Occurrence, Seasonal Abundance, and Superparasitism of Ooencyrtus kuvanae (Hymenoptera: Encyrtidae) as an Egg Parasitoid of the Spotted Lanternﬂy ( Lycorma delicatula ) in North America

: The occurrence of egg parasitoid Ooencyrtus kuvanae (Howard) (Hymenoptera: Encyrtidae) on its new host, the spotted lanternﬂy ( Lycorma delicatula (White) (Hemiptera: Fulgoridae)), was surveyed at 4 study plots in 2016 and 10 additional plots in 2017 in Pennsylvania through ﬁeld collection and laboratory incubation. O. kuvanae adults were found on L. delicatula egg mass surfaces at two plots (ODSouth and Lutz) in 2016, but at none in 2017. The results of laboratory incubation showed that O. kuvanae adults were only recovered from host eggs collected at plot ODSouth in 2016, with adults emerging between 22 April and 2 May 2016 at 22 ± 1 ◦ C, 40% ± 5% relative humidity (RH), and a 16:8 h photoperiod (light/dark). The overall parasitism at this study plot was 6.0% by egg mass and 1.2% by egg. Two oviposition sites contained parasitized L. delicatula eggs, with 12.3% (9.5–15.0%) host egg masses and 3.1% (1.3–5.0%) host eggs utilized by the parasitoid. parasitism by egg was signiﬁcantly higher on oviposition site ODSouth #7 than on ODSouth #8. No O. kuvanae adults were reared out of ﬁeld-collected host eggs from the 10 plots in 2017. Seasonal abundance and superparasitism of O. kuvanae was examined at plot ODSouth in 2017. O. kuvanae -parasitized L. delicatula eggs were found on all four oviposition sites based on ﬁeld monitoring of parasitoid adult emergence, resulting in a parasitism of 35.4% (18.8–55.6%) by egg mass and 2.2% (0.5–3.9%) by egg. No signiﬁcant difference in parasitism by egg was observed among oviposition sites. O. kuvanae adults emerged in the ﬁeld between 2 May and 1 June 2017. Superparasitism was conﬁrmed for O. kuvanae on L. delicatula eggs based on parasitoid production (1.0–3.3 adults/parasitized egg) and adult exit holes (1–3 exit holes/parasitized egg). As the ﬁrst parasitoid recorded from L. delicatula in North America, O. kuvanae has the potential to become an important biological control agent for L. delicatula in North America, with its well-synchronized life history in the spring, century-long ﬁeld establishment, superparasitism, and female-biased progeny population. L. delicatula complements the gypsy moth well as an alternative host for O. kuvanae in the ﬁeld.


Introduction
The spotted lanternfly, Lycorma delicatula (White) (Hemiptera: Fulgoridae), a sporadic pest of tree-of-heaven, Ailanthus altissima (Mill.) Swingle (Simaroubaceae), in its native range of China, Taiwan, and Vietnam [1][2][3][4], was first discovered in North America near Boyertown (40.33366 N, 75.63744 W) in Berks county, Pennsylvania, in 2014 [5,6]. It is now found in multiple counties in Pennsylvania, Virginia, Pennsylvania, Virginia, New Jersey, New York, and Delaware [7][8][9][10][11]. Recorded host species include more than 70 woody plants and vines in 25 families, such as grape, apple, hops, birch, cherry, lilac, maple, poplar, and stone fruits [3,6,12]. Both nymphs and adults feed on phloem tissue that causes oozing wounds on trunks and branches, resulting in wilting or the death of branches under high pest population levels. Large amounts of honeydew are excreted and deposited on host trees and the understories during feeding, promoting the growth of sooty mold that hinders plant photosynthesis and contaminates agricultural and forest crops [4,5]. Mold-contaminated crops are deemed unmarketable. Significant damage has been recorded in vineyards in Korea since its initial introduction in 2004 [4,13,14]. In Pennsylvania, this invasive insect pest is directly threatening the state's $18-billion fruits, nursery and landscape, and hardwood industries. Profound impacts are also expected on the livelihoods of local producers and businesses and the quality of life of the residents in the infested areas [15].
