Hadronotus pubescens (Motschoulsky) (Hymenoptera, Scelionidae): Redescription, biological attributes, and parasitism on eggs of Riptortus pedestris (Fab.) (Hemiptera, Alydidae)

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Introduction
Riptortus pedestris (Fab.) (Hemiptera, Alydidae) is a destructive pest on a wide range of crop plants in Korea and Japan (Honda 1986;Son et al. 2000;Kang et al. 2003;Lee et al. 2004) and has infested many leguminous crops in Bangladesh (Arifunnahar et al. 2019(Arifunnahar et al. , 2021. It is also an important hemipteran pest of soybean (Glycine max (L.) Merr.) (Osakabe and Honda 2002;Choi et al. 2005) and fruit trees (Chung et al. 1995). Riptortus pedestris is a major pest of many grains, including sorghum (Sorghum bicolor (L.) Moench), foxtail millet (Setaria italica (L.) P. Beauvois), and barley (Hordeum vulgare L.) in the reproductive stages (Chung et al. 1995;Mainali et al. 2014), as well as other field crops in Asian countries (Kang et al. 2003;Wada et al. 2006). Nymphs and adults of R. pedestris feed preferentially on seeds by piercing and sucking (Choi et al. 2005). Their polyphagous nature, as well as the preferential feeding on seeds, make crop plants highly vulnerable to damage (Choi et al. 2005). Both adults and nymphs feed on the fluids from seed pods, causing them to fail to mature, turn brown, shrivel and die. Generally, when such pods are opened, the seeds inside are shriveled, undersized, or malformed. These unhealthy seeds often succumb to secondary fungal infections like yeast-spot disease (Eremothecuim coryli (Peglion) Kurtzman) (Kimura et al. 2008) which can lead to the complete abortion of seeds in the entire field (Li et al. 2019). Many legume growers spray insecticides to control R. pedestris, but this is not economically effective with mung bean (Vigna radiata (L.)) in Bangladesh due to its relatively low cash value. Chemical insecticides are a useful component of integrated pest management (IPM) systems when they are quick and easy to apply, economically viable, and have reliable effectiveness against the targeted insect pest (Endo and Tsurumachi 2001). However chemical insecticides often negatively impact natural enemies and may cause pest resurgence and other environmental side effects (Schwab et al. 1995). Therefore, chemical insecticides may not be economically feasible due to the higher cost of production and environmental concerns. While most chemical insecticides are fast-acting, the high mobility of these insects makes them difficult to control (Choi et al. 2005;Wada et al. 2006). In light of these difficulties, cultural practices such as delayed seeding and use of resistant varieties have been suggested for the management of various stink bugs (Bowers 1990;Wada et al. 2006). Biological control has been successfully employed against various stink bugs by introduction or augmentation of egg parasitoids (Weber et al. 1996;Orr 1998;Alim and Lim 2011) and may be an option for R. pedestris in Bangladesh.
Previously reported parasitoids of R. pedestris eggs in soybean fields in east Asia include Hadronotus japonicus (Ashmead) (reported as Gryon japonicum (Ashmead)), Hadronotus nigricornis (Dodd) (reported as Gryon nigricorne (Dodd)) (Hymenoptera, Scelionidae) and Ooencyrtus nezarae Ishii (Hymenoptera, Encyrtidae) (Noda 1989;Hirose et al. 1996;Mizutani et al. 1996;Son et al. 2009). Species of Hadronotus Förster are known to parasitize the eggs of hemipteran pests, including pentatomids such as Piezodorus hybneri (Gmelin), Dolycoris baccarum (L.), Nezara antennata Scott and Halyomorpha halys (Stål) Mizutani et al. 1996;Zhang et al. 2005). However, the effective use of Hadronotus species for biological control requires the ability to accurately identify them. In many cases, this involves time-consuming taxonomic research, creating delays for field and laboratory studies and the publication of their results. Some recent advances in the taxonomy of the group include the work of Komeda et al. (2020), who revised some species-groups in Japan, and Talamas et al. (2021), who resurrected Hadronotus and provided images for many primary types of Gryon Haliday and Hadronotus.
Hadronotus pubescens is a solitary egg parasitoid reported from Sri Lanka and India, especially Karnataka (Sharma et al. 1982), but not previously recorded in Bangladesh. The biological parameters of this parasitoid are largely unknown, and to date no research on either H. pubescens or the egg parasitoids of R. pedestris has been conducted in Bangladesh. In this study, biological parameters of H. pubescens on R. pedestris eggs were evaluated in laboratory conditions to determine the parasitoid's potential as a biological control agent. These parameters included emergence rate, development time, sex ratio, adult longevity and size variation of the adult wasps.

