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BIOLOGICAL CONTROL- AND PREDATORS Response of Psyttalia humilis (: ) to Fruit (Diptera: ) and Conditions in California Olive Orchards

VICTORIA Y. YOKOYAMA,1 PEDRO A. RENDO´ N,2 XIN-GENG WANG,3 SUSAN B. OPP,4 5 3 MARSHALL W. JOHNSON, AND KENT M. DAANE

Environ. Entomol. 40(2): 315Ð323 (2011); DOI: 10.1603/EN10186 ABSTRACT The larval , Psyttalia humilis (Silvestri), reared on Mediterranean fruit ßy, (Weidemann), by USDA-APHIS-PPQ, San Miguel Petapa, Guatemala was imported into California for biological control of olive fruit ßy, oleae (Rossi). This study reports the results of Þeld releases and recovery of P. humilis in California, and laboratory investigations to determine the effects of food provision, high temperature, and insecticidal bait spray on the parasi- toidÕs survival and fecundity. Parasitoids (3,613Ð7,823) were released in Orland, San Juan Bautista, Cayucos, Sylmar, Santa Barbara, and San Diego during October through December 2006. Mean daily temperatures at the release sites ranged from 10.7ЊC in Orland to 20.9ЊC in San Juan Bautista. The lowest (0.5) and highest (29.7) mean number of adult B. oleae per day per trap was captured in Orland and Sylmar, while the lowest (0.01) and highest (2.21) number of third instar larvae per fruit was collected on 11 December in Orland and on 5 October in San Diego in prerelease samples, respectively. Parasitoids were recovered from all release sites, the lowest (0.3%) and highest (100%) occurred on 25 January in Sylmar and on 26 October in Cayucos, respectively. At 24ЊC, parasitoids reared from B. oleae larvae survived 36 d on honey, 31 d on orange juice, and 28 d on honeydew, which was signiÞcantly longer than on cut olive fruit (8 d) or without food (11 d), but was similar to those reared from C. capitata larvae under the same food conditions. Under a high diurnal temperature regime (18.3Ð35ЊC) reßecting the summer olive growing conditions in the California Central Valley, the parasitoids survived Ͻ5 d when no food or only water was provided. Its longevity and life-time fecundity signiÞcantly increased by provision of honey or honeydew. There was no difference in the parasitoidÕs longevity between females and males or between food and sexes. Percent mortality of parasitoid adults was not signiÞcantly affected by the exposure to insecticidal fruit ßy bait (GF-120) in four different types of choice tests with artiÞcial honeydew and GF-120.

KEY WORDS Larval parasitoid, Bactrocera oleae (Rossi), europaea L.

Olive fruit ßy, Bactrocera oleae (Rossi), has created a (Yokoyama et al. 2006, Yokoyama 2011). Current olive serious economic threat to the California olive indus- fruit ßy management strategies are based on spray try since it was Þrst detected in 1998 (Rice et al. 2003). applications of spinosad-formulated fruit ßy bait (GF- High numbers of olive fruit ßy occur in the coastal 120) (Johnson et al. 2006) that are timed using pher- areas, where nearly every fruit can be infested on omone-based trapping programs (Yokoyama et al. untreated trees, while lower numbers of the pest are 2006, Burrack et al. 2008), information on pest and found on in the warmer interior valleys olive cultivar associations (Burrack and Zalom 2008), and cultivation practices (Yokoyama and Miller 2007). Bait sprays may have limited future use because olive This article reports the results of research only. Mention of a fruit ßy resistance to spinosad has been recently re- proprietary product does not constitute an endorsement or recom- mendation for its use by the USDAÐARS or USDA-APHIS-PPQ. ported (Kakani et al. 2010). Although postharvest 1 USDAÐARS, San Joaquin Valley Agricultural Sciences Center, treatments for fruit have been developed (Yokoyama 9611 South Riverbend Ave., Parlier, CA 93648 (e-mail: and Miller 2004), the market for table olives has a very [email protected]). low tolerance for infested fruit and researchers have 2 USDA-APHIS-PPQ-CPHST, Guatemala City, Zona 10, Guate- mala. shown olive fruit ßy can negatively impact 3 Department of Environmental Science, Policy and Management, quality (Gomez-Caravaca et al. 2008). Therefore, ad- University of California, Berkeley, CA 94720. ditional control tools are needed to suppress olive fruit 4 Department, California State University, East Bay, 25800 ßy infestations. Carlos Boulevard, Hayward, CA 94542. 5 Department of Entomology, University of California, Riverside, Natural enemies have the potential to reduce olive CA 92521. fruit ßy populations, especially in untreated ornamen-