In China, L. delicatula completes one generation per year and overwinters as eggs on tree trunks, rocks, or man-made structures nearby. Eggs start to hatch in mid-April with a peak in early May. Nymphs pass through four instars to become adults between mid-June and early July. Adults mate and lay eggs in mid-August. Eggs are laid in masses arranged in 5-10 rows with 10-30 eggs/row and covered by gray wax. Both nymphs and adults are good hoppers that aggregate on leaves and tree trunks [3]. In Korea, nymphs appear in May and develop into adults in late July, with egg laying starting in August and lasting until early November [14,16]. A similar life cycle has also been observed in Pennsylvania for this pest, except eggs did not appear in the field until mid-October [6].
Ooencyrtus kuvanae (Howard) (Hymenoptera: Encyrtidae) is a solitary egg parasitoid of the gypsy moth (Lymantria dispar (L.) (Lepidoptera: Erebidae)) from Japan [17]. Other lepidopteran hosts in the field for this parasitoid in its native range include Dendrolimus spectabilis Butler (Lasiocampidae) [18] and Eriogyna pyretorum Westwood (Saturniidae) [19]. As a hyperparasitoid, it also attacks gypsy moth egg parasitoid Anastatus disparis Ruschka (Hymenoptera: Eupelmidae) and larval parasitoid Apanteles melanoscelus Ratzeburg (Hymenoptera: Braconidae) [20,21].   Pennsylvania, Virginia, New Jersey, New York, and Delaware [7][8][9][10][11]. Recorded host species include more than 70 woody plants and vines in 25 families, such as grape, apple, hops, birch, cherry, lilac, maple, poplar, and stone fruits [3,6,12]. Both nymphs and adults feed on phloem tissue that causes oozing wounds on trunks and branches, resulting in wilting or the death of branches under high pest population levels. Large amounts of honeydew are excreted and deposited on host trees and the understories during feeding, promoting the growth of sooty mold that hinders plant photosynthesis and contaminates agricultural and forest crops [4,5]. Mold-contaminated crops are deemed unmarketable. Significant damage has been recorded in vineyards in Korea since its initial introduction in 2004 [4,13,14]. In Pennsylvania, this invasive insect pest is directly threatening the state's $18-billion fruits, nursery and landscape, and hardwood industries. Profound impacts are also expected on the livelihoods of local producers and businesses and the quality of life of the residents in the infested areas [15].
In China, L. delicatula completes one generation per year and overwinters as eggs on tree trunks, rocks, or man-made structures nearby. Eggs start to hatch in mid-April with a peak in early May. Nymphs pass through four instars to become adults between mid-June and early July. Adults mate and lay eggs in mid-August. Eggs are laid in masses arranged in 5-10 rows with 10-30 eggs/row and covered by gray wax. Both nymphs and adults are good hoppers that aggregate on leaves and tree trunks [3]. In Korea, nymphs appear in May and develop into adults in late July, with egg laying starting in August and lasting until early November [14,16]. A similar life cycle has also been observed in Pennsylvania for this pest, except eggs did not appear in the field until mid-October [6].
Ooencyrtus kuvanae (Howard) (Hymenoptera: Encyrtidae) is a solitary egg parasitoid of the gypsy moth (Lymantria dispar (L.) (Lepidoptera: Erebidae)) from Japan [17]. Other lepidopteran hosts in the field for this parasitoid in its native range include Dendrolimus spectabilis Butler (Lasiocampidae) [18] and Eriogyna pyretorum Westwood (Saturniidae) [19]. As a hyperparasitoid, it also attacks gypsy moth egg parasitoid Anastatus disparis Ruschka (Hymenoptera: Eupelmidae) and larval parasitoid Apanteles melanoscelus Ratzeburg (Hymenoptera: Braconidae) [20,21].   [3,6,12]. Both nymphs and adults feed on phloem tissue that causes oozing wounds on trunks and branches, resulting in wilting or the death of branches under high pest population levels. Large amounts of honeydew are excreted and deposited on host trees and the understories during feeding, promoting the growth of sooty mold that hinders plant photosynthesis and contaminates agricultural and forest crops [4,5]. Mold-contaminated crops are deemed unmarketable. Significant damage has been recorded in vineyards in Korea since its initial introduction in 2004 [4,13,14]. In Pennsylvania, this invasive insect pest is directly threatening the state's $18-billion fruits, nursery and landscape, and hardwood industries. Profound impacts are also expected on the livelihoods of local producers and businesses and the quality of life of the residents in the infested areas [15].