Materials and methods
Experiments were conducted in the laboratory of the Department of Entomology, Hajee Mohammad Danesh Science and Technology University (HSTU), Dinajpur and different mung bean fields near HSTU campus from December 2019 to June 2020. The taxonomic portion of the study was conducted at the Florida State Collection of Arthropods, Gainesville, Florida, USA.

Imaging
Photographs were captured using a Macropod Microkit (Macroscopic Solutions) imaging system and rendered with Helicon Focus. In some cases, multiple images were stitched together in Photoshop to produce larger images at high resolution and magnification. Dissections for scanning electron microscopy were performed with a minuten probe and forceps. Body parts were mounted to a 12 mm slotted aluminum mounting stub using a carbon adhesive tab and sputter coated with approximately 70 nm of gold/palladium using a Denton IV sputter coater. Micrographs were captured using a Phenom XL G2 Desktop SEM.

Data deposition
The data associated with the specimens in this study are deposited at mbd-db.osu.edu and are retrievable via the collecting unit identifier (CUID) for each specimen. Images of the holotype specimens of Muscidea pubescens Motschoulsky and Gryon hogenakalensis Sharma were made available by Talamas et al. (2021) and Talamas et al. (2017), respectively, and direct links to these images are provided in the species treatment.

DNA barcoding
Genomic DNA was nondestructively isolated from whole specimens using the Qiagen DNeasy kit (Hilden, Germany) as described by Giantsis et al. (2016). PCRs were carried out to amplify the DNA barcode region of the cytochrome oxidase subunit I (COI) using the LCO/HCO primers of Folmer et al. (1994). The PCRs were performed in a 25 µL reaction volume using the KAPA HiFi Hotstart Ready Mix (Roche) per the manufacturer's standard protocol. PCR conditions were as follows: 95 °C for 2 min, followed by 32 cycles of 95 °C for 30 s, 50 °C for 40 seconds, 72 °C for 1 min with a final extension at 72 °C for 7 min. The fragments to be amplified by PCR were separated by electrophoresis on 1.5% agarose gels. After verification, the samples were sequenced at the Florida Department of Agriculture and Consumer Services, Division of Plant Industry, Gainesville, Florida. GenBank accession numbers for the newly generated barcodes for H. pubescens and sequences from Talamas et al. (2021) are listed in Table 2.

Rearing of R. pedestris
Adults of Riptortus pedestris were collected from infested country bean (Lablab purpureus L.) fields near the HSTU campus during 2019 and the colony was maintained in the laboratory as described by Alim and Lim (2009). Briefly, the nymphs and adults were kept in acrylic cages (40 L × 40 W × 40 H cm), each with windows on three lateral sides covered with mesh screens for ventilation. The insects were reared at a constant temperature (30 °C ± 2) and relative humidity 75% ± 4 and with a natural photoperiod. Temperature and relative humidity were monitored by the Hydro-thermometer (HTC-1). Ascorbic acid was dissolved in water and provided to the adult R. pedestris in dishes along with soybean seeds. Nymphs were fed with soybean seeds and bean plants with cotyledonous leaves. Oviposition substrates were prepared by placing a few pieces of gauze fabric in the top and bottom corners inside the adult cages. The gauze was replaced every day and the eggs were collected to continue the colony. The cage was cleaned two times per week.

Rearing of H. pubescens
Hadronotus pubescens were reared from field-collected eggs of R. pedestris from country bean fields. The parasitoids were reared under laboratory conditions as described in the previous section. The males and females of H. pubescens were placed into plastic centrifuge tubes (50 mL) (SPL Life Sciences Co. Ltd, Korea) and provided with honey on the inner surface of the tube and a piece of moistened cotton. Moistened cotton and honey were replaced every three days.