0046-225X/11/0315Ð0323$04.00/0 ᭧ 2011 Entomological Society of America 316 ENVIRONMENTAL ENTOMOLOGY Vol. 40, no. 2 tal olive trees and un-harvested orchards that serve as a reservoir for ßy populations (Collier and van Steen- wyk 2003). Reports of classical biological control pro- grams against the olive fruit ßy have provided mixed results (Tzanakakis 2006, Daane and Johnson 2010). The most commonly used parasitoid species, in past olive fruit ßy programs, has been Psyttalia concolor (Sze´pligeti). Results from early European and Mideast importation programs suggest this parasitoid has es- tablished in some regions (Neuenschwander 1982, El- Heneidy et al. 2001), but rarely contributes to olive fruit ßy control without large inundative releases (Monastero and Delanoue 1966, Kapatos et al. 1977, Liaropoulos et al. 1977). More recently, P. concolor has been reported to provide a seasonal average parasitism Ͼ20% in Majorca (Balearic Islands) in organically managed orchards without augmenting parasitoid populations (Miranda et al. 2008). Reported differences in P. concolor effectiveness may result from the parasitoidÕs environmental toler- ance to each region as olives are grown in climatic zones ranging from arid-desert to coastal-Mediterra- nean. Different pest complexes are also found in olive Fig. 1. Parasitoid research sites in 2006. orchards (Tzanakakis 2006) and insecticide treat- ments against these pests may be incompatible with the survival or performance of some natural enemy is well known (Yokoyama et al. 2006, 2010), and Þeld species (Nadel et al. 2007). Most important may be releases were concentrated in those California regions differences among populations of the P. concolor com- where high densities of olive fruit ßy populations are plex. Sime et al. (2006) showed slight biological dif- commonly found. Fly densities and were mon- ferences between two P. concolor populations that itored during pre- and postrelease samples at the re- originated from the same stock of north Africa mate- lease sites. We then conducted a series of laboratory rial, but had been reared for years under different studies to assess the potential effects of various con- conditions. Greater differences may exist among geo- ditions found in California olive orchards on the para- graphically distinct natural populations within the P. sitoidÕs survival and/or fecundity, to better under- concolor complex, which are widely distributed in Af- stand the Þeld conditions that would favor survival and rica (Wharton et al. 2000, Mkize et al. 2008). Recent possible establishment of the parasitoids after being molecular analyses showed clear separation of the released. SpeciÞcally, we investigated the effects of northern Africa and sub-Saharan populations (Karam (1) presence or absence of foods that may be found in et al. 2008, Rugman-Jones et al. 2009). Most of the early the vicinity of olive groves on the parasitoidÕs survival; European programs used P. concolor from northern (2) weather extremes found in the inland olive grow- Africa, speciÞcally Tunisia, Libya, and Morocco ing regions on the parasitoidÕs survival as well as fe- (Clausen 1978, Wharton 1989a). In contrast, parasi- cundity; and (3) GF-120 bait spray on the parasitoidÕs toid material used in this study was collected in Kenya, survival. which we henceforth refer to as P. humilis (Silvestri) as this is an available name for sub-Saharan popula- Materials and Methods tions (Rugman-Jones et al. 2009) previously referred to as P. concolor (Wharton 1989b, Wang et al. 2009c) Field Release and Recovery of P. humilis. Six sites or P. cf. concolor (Kimani-Njogu et al. 2001, Yokoyama were selected for Þeld releases of P. humilis in Cali- et al. 2008a). fornia (Fig. 1). The olive trees in each site were not Yokoyama et al. (2004) Þrst used P. humilis for sprayed with insecticides or harvested for fruit, which biological control of olive fruit ßy in 2002 in California was desired for postrelease sampling and parasitoid and later mass-produced the parasitoid in Guatemala establishment. on irradiated Mediterranean fruit ßy (Medßy), Cer- Adult P. humilis were reared from third instar Med- atitis capitata (Wiedemann) and the parasitoid ßy (Antigua strain) in the Moscamed biological con- adults were shipped to California for Þeld releases trol laboratory, San Miguel Petapa, Guatemala, as de- (Yokoyama et al. 2010). In this study, we used P. scribed by Yokoyama et al. (2008b). Adult parasitoids humilis reared on fertile Medßy. We Þrst sought to were packaged in waxed paper cups (0.275 liters), determine the ability of P. humilis to be Þeld-released with Ϸ400 parasitoids, Ϸ50% females per cup, and and consistently recovered in California olive or- shipped to the USDA-ARS in Parlier, CA (Fig. 1), as chards that used standard management practices, with described by Yokoyama et al. (2010). On arrival, 3Ð4 the exception of insecticide sprays. The seasonal abun- waxed paper cups each were placed in aluminum- dance of olive fruit ßy in different regions of California framed, organdy-screened cages (30.5 ϫ 30.5 ϫ April 2011 YOKOYAMA ET AL.: PARASITOID RESPONSE TO HOST AND FIELD CONDITIONS 317

Table 1. Region and specific location, description of the olive trees, and fruit sample dates from Oct. 2006 to Jan. 2007 in parasitoid release sites

Region Site GPS coordinates Cultivar No. trees Tree layout Sample date Trees sampled Sacramento Valley Orland 39Њ 44ЈN, 122Њ 10ЈW Ascolano 15 Grove 9 Nov. 3 11 Dec. 2 Central Coast San Juan Bautista 36Њ 50ЈN, 121Њ 32ЈW Mission 12 Grove 17 Oct. 3/4a 23 Oct. 4 Cayucos 35Њ 29ЈN, 120Њ 56ЈW Mission 15 Windrow 19 Oct. 4 26 Oct. 4 Santa Barbara 34Њ 27ЈN, 119Њ 42ЈW Mission 7 Windrow 26 Oct. 4 3 Nov. 4 Southern Sylmar 34Њ 18ЈN, 118Њ 27ЈW Mission 28 Grove 17 Nov. 1 1 Dec. 4 8 Dec. 4 15 Dec. 4 25 Jan. 4 San Diego 33Њ 01ЈN, 117Њ 02ЈW Mission 17 Windrow 5 Oct. 4/10b 2 Nov. 2 9 Nov. 2

a Three prerelease trees sampled, and parasitoids released on four trees. b Four prerelease trees sampled, and parasitoids released on 10 trees.

