Application of full-coverage protein bait spray will be scheduled and applied 7–10 days apart. The area of full coverage bait spray will extend a minimum of 2.5 km beyond any known infestation. It may be expanded to 4.0 km from any find if the infestation is heavy. Weather conditions may dictate changes in spray schedule. After an estimated two B. zonata generations of negative trapping, spray operations may be discontinued.
Properties with confirmed larval infestations and the environs within 200 m will have approved soil treatments applied within a minimum of 1 m outside the dripline of all host plants, and a minimum of a 1 m radius around any spot to which host fruit may have dropped or rolled. Take particular care to soak cracks or crevices in or next to barriers to horizontal movement of larvae (i.e. sidewalks, stones, etc.). Apply prescribed treatments at intervals stated in the specific exemption, as appropriate. Normally, the interval is 14–16 days.
Diazinon: (Diazinon AG-500) 108 mL a.s. of 48% diazinon in enough water to soak 5 cm of soil over 900 m2 (5.6 kg of a.s. per ha) to kill larvae, pupae, and emerging adults. Adjust water pH to 6.5 or less prior to adding insecticide.
Diazinon: (Diazinon 14 G). Work Diazinon 14 G 3–5 cm into the soil at the rate of 39 kg ha−1 (5.6 kg of a.s. per ha) or 41 g per 3.6 m diameter drip circle (9.6 m2). The area should be treated with water that has been buffered (pH 6.0–6.5) to enhance percolation of the material into the soil.
All hosts (available shelter, oviposition, or food sites in any stage of development) on the infested property, adjacent properties, and within approximately 200 m of the known find will be sprayed at the prescribed intervals. Ground spraying may be discontinued after an estimated two B. zonata generations of negative trapping or after the initiation of male annihilation or of aerial treatment.
The bait may be applied as a limited coverage application to hosts and plants providing shelter or resting areas by means of a backpack sprayer or equivalent unit. Applications are to be sprayed out of reach of children or pets. If full coverage application is desired, a mistblower or similar unit can be utilized. Treatments are to be applied 7–10 days apart. Subsequent applications, if in orchards or groves, may be decreased by treating every other tree.
Historically, ground applications of protein bait spray formulations in urban areas have not significantly reduced infestations, unless carried out on an area-wide basis in a centrally-coordinated fashion. This can overcome the failure to gain access to all sites requiring treatment, equipment constraints and timeliness of applications. If properly organized and carried out, such treatments can eradicate small outbreaks in urban areas.
All ripe preferred host fruit within 200 m of a confirmed larval site should be promptly stripped and placed in plastic bags and properly disposed of in an approved landfill.