Abundance of R. pedestris and its egg parasitoids at different locations
To determine the parasitism rate of field-laid eggs, 10 mung bean plants were randomly selected in plots at three locations (Table 1). These plants were examined every 10 days from February to April, 2020, to collect eggs of R. pedestris and record the numbers of nymphs and adults. Eggs were brought to the laboratory, individually placed in microtubes (2 mL capacity), and kept in the laboratory. The numbers of newly hatched R. pedestris and parasitoids were recorded daily. Additionally, the sex of the newly emerged parasitoids was recorded. Eggs that produced neither a host nymph nor an adult parasitoid were dissected under a stereomicroscope. Host eggs containing parasitoids that failed to develop or emerge were considered parasitized. Each sampling plot was spaced 200 meters apart at each location.

Monitoring of R. pedestris and its egg parasitoids by pheromone traps
Aggregation pheromone traps were made locally with an iron frame covered with mosquito netting (32 L × 13 D cm). Each trap had two separate openings that enabled entry of R. pedestris. Inside the traps were aggregation pheromone lures (Green Agro-Tech Co. Ltd., Kyungsan, Republic of Korea, 50 µL/lure). [Myristyl isobutyrate, (E)-2-hexenyl (E)-2-hexenoate and (E)-2-hexenyl (Z)-3-hexenoate at the ratio 1:5:1], and the traps were suspended in the mung bean canopy from a cord attached to the end of a bamboo pole. Inside the trap, a cord was affixed to provide a substrate for egg laying by R. pedestris adults. Three pheromone traps were installed at each location (Table 1). Adults and nymphs of R. pedestris were recorded at 10-day intervals and the eggs laid by adult R. pedestris were collected, brought into the laboratory, placed in micro tubes individually and kept at ambient temperature. The hatching of host insects and the emergence of adult parasitoids were recorded daily.

Effects of host egg age on host acceptance behavior by H. pubescens
After 0, 24, 48, 72 and 96 hours from the time that the eggs were laid, eggs were placed in an insect breeding Petri dish (4 H × 10 D cm) at room temperature. Then, a single, mated and naive, 4-day old female H. pubescens was introduced into each Petri dish. Host acceptance behaviors were observed under a stereomicroscope (AmScope SM-2TZ LWD, USA) and categorized as drumming, drilling, marking, and oviposition (Strand and Vinson 1983;Noda 1993). The time spent performing each behavior was recorded for each of the eggs when the parasitoid displayed complete host acceptance behavior. The entire procedure was repeated with 10 female parasitoids at each time interval.

Effect of host eggs age on the biological parameters of H. pubescens
After 0, 24, 48, 72 and 96 hours from the time that the eggs were laid, 10 eggs of R. pedestris were placed on an insect breeding dish (4 H × 10 D cm), and a 4-day old, mated H. pubescens female was allowed to parasitize the eggs for 24 hours at ambient conditions. After 24 hours the female was withdrawn, and the eggs were then placed individually in 2 mL micro tubes with a drop of honey. The eggs were checked daily for the emergence of parasitoids. The number of host eggs parasitized, adult emergence, sex ratio, development time and longevity of male and female H. pubescens were recorded. Host eggs containing parasitoids that failed to develop or emerge were also considered parasitized, as determined by dissection of each egg. These procedures were replicated 10 times for each age period. Each parasitoid that emerged was collected and placed in a 50 mL rearing tube. To maximize longevity, fresh honey and moistened cotton were provided every three days, and the parasitoids were transferred to new tubes as needed. To determine the effect of time on the size of the emerged parasitoids, a total of 30 individuals, both males and females, were randomly selected in each group and their hind tibia lengths were measured under a stereomicroscope (Am Scope, China.) using a micrometer.

Statistical analyses
Emergence rate, adult sex ratio and seasonal parasitism rate were subjected to a chi-square test of a contingency table and a Tukey-type multiple comparison test for post hoc analysis (Zar 2010). The number of parasitized host eggs, number of emerged parasitoids, development time, and hind tibia length of parasitoids was analyzed by a Kruskal-Wallis single factor analysis of variance by rank. If significance was detected, multiple comparisons were conducted using the Duncan test (Zar 2010). The number of eggs, nymphs and adults recorded in the field were analyzed by a univariate analysis of variance by rank. If significance was detected, multiple comparisons were conducted using the Duncan test (Zar 2010). Statistical analyses were performed in IBM SPSS Statistics for Windows.  Intraspecific variation: The specimens examined here are phenotypically uniform, with slight variation occurring in the degree to which transverse striation is developed on the frons and how far the striation extends laterally. The specimens from Bangladesh showed little variation in size, with females ranging from 1.25-1.43 mm. The female specimen from Taiwan was significantly smaller (1.07 mm). Comments. Hadronotus pubescens is a widespread species, ranging at least from Sri Lanka to Taiwan based on the specimens examined here. The COI sequences from the Taiwanese and Bangladesh specimens share 99.83% sequence identity, providing strong molecular support that they are conspecific. However, a more comprehensive examination of the species limits of H. pubescens is still needed and will require analysis of specimens from an even greater geographic range. We examined specimens from South Africa that are morphologically very similar to H. pubescens in Asia, pres- ently separable only by the color of the appendages, yet their COI sequences differ by nearly 13%.