30.5 cm, BioQuip Products, Rancho Dominguez, CA). To estimate olive fruit ßy populations, adults were The cups were opened in the cages, and the parasitoids trapped using four to six yellow panel Pherocon AM provided with water and honey for food, allowed to traps (Tre´ce´ Inc., Adair, OK), with a clear packet of mate, and observed within 1 d. The parasitoids were ammonium bicarbonate bait (15Ð20 g), and a plastic then transported to release sites where the cages were dispenser (1.7 cm wide ϫ 4.8 cm long) containing placed beneath trees with fruit visibly infested with pheromone (1,7-dioxaspiro[5,5]undecane, 80 mg). olive fruit ßy larvae, and the parasitoids released di- Traps were placed at mid-canopy height (Ϸ2.4 m) in rectly from the cages. The number of dead parasitoids a shaded area near fruit, with each trap in a separate were counted inside each paper cup and cage and tree and traps spaced one to several trees apart. At the subtracted from known number in each shipment to end of the exposure period, the total number of fe- determine the number of parasitoids released. males and males in each trap were counted, and the Releases were made from 5 October to 15 Decem- results reported as mean (ϮSEM) per day per trap and ber 2006, during the period when olive fruit can be percentage females. heavily infested. The number of parasitoids released To determine parasitism levels, samples of olive was based on the quantity received in each shipment. fruit were randomly sampled from trees before and The number of trees and fruit per tree sampled was after parasitoid releases to record emerging numbers based primarily on availability at each site, with a goal of olive fruit ßy pupae and adults or P. humilis adults. of sampling and releasing in four trees per site, and Fruit samples were placed in plastic containers (22 cm collections of Ͼ100 fruit per tree. Postrelease samples wide ϫ 32 cm long ϫ 13 cm high), covered with were made from those trees receiving parasitoids the organdy cloth, and held in the laboratory at 23 Ϯ 2ЊC. previous sample date, and typically ranged from 4 to After all had emerged, rates of parasitism were 8 d after the release. Information in Table 1 shows the calculated for each site and sample date, based on region and speciÞc location of parasitoid releases, de- previously published procedures (Yokoyama et al. scription of the olive trees, and fruit sample dates and 2008, 2010). Percentage parasitism was based on the trees sampled at each release site. number of available third instar, rather than the total Temperature loggers (model XTI08Ð5 ϩ 37) with number olive fruit ßy larvae present, as eggs and young external thermistors (model TMC6Ð1T) and humidity instar olive fruit ßy are unsuitable oviposition of the P. loggers (model SRHA08, Onset Computer, Bourne, concolor species complex (Sime et al. 2006) and MA) were used to record temperature and relative Yokoyama et al. (2008) reported that P. humilis caused humidity at each site. The data loggers (2Ð4 per site) mortality of the Þrst and second instars. Thus, the were placed in the canopy of sampled trees, and pro- number of third instars available to the parasitoids on grammed to record every hour. During the study, two each release date was calculated from the number of temperature loggers failed in San Juan Bautista, and olive fruit ßy larvae and pupae that emerged for4din the hourly temperatures were obtained from the Cal- prerelease fruit samples. The number of available third ifornia Irrigation Management Information System instars was multiplied times the number of fruit in (CIMIS) weather station No. 143, San Juan Valley (36Њ each postrelease fruit sample, and reported as the 49ЈN, 121Њ 28ЈW), Ϸ6.6 km southeast. The temperature mean (ϮSEM) of the replicates. Percentage parasit- logger for 17 November through 1 December was lost ism was calculated by dividing the number of parasi- at the Sylmar location, and the daily temperatures toids that emerged in the postrelease fruit samples by were obtained from the Weather Underground station the estimated number of available third instars and KCASYLMA2 (34Њ 18ЈN, 118Њ 27ЈW) in Sylmar. reported as the mean (ϮSEM) of the replicates. 318 ENVIRONMENTAL ENTOMOLOGY Vol. 40, no. 2