In China, L. delicatula completes one generation per year and overwinters as eggs on tree trunks, rocks, or man-made structures nearby. Eggs start to hatch in mid-April with a peak in early May. Nymphs pass through four instars to become adults between mid-June and early July. Adults mate and lay eggs in mid-August. Eggs are laid in masses arranged in 5-10 rows with 10-30 eggs/row and covered by gray wax. Both nymphs and adults are good hoppers that aggregate on leaves and tree trunks [3]. In Korea, nymphs appear in May and develop into adults in late July, with egg laying starting in August and lasting until early November [14,16]. A similar life cycle has also been observed in Pennsylvania for this pest, except eggs did not appear in the field until mid-October [6].
Ooencyrtus kuvanae (Howard) (Hymenoptera: Encyrtidae) is a solitary egg parasitoid of the gypsy moth (Lymantria dispar (L.) (Lepidoptera: Erebidae)) from Japan [17]. Other lepidopteran hosts in the field for this parasitoid in its native range include Dendrolimus spectabilis Butler (Lasiocampidae) [18] and Eriogyna pyretorum Westwood (Saturniidae) [19]. As a hyperparasitoid, it also attacks gypsy moth egg parasitoid Anastatus disparis Ruschka (Hymenoptera: Eupelmidae) and larval parasitoid Apanteles melanoscelus Ratzeburg (Hymenoptera: Braconidae) [20,21].  In China, L. delicatula completes one generation per year and overwinters as eggs on tree trunks, rocks, or man-made structures nearby. Eggs start to hatch in mid-April with a peak in early May. Nymphs pass through four instars to become adults between mid-June and early July. Adults mate and lay eggs in mid-August. Eggs are laid in masses arranged in 5-10 rows with 10-30 eggs/row and covered by gray wax. Both nymphs and adults are good hoppers that aggregate on leaves and tree trunks [3]. In Korea, nymphs appear in May and develop into adults in late July, with egg laying starting in August and lasting until early November [14,16]. A similar life cycle has also been observed in Pennsylvania for this pest, except eggs did not appear in the field until mid-October [6].
O. kuvanae was first introduced to the Unites States in 1908 for gypsy moth biological control [22]. The gypsy moth is native to most of temperate Europe and Asia. It was accidentally introduced to Massachusetts in 1869. By the 1930s, it was widespread in all six New England states (Maine, Vermont, New Hampshire, Massachusetts, Connecticut, and Rhode Island), as well as in eastern New York and regions of New Jersey [23]. The successful establishment of O. kuvanae was first achieved in Massachusetts in 1911 [24]. Since then, millions of O. kuvanae have been reared and released throughout the areas infested by gypsy moths in North America [25]. The release and subsequent recovery of O. kuvanae in Pennsylvania occurred between 1969 and 1971 [26]. In 2016, O. kuvanae was confirmed as an egg parasitoid of L. delicatula based on genetic and morphological features of adults collected from the field as well as reared out of host eggs in the laboratory [27]. This was the first report of O. kuvanae as a primary parasitoid of a non-lepidopteran host.
Superparasitism refers to the oviposition behavior of a female parasitoid in a host already parasitized by itself (self-superparasitism) or a conspecific female (conspecific superparasitism) [28][29][30][31][32]. It is an adaptive reproductive strategy commonly found in both solitary and gregarious parasitoids when multiple parasitoid progenies are found in a single host. The incidence of superparasitism for O. kuvanae was recently reported on Philosamia ricini Donovan (Lepidoptera: Saturniidae) under laboratory conditions [33]. This phenomenon was also reported for O. kuvanae on field-collected gypsy moth larval parasitoid A. melanoscelus pupae [20] and laboratory-reared pine tussock moth Dasychira pinicola Dyar (Lepidoptera: Erebidae) eggs [34], although the term "superparasitism" was not used in those publications.
In this study, the occurrence of O. kuvanae as an egg parasitoid of L. delicatula was surveyed at multiple field plots over two years. Its seasonal abundance was monitored through laboratory incubation of parasitized host eggs and field observation of marked host eggs. Evidence of superparasitism was examined through parasitoid production and adult exit holes on host eggs after laboratory incubation.