Hadronotus pubescens (Motcshoulsky)
Hadronotus pubescens belongs to a lineage, the pubescens species group, that Mineo (1980) defined primarily by the presence of a "marginal carina" (Figs 4, 8, mac), which extends medially from the hyperoccipital carina. Two characters provide evidence that this lineage is close to the charon species group: the mesoscutal humeral pit (Fig. 10, mhp) and the epiclypeal carina (Figs 2, 7, ec). The mesoscutal humeral pit was first documented by Chen et al. (2020) in H. ancinla (Kozlov & Lê) and is present in all species of the charon group that we have examined. The antennal scrobe in the charon group is entirely delimited by a continuous carina. We consider the ventral, transverse portion of this carina to be homologous with the epiclypeal carina, as is found in H. pubescens. The taxon sampling in the multi-gene phylogeny presented in Fig. 2 of Talamas et al. (2021) does not allow for analysis of the monophyly or delimitation of these two species groups. The systematics of Hadronotus is ongoing and treatment of species groups within the genus is a research priority.
The metapectal propodeal complex contains morphological characters that have yet to be fully exploited in Hadronotus. Carinae and sulci on the metasomal depression vary remarkably among species that we have examined and are likely to become more informative as they are studied in greater detail. The ventral mesopleural carina delimits the posterior margin of the metapleuron on the venter and may be interrupted by the foramen of the hind coxa, as in H. pubescens (Figs 9, 11). A transverse carina often extends from the propodeal foramen across the metasomal depression and may be accompanied by a sulcus (Fig. 11). Talamas et al. (2021) provided the term "sulcus of the propodeal foramen" for Gryon aetherium Talamas, which is present only dorsally. In H. pubescens, foveae are present ventral to the transverse carina on the metasoma depression. It is presently unclear if these foveae are a continuation of the sulcus of the propodeal foramen or an independent structure.

Abundance of R. pedestris and its egg parasitoids in different locations
All life stages of R. pedestris were found throughout the sampling period. The occurrence of R. pedestris eggs, nymphs, and adults started in February and peaked in the month of April. The seasonal number of eggs (H C = 11.201, df = 8, P = 0.076), nymphs (H C = 11.028, df = 8, P = 0.284) and adults (H C = 3.00, df = 8, P = 0.876) of R. pedestris was not significantly different among the three different locations (Fig. 12). The number of both unparasitized and parasitized eggs was higher in the mung bean field in Shadipur compared to the other two locations (Fig. 13). The number of unparasitized eggs (H C = 1.192, df = 8, P = 0.981) and parasitized eggs (H C = 8.998, df = 8, P = 0.98) were not significantly different among the three locations (Fig. 13). The total parasitism rate of natural host eggs at each sampling site was separated by parasitoid species, i.e., solitary parasitoid Hadronotus pubescens and gregarious parasitoids like Ooencyrtus sp. Throughout the sampling period, the total parasitism rate , and adults (C) of R. pedestris sampled from three different study sites. Analyses were conducted on the seasonal data using Kruskal-Wallis single factor analysis of variance by rank. Figure 13. Parasitism rate (%) of natural R. pedestris eggs collected from three different study sites. Analyses were conducted on the seasonal data using Kruskal-Wallis single factor analysis of variance by rank. by both species was found to be higher in Kornai compared to HSTU campus and Shadipur mung bean field (χ 2 = 0.005, df = 2, P = 0.997) (Fig. 13). The total parasitism rates by both parasitoid species were higher in the month of April, when the mung bean seeds were maturing. The parasitism rate by H. pubescens on naturally-laid host eggs was higher in Kornai than in Shadipur or the HSTU Campus (χ 2 = 5.371, df = 8, P = 0.639) (Fig. 14). On the other hand, the parasitism rate of Ooencyrtus sp.alone (χ 2 = 9.746, df = 8, P = 0.201) was highest in the HSTU campus among the three study sites (Fig. 14).