Laboratory Studies and Colonies. A series of drops of brown soft scale honeydew presented on 3Ð4 three laboratory studies were conducted to determine leaves of a Þcus (Ficus benjamina L.); and (5) no food the effect of limited food resources, temperature, and or water. For each treatment, 13Ð15 newly emerged insecticidal bait use on longevity and/or fecundity of (Ͻ1d old) collected from the USDA-ARS col- P. humilis at the University of CaliforniaÕs Kearney ony were placed in an aluminum frame and screened Research and Education Center (KREC) in Parlier, cage (20.3 ϫ 20.3 ϫ 20.3 cm) (model 1450AS, BioQuip CA; USDA-ARS in Parlier; and California State Uni- Products) with water in a shell vial at the top of the versity, East Bay, CA, respectively. cage. Food provisions were placed on the bottom of At KREC, colonies of olive fruit ßy and P. humlis the cage. Every 1Ð3 d thereafter, parasitoid survival were maintained on olives in an insectary room at 25 Ϯ was evaluated in each cage and food treatments were 2ЊC, 16L:8D, and 40Ð60% RH. The olive fruit ßy colony renewed. There were four or Þve replicate for each had been maintained since 2003, with periodic addi- food treatment. tions of Þeld-collected insects into the colonies. Fruit The tests were repeated using 3Ð5 d-old parasitoids were collected from an insecticide-free KREC or- (22Ð30 wasps per cage) imported from the Guatemala. chard. The fruit were placed in organdy-screened Food treatments were similar except that honeydew cages (61 ϫ 61 ϫ 61 cm, Bug Dorm2, BioQuip, Rancho from the black scale on olive leaves was used instead Dominguez, CA). Each cage had 100Ð200 mature (1Ð2 of honeydew from brown soft scale. Results were wk old) olive fruit ßy females, which were supplied reported as the survival time mean (ϮSEM) of the with honey, water, and hydrolyzed yeast (FisherBio- replicates and compared among the different foods tech, Fairlawn, NJ). The fruit were left in the cage using a one-way analysis of variance (ANOVA), and until each fruit had 3Ð5 ovipositional sites. Exposed TukeyÕs test (GraphPadSoftware 2007). fruit were removed from the cage and placed on a Parasitoid Longevity and Fecundity in Response to raised metal screen, held 2 cm above a plastic tray. a High Diurnal Temperature Regime and Food After 10Ð12 d olive fruit ßy larvae exited the fruit and Source. The effects of high temperature and food dropped into the tray, where puparia were collected source on the survival and fecundity of P. humilis were and placed into holding cages for adult emergence. A evaluated at KREC in an incubator under a high di- P. humilis colony was initiated with Ϸ400 adults from urnal temperature regime of 35ЊC from 1200 hours to Guatemala in 2007, and the parasitoid had been main- 1900 hours, 18.3ЊC from 1900 hours to 1200 hours, and tained on olive fruit ßy. Adult parasitoids were held in photophase from 0500 hours through 1900 hours. This clear acrylic cages (30 ϫ 30 ϫ 30 cm) that had organdy temperature regime reßects common daily summer screen on three sides for ventilation and provisioned conditions in the inland valleys of California (Wang et with water and honey. Between 50Ð100 olives, con- al. 2009a). Chamber temperature was monitored with taining second and third instar olive fruit ßy, were a data logger (HOBO, Onset Computer, Bourne, MA). placed in the cages for a 1Ð3 d exposure period, de- Food provision treatments were (1) no food or water; pending on parasitoid density. After exposure, the (2) water only; (3) water and black scale honeydew; olives were placed on the metal grids above the plastic and (4) water and honey. Fresh black scale honeydew trays to collect the parasitized olive fruit ßy larvae and was collected on olive leaves from an untreated olive pupae as previously described (Wang et al. 2009c). orchard at KREC. The availability of water and food At the USDA-ARS in Parlier, a colony of P. humilis were continuously monitored and replenished as was also reared from olive fruit ßy in a manner similar needed throughout each test. to the KREC colony (Yokoyama et al. 2008). The Infested fruit containing olive fruit ßy early third parasitoids used in all laboratory studies were col- instars were obtained using similar methods as de- lected from the KREC or USDA-ARS P. humilis col- scribed above for insect rearing. For each food treat- onies, or directly imported from the Guatemala reared ment, a pair of newly emerged parasitoids (Ͻ1-d old) on Medßy. was released into a cylindrical acrylic cage (20 ϫ 15 ϫ Parasitoid Longevity in Response to Food Source. 15 cm) that had three organdy screen holes for ven- The effect of food source on the longevity of adult P. tilation. Each female parasitoid was provided with Þve humilis was tested under a laboratory condition infested fruit every 2 d until the female died. The (24.0 Ϯ 1.5ЊC, 63 Ϯ 3% RH and a photoperiod of longevity of both male and female parasitoids was 12L:12D) at the USDA-ARS in Parlier, using poten- evaluated in the morning and afternoon each day after tially available food sources in or near olive orchards. the beginning of the test. Life-time parasitoid fecun-

Natural food sources may include honeydew, excreted dity was estimated based on the number of F1 para- by the black scale, (Olivier) or brown sitoids that emerged from the exposed olives. Twenty soft scale, Coccus hesperidum L., (Hemiptera: Cocci- replicates were used for each treatment. Data were dae), common olive or citrus pests in California (Ew- compared using two-way or one-way ANOVA and art and Metcalf 1956, Daane et al. 1991); fruit juices TukeyÕs honestly signiÞcant difference test among dif- (Sivinski et al. 2006) such as orange commonly found ferent treatments (JMP, V. 6.0.3, SAS 2006, Cary, NC). in nearby citrus orchards; or damaged olive fruit. Parasitoid Response to GF-120 Fruit Fly Baiting. Food treatments were (1) damaged green olive fruit The potential effect of fruit ßy baiting using GF-120 on manually cut to the pit with a knife; (2) 13Ð16 drops P. humilis was evaluated under laboratory conditions of frozen orange juice concentrate that was diluted at California State University in East Bay, CA, using with water (1:1); (3)13Ð16 drops of bee honey; (4) female parasitoids directly imported from Guatemala. April 2011 YOKOYAMA ET AL.: PARASITOID RESPONSE TO HOST AND FIELD CONDITIONS 319

Table 2. Mean (؎SEM) trap captures of olive fruit fly adults, and daily temp and relative humidity from Oct. 2006 to Jan. 2007 at parasitoid release sites

% Њ No. ßies captured Daily temp ( C) Daily Site Trap period Captured per day per trap %RH females Highest Lowest Mean Orland 9 Nov.Ð11 Dec. 0.5 Ϯ 0.2 30.6 Ϯ 16.9 20.3 Ϯ 1.0 5.9 Ϯ 0.6 10.7 Ϯ 0.1 65.8 Ϯ 0.4 San Juan Bautista 17Ð23 Oct. 28.6 Ϯ 6.0 43.2 Ϯ 2.9 27.1 Ϯ 1.3 7.0 Ϯ 0.6 15.2 Ϯ 0.5 66.2 Ϯ 2.4 Cayucos 19Ð26 Oct. 6.6 Ϯ 1.2 31.7 Ϯ 3.6 24.8 Ϯ 2.2 14.4 Ϯ 1.7 19.6 Ϯ 0.5 51.6 Ϯ 2.8 Santa Barbara 26 Oct.Ð3 Nov. 25.4 Ϯ 4.5 49.0 Ϯ 3.0 23.2 Ϯ 1.8 15.7 Ϯ 1.1 19.9 Ϯ 0.4 20.4 Ϯ 0.5 Sylmar 17 Nov.Ð1 Dec. 17.5 Ϯ 4.9 29.0 Ϯ 2.9 21.1 Ϯ 1.3 10.2 Ϯ 0.8 15.5 Ϯ 1.0 34.5 Ϯ 1.0 1Ð8 Dec. 29.7 Ϯ 3.8 30.8 Ϯ 1.7 21.6 Ϯ 1.0 16.2 Ϯ 0.8 19.0 Ϯ 0.2 32.1 Ϯ 1.0 8Ð15 Dec. 22.5 Ϯ 4.0 19.1 Ϯ 5.8 17.4 Ϯ 0.7 14.3 Ϯ 0.5 15.8 Ϯ 0.1 69.5 Ϯ 0.5 15 Dec.Ð25 Jan. 3.8 Ϯ 0.5 41.8 Ϯ 5.4 17.5 Ϯ 0.9 11.7 Ϯ 0.7 14.3 Ϯ 0.2 50.9 Ϯ 0.9 San Diego 5 Oct.Ð2 Nov. 2.1 Ϯ 1.1 33.8 Ϯ 14.6 18.8 Ϯ 0.7 14.6 Ϯ 0.6 16.5 Ϯ 0.1 76.8 Ϯ 0.4 2 Nov.Ð9 Nov. 3.2 Ϯ 1.0 61.0 Ϯ 3.4 18.5 Ϯ 1.9 14.0 Ϯ 1.5 16.2 Ϯ 0.3 77.8 Ϯ 0.8