Egg Collection
Field sampling was carried out between the end of March and mid-April to ensure overwintering O. kuvanae adults were active and had the chance to parasitize L. delicatula eggs in the field. Egg collection in 2016 was conducted at four plots (Rolling, ODSouth, Rock, and Lutz) between 30 March and 6 April. At each plot, potential L. delicatula oviposition sites (trunks of live or dead trees, shrubs, vines, rocks, fence posts, building structures, etc.) were searched for egg masses. Egg masses found on low 2-m tree trunks or vines and shrubs were collected using a 1.27-cm (1/2-inch) bench chisel (Buck Brothers, Everett, WA). To collect egg masses on bark, two direct cuts, one 5 mm above and one 5 mm beneath them, were first created. The egg masses were then dislodged by gently pushing the chisel under the bark upwards from the lower end. Care was taken to make sure no eggs were accidentally missed, cut, squeezed, or otherwise damaged. Egg masses found on other oviposition sites (rocks, fence posts, building structures) were gently removed from beneath with a pair of 118-mm blunt featherweight forceps (BioQuip, Rancho Dominguez, CA). Each dislodged egg mass was held inside a 100-mm petri dish (VWR International, Radnor, PA) before being transferred into a 16-mL borosilicate clear glass vial with a black phenolic cap (Fisher Scientific, Hampton, NH). Egg masses were held individually in the vials and labeled by plot name, oviposition site number, and egg mass number (e.g., ODSouth #7-2 represented the second egg mass collected from oviposition site No. 7 at plot ODSouth). A total of six man-hours (three skilled surveyors for two hours) was spent to collect L. delicatula egg masses at each plot. No egg masses from chemically treated tree-of-heaven trees were collected.

Occurrence of O. kuvanae
Occurrence of O. kuvanae was observed through field collections and laboratory rearing between 2016 and 2017. In the field, during egg collection at the 14 plots, L. delicatula oviposition sites were examined for potential egg parasitoid adults. Parasitic wasps found actively searching and probing on the surface of L. delicatula egg masses were collected and brought back to the laboratory for identification. In addition, field-collected L. delicatula eggs were incubated in the laboratory for   O. kuvanae parasitism was calculated by egg mass (number of egg masses parasitized/total number of egg masses) and egg (number of eggs parasitized/total number of eggs) for plot ODSouth only, since no parasitoid adults were reared out of L. delicatula eggs collected from other plots. Parasitism was also calculated by egg mass and egg for individual oviposition site at this plot. Oviposition sites containing no parasitized L. delicatula eggs were excluded from parasitism calculation to simplify data analysis. Parasitism in 2016 was based on laboratory incubation of parasitized L. delicatula eggs, whereas parasitism in 2017 was calculated based on observation of parasitoid emergence from L. delicatula eggs on oviposition sites in the field.

Superparasitism in O. kuvanae
To determine whether superparasitism occurred for O. kuvanae on L. delicatula, field-collected host eggs were examined under a dissecting scope for parasitoid adult emergence and number of exit holes on each parasitized host egg. The number of O. kuvanae adults emerged, the number of host eggs parasitized for each egg mass, and the number of parasitoid exit holes on each parasitized host egg were recorded. Superparasitism occurred when the total number of O. kuvanae obtained from a host egg mass was greater than the total number of parasitized host eggs in it. Evidence of superparasitism was further examined by parasitoid exit holes registered on each parasitized egg. Multiple parasitoid exit holes on a single host egg indicated multiple adult emergences and hence superparasitism.

Identification of O. kuvanae
Adult specimens were initially identified by Dr. Jason Mottern (USDA ARS Systematic Entomology Laboratory, Washington, DC, USA) using the key to species in Huang and Noyes [35]. This identification was further confirmed by morphological comparison with O. kuvanae specimens in the United States National Museum of Natural History (USNM) collection and the results of gene sequencing [27]. Images were also sent to Dr. John Noyes at the Natural History Museum, London, who concurred with the initial identification. All specimens were deposited in the USNM and DCNR Entomology Collection.

Data Analysis
A generalized linear model (GLM) with a binomial distribution was fitted in R to examine the effect of oviposition site on O. kuvanae parasitism by egg [36]. No comparison on parasitism was made between years since different sampling methods were used.