Monitoring of R. pedestris and its egg parasitoids by pheromone traps
Throughout the sampling period, the number of eggs, nymphs, and adults of R. pedestris found in the pheromone traps differed between the sites. The seasonal numbers of eggs (H C = 7.513, df = 8, P = 0.341), nymphs (H C = 10.096, df = 8, P = 0.268), and adults (Hc = 14.415, df = 8, P = 0.254) of R. pedestris were not significantly different among the study sites (Fig. 15). However, the numbers of eggs, nymphs, and adults of R. pedestris caught by pheromone traps was higher on the HSTU campus than at the other two sites in the month of April. The number of unparasitized eggs was higher  on the HSTU campus compared to the other two sites, and the number of parasitized eggs was higher in Kornai compared to other locations in the month of April. The seasonal numbers of unparasitized eggs (H C = 0.507, df = 8, P = 1.00) and parasitized eggs (H C = 6.302, df = 8, P = 0.330) were not significantly different among the three different locations (Fig. 16). Throughout the sampling period, the total parasitism rate was not significantly different but was higher in the month of April in Kornai compared to the other sites (χ 2 = 0.862, df = 2, P = 0.649) (Fig. 16).
The total parasitism rate on natural host eggs at each sampling site was separated by parasitoid species, i.e., H. pubescens and Ooencyrtus sp. The overall parasitism rate by H. pubescens peaked in February and was lowest in April, whereas parasitism by Ooencyrtus sp. peaked in April and was lowest in February. The parasitism rate of both H. pubescens (χ 2 = 2.440, df = 8, P = 0.827) and Ooencyrtus sp. (χ 2 = 7.745, df = 8, P = 0.357) were not statistically different among sites and were highest in Kornai (Fig. 17).

Effects of host egg age on host acceptance behavior by H. pubescens
All H. pubescens showed a complete process of host acceptance behaviors on the eggs of R. pedestris. Each phase consisted of one or more bouts. The duration of host acceptance behaviors displayed by the egg parasitoids is shown in Table 3. Drumming was Table 3. Duration (seconds ± SE) of host acceptance behaviors in different ages of R. pedestris eggs Numbers in each row followed by the same letter are not significantly different (P > 0.05).

Behaviors
Age of host eggs ( Figure 16. Parasitism rate of natural R. pedestris eggs collected from aggregation pheromone traps from three different study sites. Analyses were conducted on the seasonal data using Kruskal-Wallis single factor analysis of variance by rank. characterized by moving antennae up and down over the exposed surface of the eggs while the female remained still, standing over the eggs. The duration of drumming increased as the age of the host egg increased (H C = 43.562, df = 4, P < 0.001) ( Table 3). The 96 hr old eggs of R. pedestris received the longest duration of drumming by the parasitoid. The female parasitoid started drilling after the drumming by inserting her ovipositor into the host eggs. After head pumping, the female remained motionless for 10-15 seconds until oviposition was completed. The mean time spent on drilling and oviposition increased as the age of the host egg increased. The eggs of R. pedestris at 96 hours showed the longest duration of drilling and oviposition by the parasitoid. (H C = 47.063, df = 4, P < 0.001) (Table 3). Similarly, females of H. pubescens spent more time marking eggs that were 96 hours old compared to eggs of other ages (H C = 47.059, df = 4, P < 0.001) ( Table 3).

Effect of host egg age on the biological attributes of Hadronotus pubescens
The number of eggs parasitized by H. pubescens was influenced by the age of the host eggs. Hadronotus pubescens can successfully parasitize host eggs up to 48 hours old without a change in the parasitism rate (H C = 10.813, df = 4, P = 0.029) (Table 4). However, for the host eggs 96 hours old, the parasitism rate decreased approximately 14% compared to the control (Table 4). The emergence rate (H C = 8.802, df = 4, P = 0.662) and the sex ratio (χ 2 = 6.416, df = 4, P = 0.170) of H. pubescens were unaffected by host egg ages (Table 4). However, the total number of parasitoids that emerged from parasitized eggs significantly decreased with the increase in the host egg age. The sex ratios of the emerged parasitoids were all female biased. The mean development time (from egg to adult) of H. pubescens males and females increased significantly as host egg age increased (male H C = 14.288, df = 4, P < 0.001; female H C = 105.398, df = 4, P < 0.001) ( Table 4). The highest mean development time for both males and females was found in eggs 96 hours in age and was lowest in the control (0 hours). The longevity of male and female H. pubescens decreased significantly when host egg age increased (male H C = 41.432 df = 4 P < 0.001; female H C = 192.442 df = 4 P < 0.001) ( Table 4). The highest longevity was found at 0 hours of age (control) compared to the other treatments.