Parasitoids were maintained in the laboratory and are shown in Table 2. The mean number of adults provided with honey and water but the honey was captured per trap per day ranged from 0.5 in Orland removed 20 h before the tests. Five to 10 female (9 November through 11 December) to 29.7 in Sylmar parasitoids were placed in plastic and screen testing (1Ð8 December). Mean percentage of females per containers (23 cm2) and exposed to test substances for trap ranged from 19% in Sylmar (8Ð15 December) to 2 h. Test substances were artiÞcial honeydew (0.49 g 61% in San Diego (2Ð9 November). Mean daily tem- fructose, 0.42 g sucrose, 0.09 g glucose in 10 ml distilled peratures at the locations ranged from 10.7ЊCinOr- water, following the description by Byrne et al. 2003) land (9 November through 11 December) to 19.9ЊCin and GF-120, Naturalyte (Dow AgroSciences, India- Santa Barbara (26 October through 3 November). napolis, IN) fruit ßy bait (diluted 1:4 with distilled Mean daily relative humidity ranged from 20.4% in ␮ water). Four treatments were (1) no-choice, 30 2- l Santa Barbara (26 October through 3 November) to drops of artiÞcial honeydew; (2) no-choice, 30 2-␮l ␮ 77.8% in San Diego (2Ð9 November). The lowest tem- drops of GF-120; (3) separated-choice, 15 2- l drops perature (1.6ЊC) was recorded in Sylmar (21 January of artiÞcial honeydew and 15 2-␮l drops of GF-120 2007) and on a subsequent visit to the site (25 January) physically separated; and (4) mixed-choice of 15 2-␮l most of the fruit had fallen from the trees. drops of artiÞcial honeydew interspersed with 15 2-␮l The mean number of olive fruit ßy third instars per drops of GF-120 in the test container. Eight to nine replicates were used for each treatment. fruit and percentage parasitism by P. humilis is shown in After exposure, test substances were removed, and Table 3. In the Orland location, olive fruit ßy third instars the parasitoids were allowed to feed on honey and did not emerge from prerelease fruit samples and the water. Numbers of dead parasitoids were counted and number of third instars per fruit and the rate of parasitism removed for 4 d after each test. The results were were calculated from the postrelease fruit. Numbers of reported as the mean (ϮSEM) percentage mortality. third instars emerging from fruit samples was lowest Mortality was arcsine transformed and compared (0.01 per fruit) in Orland (11 December) and highest among the different treatments using a one-way (2.21 per fruit) in San Diego (5 October). Parasitism was ANOVA, and TukeyÕs test (GraphPad Software 2007). lowest (0.3%) in postrelease fruit collected in Sylmar (25 January). In Cayucos, a total of 350 parasitoids were collected from postrelease fruit collected on 26 October Results exceeding the calculated number of third instars per fruit Field Release and Recovery of P. humilis. Olive fruit and parasitism was reported as 100% in all replicate fruit ßy adult trap captures at six release sites in California samples.

Table 3. Number and dates P. humilis released, mean (؎SEM) no. of fruit and olive fruit fly emerged, estimated third instars exposed to parasitoids, and percentage parasitism of third instars at six sites from Oct. 2006 to Jan. 2007

Prerelease olive fruit ßy No. Total % Parasitism Release Postrelease reared Location parasitoids No. fruit P. humilis of olive fruit date sample date Third instars released Total reared ßy third instar per fruit Orland 9 Nov. 5,063 11 Dec. 267 Ϯ 4 22.5 Ϯ 13.5 0.01 Ϯ 0.0 1.0 Ϯ 1.0 36.9 Ϯ 36.9 San Juan Bautista 17 Oct. 3,687 23 Oct. 332 Ϯ 72 103.3 Ϯ 28.5 0.05 Ϯ 0.03 6.7 Ϯ 3.4 26.0 Ϯ 15.3 Cayucos 19 Oct. 5,420 26 Oct. 337 Ϯ 42 107 Ϯ 34.6 0.08 Ϯ 0.02 87.5 Ϯ 18.0 100.0 Ϯ 0.0 Santa Barbara 26 Oct. 5,850 3 Nov. 418 Ϯ 30 185.2 Ϯ 16.6 0.52 Ϯ 0.08 39.0 Ϯ 13.3 18.7 Ϯ 6.7 Sylmar 17 Nov. 7,823 1 Dec. 280 Ϯ 20 95 0.22 Ϯ 0.00 0.5 Ϯ 0.5 0.8 Ϯ 0.8 1 Dec. 5,103 8 Dec. 324 Ϯ 27 577.2 Ϯ 75.7 0.54 Ϯ 0.14 9.0 Ϯ 4.0 5.6 Ϯ 3.0 8 Dec. 5,528 15 Dec. 194 Ϯ 16 542.8 Ϯ 96.0 0.57 Ϯ 0.11 10.5 Ϯ 4.3 10.2 Ϯ 4.2 15 Dec. 5,587 25 Jan. 289 Ϯ 34 283.5 Ϯ 69.1 0.56 Ϯ 0.17 1.0 Ϯ 0.4 0.3 Ϯ 0.3 San Diego 5 Oct. 3,613 2 Nov. 108 Ϯ 14 1,084 Ϯ 98.2 2.21 Ϯ 0.51 0 0 2 Nov. 5,372 9 Nov. 1,142 Ϯ 16 881.5 Ϯ 27.5 0.20 Ϯ 0.01 323 Ϯ 139 90.9 Ϯ 9.1 320 ENVIRONMENTAL ENTOMOLOGY Vol. 40, no. 2