Egg Collection
A total of 663 L. delicatula egg masses (22,202 eggs) were collected from 208 oviposition sites for this study over two years, including 262 egg masses (8282 eggs) from 97 oviposition sites at 4 study plots in 2016 and 401 egg masses (13,920 eggs) from 111 oviposition sites at 10 study plots in 2017 (Table 1). L. delicatula egg masses were found on all sorts of oviposition sites, including various live and dead trees, shrubs, building structures, fence posts, rocks, etc. Major oviposition sites for L. delicatula recorded at each plot ranged from tree-of-heaven (Lutz, Straub, Conrad, Kulps, Huffs, and HCWest) to black birch (Rolling and Nuss), black cherry (ODSouth and HCEast), yellow birch (Rock), tulip trees (ODNorth), sweet cherry (WSWest), and even metal fence posts (WSEast) ( Table 1). Tree-of-heaven was found in all study plots either as single trees, in pockets, or scattered in the woods. Dominant tree species at each study plot were not necessarily the most used oviposition sites by L. delicatula females, although tree-of-heaven would have been preferred if the majority of them were not preemptively excluded at most plots due to chemical or mechanical control (Table 1). Mechanical and chemical control of tree-of-heaven was implemented as part of L. delicatula management at all but two of the study plots (Table 1). a "Pockets" is defined as groups of at least five mature tree-of-heaven trees at each location inside the mixed hardwood forest, whereas "scattered" refers to single tree-of-heaven trees found throughout the forest. b Chemical: Triclopyr through hack-and-squirt (large trees) or spray (small trees); mechanical: Felling and chipping trees.

Occurrence of O. kuvanae
The results of the field collections indicated that O. kuvanae presented at two of the four study plots in 2016. A total of 33 adults were collected on the surface of L. delicatula egg masses in 2016, O. kuvanae adults were recovered from L. delicatula eggs collected at plot ODSouth based on laboratory incubation in 2016. A total of 83 egg masses (3103 eggs) were collected from nine oviposition sites at this plot (Table 1). However, O. kuvanae was only recovered from two oviposition sites ( Table 2). Five of the 41 egg masses (1507 eggs) from those two sites were parasitized, including 3 out of the 20 egg masses from oviposition site ODSouth #7 and 2 out of the 21 egg masses from oviposition site ODSouth #8 (Table 2). Among the 186 total eggs from those five parasitized egg masses, 37 eggs were utilized by O. kuvanae, including 28 from oviposition site ODSouth #7 and 9 from oviposition site ODSouth #8 (Table 2).
No O. kuvanae adults were found at the 10 plots in 2017 through field collections. No O. kuvanae adults were recovered from field-collected L. delicatula eggs at any plot either based on the results of laboratory incubation in 2017.
For the 41 egg masses (1726 eggs) on 4 oviposition sites monitored at study plot ODSouth in 2017, O. kuvanae adult exit holes were found on 13 of them, including 3 out of 16 from oviposition site A, 3 out of 11 from oviposition site B, 5 out of 9 from oviposition site C, and 2 out of 5 from oviposition site D (Table 2). A total of 37 L. delicatula eggs were parasitized from those 13 egg masses (containing a combined total of 634 eggs), with the highest number of parasitized eggs (17) found on oviposition site A, where 3 egg masses were parasitized ( Table 2). A total of 3, 13, and 4 L. delicatula eggs were parasitized on oviposition sites B, C, and D, respectively ( Table 2).

Seasonal Abundance of O. kuvanae
In 2016, O. kuvanae adult emergence started on 22 April and ended on 2 May based on laboratory incubation of field-collected L. delicatula eggs, with three overall peaks on 25 April, 28 April, and 2 May (Figure 2). For L. delicatula egg masses collected from oviposition site ODSouth #7, parasitoid adults emerged between 25 April and 2 May for egg mass ODSouth #7-1, with three peaks on 25 April, 28 April, and 2 May; between 25-28 April for egg mass ODSouth #7-2, with a single peak on 26 April; and on 29 April for egg mass ODSouth #7-6 ( Figure 2). For egg masses collected from oviposition site ODSouth #8, adults emerged between 22 April and 2 May, with two peaks on 22 April and 28 April for egg mass ODSouth #8-2; and between 25 April and 2 May, with a single peak on 25 April for egg mass ODSouth #8-21 ( Figure 2).   (Fig. 3). For egg masses on oviposition site A, parasitoid adults emerged between 2 and 18 May, with three peaks on 2, 11, and 18 May (Figure 3). For egg masses on oviposition site B, adults emerged between 8-11 May, with a single peak on 8 May (Figure 3). For egg masses on oviposition site C, adults emerged between 2-30 May, with three peaks on 2, 11, and 30 May (Figure 3). No significant emergence peak was observed for egg masses on oviposition site D, with an adult emergence period between 2 May to 1 June (Figure 3).