Discussion
Throughout the sampling period, eggs, nymphs, and adults of R. pedestris were found in the three mung bean fields that we sampled. All life stages of R. pedestris were observed early in the mung bean season (February) and increased in abundance in April. Son et al. (2008) reported R. pedestris in different fruit orchards starting in the last week of April and found the highest abundance in June and October. Riptortus pedestris populations were found to start infesting soybeans in the second week of August, with a population peak occurring in the first half of September (Kim and Lim 2010). In the present study, nymphs were caught in pheromone traps during the whole experimental period at the three different locations. The highest number of nymphs was attracted by pheromone traps in the month of April. The synthetic pheromone was effective in attracting second instar R. pedestris nymphs only. Leal et al. (1995) speculated that older nymphs do not respond because they may not need information to locate a food source as they have already reached the host plant. The R. pedestris adults were attracted to pheromone traps starting in the month of February and showed the highest levels of attraction in the middle of April. Adults of R. pedestris were found in traps on barley in the second week of April. The population then increased and peaked in the last week of August on soybeans, and sharply decreased in October (Mainali and Lim 2012).
In this study, we confirmed that the solitary egg parasitoid H. pubescens appears in mung bean fields from the first week of February to the last week of April. On the other hand, gregarious parasitoids Ooencyrtus sp. appear in mung bean fields from the middle of February to the end of April.
The differential pattern of occurrence, i.e., H. pubescens during spring and Ooencyrtus sp. during summer, is a new finding in mung bean fields in Bangladesh. Differences in the temporal patterns of each parasitoid's occurrence could be the result of adaptation to certain environmental conditions such as temperature or humidity. Patterns observed in our survey demonstrated that H. pubescens probably perform better in the spring and early summer, when humidity is low, compared to Ooencyrtus sp., whose abundance was greatest in the summer when higher humidity was recorded in Bangladesh. The effects of weather conditions on the timing of occurrence and on biological attributes have been reported for other parasitoid species (Ouedraogo et al. 1996;Rousse et al. 2009;Sorribas et al. 2010).
Another factor that could affect the abundance of adult populations is interspecific competition inside the host eggs. Takasu et al. (1998) found that interactions between adults of Ooencyrtus sp. and Hadronotus spp. did not influence the reproduction of either species (Takasu et al.1998). Given that some species of Ooencyrtus, eg., O. nezarae, are facultative hyperparasitoids, use of these species as biological control agents may reduce the population of other parasitoids in the system, such as H. pubescens.
The emergence rate and the sex ratio of H. pubescens were unaffected by host egg ages. This, in combination with the increased time spent on host assessment and the lower parasitism rate associated with older eggs, suggests that females of H. pubescens discriminate and reject eggs that are too old to be viable for their progeny. The sex ratios of the emerged parasitoids were all female-biased without statistical significance among the different periods. The highest mean development time (male and female) was found at 96 hours of age and the lowest in control (0 hours), which might be due to the lower nutritional quality attributed to older host eggs that can slow the offspring development rate (Godfray 1994). Male and female H. pubescens had shorter lifespans as age of the the host eggs increased, perhaps due to reduced nutritional quality of the eggs (Alim and Lim 2009).

Conclusion
This study provides baseline data on the parasitism of R. pedestris eggs by H. pubescens and a species of Ooencyrtus and indicates that H. pubescens has potential as a biological control agent. It also showcases the necessity of integrating taxonomy with field studies so that the biological parameters of a species can be confidently associated with a species name. In the case of H. pubescens, the species-level treatment provided here is the first since its original description in 1863 and was facilitated by the holotype images and molecular data provided in Talamas et al. (2021). We hope that this paradigm of integration will continue to be employed as additional studies on parasitoids of hemipteran eggs are conducted.