Table 4. Comparison of mean (؎SEM) survival (d) of P. humilis Table 5. Mean (؎SEM) mortality of female parasitoids exposed adults reared from olive fruit fly or Medfly under various food to artificial honeydew or GF-120 bait spray in four types of choice conditions tests

Host % Food Test Treatment Olive fruit ßy Medßy Mortality Ϯ No-choice ArtiÞcial honeydew 49.9 Ϯ 8.2a None 11.0 1.1a Ñ Ϯ Cut olive fruit 7.6 Ϯ 0.5a Ñ No-choice GF-120 32.4 9.5a Ϯ Ϯ Separated-choice ArtiÞcial honeydew ϩ GF-120 35.6 Ϯ 9.0a Orange juice 31.0 4.5bc 30.8 1.3a ϩ Ϯ Honey 35.8 Ϯ 4.4c 34.0 Ϯ 5.4a Mixed-choice ArtiÞcial honeydew GF-120 21.5 6.2a Scale honeydew 28.0 Ϯ 3.7b 34.2 Ϯ 3.5a Means within a column followed by the same letter are not signif- Ͼ Means within a column followed by the same letter are not signif- icantly different (P 0.05). icantly different (P Ͼ 0.05, TukeyÕs test). was provided. Provision of honey and honeydew signif- Parasitoid Longevity in Response to Food Source. icantly increased the longevity of females (F ϭ 24.79; At 24ЊC, parasitoids reared from olive fruit ßy and df ϭ 3, 76; P Ͻ 0.001) and males (F ϭ 15.67; df ϭ 3, 76; provided with water survived the longest (36 d) on P Ͻ 0.01). No difference was observed in parasitoid honey for food (Table 4) under constant laboratory longevity between no food versus water only, or be- temperatures. Mean survival on honey was similar to tween honeydew versus honey. orange juice (31 d) and honeydew (28 d) and sig- The life-time fecundity of P. humilis was signiÞ- niÞcantly higher than on cut olive fruit and no food cantly different among water and food sources (F ϭ or water (F ϭ 18.09; df ϭ 4, 17; P ϭϽ0.0001). 20.40; df ϭ 3,76; P Ͻ 0.001) (Fig. 2B). Parasitoid fe- Survival of parasitoids reared on Medßy ranged cundity was increased when females were provided from 31 d on orange juice to 34 d on honey and with water, honeydew and honey versus no food, and honeydew. with honey versus honeydew treatments. Parasitoid Longevity and Fecundity in Response to Parasitoid Response to GF-120 Fruit Fly Baiting. a High Diurnal Temperature Regime and Food Percent mortality of P. humilis adults was not signif- Source. At a high diurnal temperature regime (18.3Ð icantly different (F ϭ 1.94; df ϭ 3, 31; P ϭ 0.144) among 35ЊC), longevity of P. humilis was signiÞcantly different the four choice tests with artiÞcial honeydew and among different food or water provision treatments (F ϭ GF-120 (Table 5). 39.70; df ϭ 7, 152; P Ͻ 0.001), but not between sexes (F ϭ ϭ ϭ 3.35; df 7, 152; P 0.069) or between food source and Discussion sexes (F ϭ 0.45; df ϭ 7, 152; P ϭ 0.713) (Fig. 2A). The parasitoids survived Ͻ5 d when no food or only water Our results showed highly variable captures of adult olive fruit ßies at six different Þeld release sites. In some sites a higher number of captures seemed to be related to favorable temperatures but not so in other sites. For example, 20Ð25 ßies were captured per day per trap when temperature ranged from 19 to 21ЊCin San Juan Bautista, Sylmar, and Santa Barbara. How- ever, in Cayucos only 6.6 ßies were captured even under warm temperatures and moderate humidities. The high variability in adult captures may be affected by many factors, and each release is unique in terms of geography, climatic conditions, and habitat types. Thus, the six locations we selected for Þeld releases of P. humilis cover the diverse olive growing regions in California where olive fruit are produced either pri- marily for oil in coastal areas (San Juan Bautista, Cayu- cos, Santa Barbara, and San Diego), or canned fruit in inland valleys (Orland and Sylmar). Although the difference in habitat types among these release sites, P. humilis were consistently recov- ered within the same fruit season after the release of the parasitoid, with the exception of one release in San Diego. Inability to recover the parasitoid in San Diego after the 5 October release was likely related to the Fig. 2. Longevity (A) and fecundity (B) of P. humilis low number of parasitoids being released at this site under a high diurnal temperature regime (18.5Ð35ЊC) and and the relatively large release area (10 trees) when different water and food sources. Bars are mean (ϮSEM) and compared with other locations. In addition, the post- different letters over the bars indicate signiÞcant differences release sample was collected on 2 November, that is, (P Ͻ 0.05, TukeyÕs test). ϳ1 mo later when the parasitized larvae could have April 2011 YOKOYAMA ET AL.: PARASITOID RESPONSE TO HOST AND FIELD CONDITIONS 321 exited from the fruit for pupation, or the second gen- leased in different types of olive trees, at different eration had not emerged in the Þeld. In Orland, the times in different sites that varied in location size, tree parasitoids were recovered even at an extremely low size, fruit load, fruit maturity, and other factors. Num- host density and low temperatures. Furthermore, the bers of P. humilis released was based on parasitoids olive cultivar in Orland was Ascolano that is a large- shipped and mortality after arrival. The complexity of size fruit and reported by Wang et al. (2009c, d) to parasitoid-host-weather Þeld relationships in this impede parasitism. These results suggest that P. hu- study lacks predictability and in the absence of inde- milis can be used for biological control of the pest in pendent measurements the data does not lend itself to many diverse olive growing regions in California. further analysis especially in relation to laboratory test P. humilis had been released in California in 2002 results under