Discussion
The status of L. delicatula as a major forest pest in North America is still under evaluation despite observations of its feeding on other important crops such as apple and hops (so far). Tree-of-heaven, a small-to medium-sized invasive species native to China [37], was first introduced to North America from Europe as an ornamental in 1784 [38]. It is now generally considered to be a noxious plant that is widely distributed across the continent, from southern Ontario to Florida and British Columbia to southern California [39,40]. Any negative impact of L. delicatula on tree-of-heaven could potentially be welcomed in many states. However, it is the feeding of L. delicatula on other major tree species that concerns forest managers and forest health professionals. Feeding damage in the field has been observed on Chinese mahogany (Toona sinensis (A. Juss) M. Roem) in China [41] and on northern red oak, black walnut, silver maple, and bigtooth aspen (Populus grandidentata Michaux) in Pennsylvania [42]. Laboratory rearing results have shown that L. delicatula can develop into adults from first instar nymphs on black walnut, tulip trees, chinaberry (Melia azedarach L.), butternut (Juglans cinerea L.), sawtooth oak (Quercus acutissima Carruth), or weeping willow (Salix babylonica L.), exclusively [41,43]. More species could be added to this list as host range studies continue.
Current management approaches for L. delicatula in Pennsylvania include silvicultural, mechanical, and chemical control [44]. Silvicultural control focuses on host removal through cutting and chipping and herbicide treatment of tree-of-heaven inside the infestation. Chipping infested material into standard one-inch in two-dimension chip sizes in mid-winter destroyed all L. delicatula eggs [45]. Mechanical control targets L. delicatula eggs or nymphs through egg scaping and tree banding. Chemical control is generally used to treat a few trap trees in each management area with systemic insecticides such as dinotefuran and imidacloprid to kill feeding L. delicatula nymphs and adults. While all of them may be effective in localized areas, the long-term management of L. delicatula in North America relies on biological control in the absence of an effective insecticide that can be broadcast over large areas.
The natural enemies of L. delicatula in its native range include Anastatus orientalis Yang and Choi (Hymenoptera: Eupelmidae), a solitary egg parasitoid [46,47]; and Dryinus browni Ashmead (Hymenoptera: Dryinidae), a solitary nymphal ectoparasitoid [48]. Field parasitism in China has ranged from 30.5% to 69.0% (by egg mass) and 33.0% to 40.2% (by egg) for An. orientalis [46,47] and from 12.5% to 43.5% for D. browni, respectively [48]. An unidentified Anastatus species, possibly An. orientalis, was also reported in Korea, where an invasion of L. delicatula occurred in 2004 [49]. In China, an unidentified species of Epipyropidae was recovered from L. delicatula nymphs on traps in the field [41]. An. orientalis is currently being evaluated by USDA researchers as a potential agent for the classical biological control of L. delicatula in North America.
The recently discovered new association between O. kuvanae and L. delicatula could open doors for the biological control of this pest in North America [27]. The new association approach in biological control utilizes natural enemies that have not co-evolved with the pest. It has been considered more effective than the traditional approach (where co-evolved natural enemies are used) by some due to higher host vulnerability to novel agents [50][51][52][53]. O. kuvanae is commonly found on gypsy moth eggs across the eastern United States, exerting a parasitism rate of 10%-40% [25,54]. Factors limiting its efficacy on gypsy moths include high overwintering adult mortality, poor dispersal ability, and a short ovipositor that prevents females from reaching host eggs beyond the upper layer in the egg masses [24,25,55]. In the current study, O. kuvanae adults were collected from L. delicatula egg mass surfaces at two study plots in the field and reared from eggs collected at one study plot in the laboratory in 2016. The overall parasitism on L. delicatula at this site (1.2%) was low compared to that on gypsy moths, although a higher rate was observed on specific egg masses and oviposition sites ( Table 2). Localized high parasitism rates are common for invasive pests by new association native or exotic parasitoids. In Michigan, a native solitary parasitoid, Atanycolus cappaerti Marsh and Strazanac (Hymenoptera: Braconidae), was found to be parasitizing 56%-71% of larvae of the invasive emerald ash borer Agrilus planipennis Fairmare (Coleoptera: Buprestidae) at one plot [56]. In Alabama, an average parasitism rate of 95.6% was observed at a single study plot for Ooencyrtus nezarae Ishii (Hymenoptera: Encyrtidae), a facultative gregarious egg parasitoid from Asia, on the kudzu bug (Megacopta cribraria (F.) (Hemiptera: Plataspidae)) [57]. More exposure of L. delicatula eggs to O. kuvanae over time in the field could result in higher parasitism in the future.
O. kuvanae adult emergence occurred a week after the initial hatching of L. delicatula eggs and lasted for about a month based on the results of laboratory incubation [42]. In the laboratory at 22 ± 1 • C, 40% ± 5% relative humidity, and a photoperiod of 16:8 (light/dark) h, adult emergence occurred between 22 April and 2 May in 2016, with peak emergence on days 3, 8, and 11, respectively ( Figure 2). Similar peak emergence between day 2 and day 9 was also observed for this parasitoid on its substitute host P. ricini when reared at 25 ± 1 • C, 65% ± 5% relative humidity, and a photoperiod of 16:8 (light/dark) in laboratory incubation [58]. A development time from egg to adult of 21 days at 25 • C was recorded on gypsy moths [24], compared to a developmental period of 16.5-18.7 days at the same temperature on P. ricini [58]. Differences in host species and incubation temperatures could explain the discrepancies between different studies.
The results of seasonal abundance studies showed that O. kuvanae synchronized well with overwintering L. delicatula eggs in the field in the spring, with adult emergence observed between 2 May and 1 June in 2017 (Figure 3). L. delicatula egg hatching started on 2 May and ended on 5 June in 2017 [42]. O. kuvanae overwinters as fertilized adult females in forest litter layers and completes at least four generations per year in the field [24]. Females can parasitize infertile, developed, unhatched, or even recently killed gypsy moth eggs [20,59]. They become active in mid-April and lay eggs on overwintering host eggs. Adults of the first spring generation emerge in late May to early June to parasitize suitable unhatched gypsy moth eggs. Adults of the second spring generation appear in July for the new gypsy moth eggs. Parasitoid populations reach peak levels in August and September for the first and second summer generations before declining rapidly toward November as adults prepare to overwinter [24,54,59,60]. Despite obvious similarities in life history traits (e.g., voltinism, overwintering patterns, egg site selection) between L. delicatula and gypsy moths, there are significant differences in metamorphosis, host plants, and egg period that could potentially alter the behavior of O. kuvanae as an egg parasitoid of L. delicatula in North America. Under current conditions, the new L. delicatula eggs laid in October might not be favored by O. kuvanae females as they prepare for overwintering. However, a gradual shift of egg period from October to December [6] to August to October that has been observed in Asia [14,16] could be beneficial to O. kuvanae as an important biological control agent of L. delicatula in North America. Whether this shift will occur remains to be seen. Chances of multiple O. kuvanae generations on L. delicatula in the field will depend on its adaptive response to the biological features of L. delicatula eggs. Periodic sampling on both new and overwintering host eggs from the field could shed more light on this.