controlled conditions. Analysis of pos- (Yokoyama et al. 2008a) and in 2005 (Yokoyama et al. sible relationships between host abundance or para- 2008b) for control of olive fruit ßy. In general, more sitism and environmental factors may be more appro- parasitoids were released on each release date in this priate for studies conducted in a relatively controlled study than previously done before 2006 at various agricultural crop system. However, quantitative stud- locations in California. From 2008Ð2009, P. humilis ies were only possible with cage tests and this has been rearing procedures were changed in the biological done (Wang et al. 2010) showing parasitism was lower control laboratory in Guatemala. The parasitoid was in large than small fruit, and high temperature and low mass reared on irradiated Medßy larvae to reduce the humidity in the summer reduced parasitism. risk of fertile adults in shipments, and imported and Parasitoids rely on food for survival (Yokoyama et released in high numbers (Yokoyama et al. 2010). In al. 2008). As expected, orange juice and scale honey- the same study, rearing P. humilis on irradiated Medßy dew could sustain the longevity of P. humilis and did not affect parasitoid Þtness based on fecundity and longevity of the parasitoid feeding on these two food ßight tests. Although fruit infested with olive fruit ßy sources was similar to those feeding on honey, regard- was available in the release years of October 2006 to less if the parasitoids were reared from Medßy or olive January 2007 (Table 3) and 2008Ð2009 in the Orland, fruit ßy. Two different honeydews, produced by ei- Cayucos, and San Diego release sites, rates of parasit- ther soft brown scale or black scale, respectively, were ism in the latter study were lower and ranged from 0 tested in this study. Ewart and Metcalf (1956) com- in Orland to 7.6 in Cayucos. Releasing greater num- pared these honeydews between the species and bers of parasitoids in 2008Ð2009 did not improve cal- found no differences in the composition of sugars or culated rates of parasitism. However, the only report amino acids. The species of leaf on which the honey- of recaptures of P. humilis that may have resulted in dew was presented, F. benjamina versus O. europaea, prior year releases was by Yokoyama et al. (2009). One probably did not affect the behavior of the parasitoid adult of P. humilis was recovered from fruit infested because survival on honeydew was comparable to with olive fruit ßy in October 2006 in San Jose after honey in all tests. Sivinski et al. (2006) found that another multiple releases of 2,587; 3,600; 4,630; 3,655; and 5,089 fruit ßy parasitoid Diachasminorpha longicaudata (Ash- parasitoids and subsequent rates of 0.6, 0.5, 0.7, 3.6% mead) had similar longevities on homopteran honey- parasitism in November to December 2005. dew, extraßoral nectary secretions, and honey, and was Multiple parasitoid releases were conducted in Syl- able to sustain their longevity by feeding on fruit juice or mar (Table 3) with the intent to permanently establish pulp. In related studies, Bautista et al. (2001) found that P. humilis on olive fruit ßy at this location. Low numbers females of the egg parasitoid Fopius arisanus (Sonan) of olive fruit ßy persisted in the fruit from November to lived longer when fed honey, and discussed the use of December and the parasitoid was recaptured in postre- sugars as potential food supplements in the Þeld to sus- lease fruit samples during this period. However, the work tain parasitoid effectiveness. In California, olives was discontinued in January because mid-month freez- may be grown in proximity to citrus orchards. The ing conditions throughout the state caused the fruit to black scale is common throughout the coastal and drop from the trees. Freezing conditions may have Central Valley of California (Daane et al. 1991). The caused high mortality of immature parasitoids develop- current study suggests that those natural food ing in the host resulting in low calculated rates of para- sources may improve the parasitoid survival in the sitism on the last postrelease sample date. Þeld after being released. As previous studies, a relationship was not observed Our laboratory studies also showed that high sum- between host ßy density per fruit and percentage mer temperatures that reßect the San Joaquin Valley parasitism (Table 3). For example, in Cayucos and San summer conditions (Johnson et al. 2006) could sig- Diego (5 October) the mean numbers of third instars niÞcantly reduce the longevity of P. humilis without per fruit was 0.08 and 2.21, but the mean rates of water or food. However, when adequate food sources parasitism were 100 and 0%, respectively. Many fac- are available, the parasitoid could still produce F1 tors, other than host ßy density, could have affected progeny. Therefore, the availability of food is key for the observed parasitism. These factors may include survival and reproduction of the parasitoids under release site size, tree size, fruit size (varied even within adverse climate conditions, and also applies to the host the same cultivar, Wang et al. 2009d), fruit load, num- ßy (Wang et al. 2009a,b). Therefore, our laboratory ber of parasitoids released, sample size, and microcli- studies suggest that parasitism or recovery of the para- mates in the vicinity of trees where parasitoids have sitoid could be affected not only by temperature con- been released. In this study, the parasitoids were re- dition but also the availability of food sources in the 322 ENVIRONMENTAL ENTOMOLOGY Vol. 40, no. 2