Superparasitism was observed for O. kuvanae on L. delicatula eggs based on evidence of average parasitoid production and adult exit holes on single host eggs (Figures 4 and 5). The sex ratio for its offspring was extremely female-biased. It is unclear whether this was self-or conspecific superparasitism and why it occurred on L. delicatula eggs in the field. Self-superparasitism in solitary parasitoids is considered a waste of energy, as only one parasitoid individual survives in the end, whereas conspecific superparasitism can be advantageous under certain circumstances, since non-sibling competitors could be eliminated from parasitized hosts [28]. The benefits of increased numbers of offspring through superparasitism is usually negated by the deleterious effects on progeny fitness (i.e., prolonged development time, a smaller body size, a male-biased sex ratio, and decreased longevity) [28,33,61]. The tendency to superparasitize by parasitoids is largely determined by female age and host density, as older females and lower host densities tend to result in attacks on already parasitized hosts [33,62,63]. As a solitary arrhenotokous egg parasitoid, O. kuvanae has superparasitized larger hosts under laboratory conditions [33]. However, this phenomenon has not been reported from the field before. The same factors may not be sufficient to explain the field superparasitism on L. delicatula observed in this study, since plenty of unparasitized host eggs were available in the environment, and the old parasitoid females, after overwintering, did not superparasitize gypsy moth eggs based on other studies. One can point to the difference in egg size between the two species from a resource exploitation point of view. An L. delicatula egg is cylindrical, with measurements of 1.5 × 3.0 mm (diameter × height) [3], whereas a gypsy moth egg is oval, with a diameter of 1 mm [23]. It contains about 10 times the nutrition to support the development of multiple O. kuvanae individuals. Another explanation could be encapsulation evasion, where multiple parasitoids can better overcome a host's immune system, especially for solitary species [28]. Field superparasitism has also been reported for Diachasmimorpha longicaudata (Ashmead) (Hymenoptera: Braconidae), a solitary larval-pupal parasitoid of the Mexican fruit fly Anastrepha ludens (Loew) (Diptera: Tephritidae) [64]; and Phymastichus coffea LaSalle (Hymenoptera: Eulophidae), a gregarious endoparasitoid of the female coffee berry borer Hypothenemus hampei (Ferrari) (Coleoptera: Curculionidae) [65].
It is possible for other native natural enemy species to start their own new associations with L. delicatula in the future, just like O. kuvanae did. An unidentified species of Dryinidae was found attacking L. delicatula nymphs in Berks county in 2016 [42]. There are approximately 143 genera and 716 species in the Fulgoridae family worldwide, with all Lycorma species found in Asia [66]. In the Americas north of Mexico, this family is represented by 17 species in 9 genera [67]. None had been found in Pennsylvania prior to the introduction of L. delicatula in 2014. However, the planthopper parasitoid Fulgoraecia exigua (H. Edwards) (Lepidoptera: Epipyropidae) has been recorded in Pennsylvania [68]. Time will tell whether it can switch to L. delicatula in Pennsylvania in the future.

Conclusions
O. kuvanae is the first parasitoid recorded on L. delicatula in North America, with a life cycle well synchronized with overwintering L. delicatula eggs in the spring. As a solitary arrhenotokous egg parasitoid, it can superparasitize L. delicatula eggs in the field and result in a female-biased progeny population. It has great potential as an important biological control agent for the management of L. delicatula in North America. Compared to the gypsy moth, L. delicatula provides some unique opportunities (e.g., a single-layer egg mass, larger eggs) and challenges (e.g., a late egg period) as a host for O. kuvanae to complete its life cycle in the field. They could complement each other as alternative hosts for O. kuvanae in the future. One advantage of this parasitoid over other exotic natural enemies (e.g., An. orientalis) being considered for L. delicatula biological control is its century-long field establishment in North America, which makes it readily available for use in potential augmentation and conservation biological controls. Its success on gypsy moths as an effective biological control agent could well be translated to L. delicatula. Past experiences with it in biology studies, laboratory rearing techniques, field release protocols, and recovery confirmation methodologies against the gypsy moth could be very helpful in the future utilization of O. kuvanae in the biological control of L. delicatula. Concerns over nontarget impacts in North America will be minimized, since no hosts other than the gypsy moth have been recorded from the field. The relatively low field parasitism and apparent lack of synchronization with host eggs in the fall could be overcome with time and more studies on its life history, field host range, attacking patterns, consequences of superparasitism, and host biology and seasonal development.
Author Contributions: H.L. was responsible for the study conceptualization, methodology, funding acquisition, investigation, work supervision, formal analysis, draft preparation, and manuscript reviewing and editing.
Funding: This research was partially funded by the USDA-APHIS-PPQ Cooperative Agreement 16-8130-0655-CA and Farm Bill #AP17PPQS&T00C057.