Þeld. However, the availability of food sources could (Diptera: Tephritidae) captures in several commercial be quite different at different release sites, and this traps in California. Int. J. Pest Manage. 54: 227Ð234. may partly explain the large variation of parasitism Byrne, D. N., D. L. Hendrix, and L. H. Williams. 2003. among different sites. For example, the highest per- Presence of trehalulose and other oligosaccharides in centage parasitism in Cayucos could contribute to the hemipteran honeydew, particularly Aleyrodidae. Physiol. most suitable temperature condition but also the pos- Entomol. 28: 144Ð149. Clausen, C. 1978. Introduced parasites and predators of ar- sibility that the parasitoids may have readily located thropod pests and weeds: a world review. United States food and survived throughout the exposure period. Department of Agriculture, Agriculture Handbook No. This further limits our ability to predict Þeld parasit- 480, Washington, DC. ism. Collier, T. R., and R. A. van Steenwyk. 2003. Prospects for The current study shows that a brief exposure to integrated control of olive fruit ßy are promising in Cal- GF-120 for 2 h did not cause a signiÞcantly higher ifornia. Calif. Agric. 57: 28Ð31. mortality of P. humilis when compared with artiÞcial Daane, K. M., M. S. Barzman, C. E. Kennett, and L. E. honeydew. However, several other laboratory studies Caltagirone. 1991. Establishment of Prococcophagus pro- showed low adult survival after direct contact to GF- bus Annecke and Mynhardt and Coccophagus rusti Com- 120 for the fruit ßy parasitoids Psyttalia fletcheri Sil- pere (Hymenoptera: ): parasitoids of black scale in California. Pan-PaciÞc Entomol. 67: 99Ð106. vestri, Fopius arisanus (Sonan), and Daane, K. M., and M. W. Johnson. 2010. Olive fruit ßy: tryoni (Cameron) (Wang et al. 2005), and D. longi- managing an ancient pest in modern times. Annu. Rev. caudata (Ruiz et al. 2008). Parasitoids are not attracted Entomol. 55: 155Ð169. to GF-120 or directly fed on GF-120, but are observed El-Heneidy, A. H., A. H. Omar, H. El-Sherif, and M. A. to be trapped in the bait solution that leads to a direct El-Khawas. 2001. Survey and seasonal abundance of the body contact with GF-120 and consequently mortality parasitoids of the olive fruit ßy, Bactrocera (Dacus) oleae (Wang et al. 2005). The current study further suggests Gmel. (Diptera: Trypetidae) in Egypt. Arab J. Prot. that P. humilis does not feed on GF-120 that supports 19: 80Ð85. use of the parasitoid in olive integrated pest manage- Ewart, W. H., and R. L. Metcalf. 1956. Preliminary studies ment programs that recommend the use of GF-120 for of sugars and amino acids in the honeydews of Þve species of coccids feeding on citrus in California. Ann. Entomol. control of olive fruit ßy, although repeat application of Soc. Am. 49: 441Ð447. GF-120 in orchards may contaminate honeydew; re- Gomez-Caravaca, A. M., L. Cerretani, A. Bendini, A. Segura- ducing the availability of natural food sources for nat- Carretero, A. Fernandez-Gutierrez, M. Del Carlo, D. ural enemies in ecosystems. Compagnone, and A. Cichelli. 2008. Effects of ßy attack (Bactrocera oleae) on the phenolic proÞle and selected chemical parameters of olive oil. J. Agric. Food Chem. 56: Acknowledgments 4577Ð4583. GraphPadSoftware. 2007. GraphPad Prism, version 5.00. We are grateful to Gina T. Miller and Gail E. Sergent, GraphPad Software, San Diego, CA, computer program, USDA-ARS, San Joaquin Valley Agricultural Sciences Cen- version By GraphPadSoftware. ter, Parlier, CA; Miguel Lopez and Alicia Aldana, USDA- Johnson, M. W., F. G. Zalom, R. Van Steenwyk, P. Vossen, APHIS-PPQ, Moscamed Program, Guatemala City, Guate- A. K. Devarenne, K. M. Daane, W. H. Krueger, J. H. mala; Martha Gerik, University of California Kearney Connell, V. Yokoyama, B. Bisabri, J. Caprile, and J. Nel- Agricultural Center, Parlier, CA; Melanie Durbin, California son. 2006. Olive fruit ßy management guidelines for State University, East Bay, Hayward, CA; and Barat Bisabri, 2006. UC Plant Prot. Q. 16: 1Ð7. Dow AgroSciences, Orinda, CA, for their assistance; Bill Kakani, E. G., N. E. Zygouridis, K. T. Tsoumani, N. Seraphi- Krueger, Orland, CA; Mission San Juan Batista, CA; Steve des, F. G. Zalom, and K. D. Mathiopoulos. 2010. Spi- Martin, Cayucos, CA; Mike Fusano, Sylmar, CA; Gebb Tur- nosad resistance development in wild olive fruit ßy Bac- pin, Santa Barbara, CA; and Ross Rizzo, Rancho Bernardo trocera oleae (Diptera: Tephritidae) populations in Winery, Rancho Bernardo, California for use of their olive California. Pest Manage. Sci. 66: 447Ð453. orchards for this project. This research was funded in part by Kapatos, E., B. S. Fletcher, S. Pappas, and Y. 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