1. Introduction
The erythrina gall wasp (EGW),
Quadrastichus erythrinae Kim (Hymenoptera: Eulophidae), is an invasive species that threatens erythrina trees (Fabaceae) including the endemic wiliwili tree,
Erythrina sandwicensis Degener in Hawaii. This gall-forming wasp was described in 2004 as a new species from specimens collected in Mauritius, Reunion, and Singapore [
1]. During April 2005, it was detected on the island of Oahu, and quickly spread to all of the major Hawaiian islands by August 2005. Its worldwide distribution currently includes American Samoa, mainland China, Guam, Hong Kong, India , Okinawa, Philippines, Taiwan, and Thailand [
2,
3,
4,
5]. It was reported from the continental United States (Florida) during October 2006, subsequently Mexico and widely throughout the Neotropical region [
6,
7,
8].
Erythrina is a genus of 123 species of Gondwanan origin, which are distributed throughout the tropics and warm temperate regions [
9,
10]. Hawaii is home to the endemic wiliwili tree,
Erythrina sandwicensis, a deciduous species that is an important component of dryland forest areas on the leeward sides of the islands. The soft, light wood of wiliwili was traditionally used for outriggers of Hawaiian canoes and for fishnet floats and surfboards. The orange and scarlet seeds are strung into valuable wreathes [
9]. Wiliwili trees are also mentioned in Hawaiian legend [
11]. Wiliwili is unique in that it is the only species in the genus to produce flowers of various colors (orange, red, salmon, peach, light green, yellow, or white). In response to concerns of loss of natural stands of wiliwili and possible extinction due to the EGW infestation, the University of Hawaii Lyon Arboretum’s Rare Hawaiian Plants Program established a wiliwili seed bank with representative seed collections from multiple microhabitats of the islands to preserve the species and its genetic diversity [
12].
Non-native
Erythrina species in Hawaii include
E. variegata L., an introduced ornamental species from tropical Asia that is commonly used in landscape parks, schools, and roadways. The beauty and shade provided by these large, spreading trees have been lost as almost all these trees were killed by EGW shortly after the invasion occurred (
Figure 1A–D). Only a few trees have survived, and these have been routinely treated with expensive systemic insecticides. During the onslaught of infestation, The City and County of Honolulu removed about 2,000
Erythrina trees killed by the EGW [
13]. The columnar form of
E. variegata, known as Tropic Coral or tall
Erythrina, was developed for use as a windbreak for soil and water conservation and for planting around farms [
14]. It is highly susceptible to EGW infestations and only a few of these trees remain alive in the state (
Figure 1F). Another introduced ornamental tree,
E. crista-galli L., a South American species, showed some tolerance to the EGW and has survived despite unsightly galled flowers, stems, and seedpods [
15].
The EGW is a minute gall-forming wasp belonging to the family Eulophidae (≈ 1.6 mm in length). Females insert their eggs (mean ± SEM = 203.6 ± 5.3 eggs/female @ 30 C°, [
16] into young leaves and stems and the wasp larvae develop within plant tissue, inducing the formation of galls in leaflets and petioles (
Figure 1A). As the infestation progresses, leaves curl, and appear deformed while petioles and shoots become swollen (
Figure 1B). Larvae pupate within the galls (
Figure 2A) and adult wasps emerge by tunneling through tissue. Heavily galled leaves and stems result in loss of growth and vigor as photosynthesis is reduced and plant health declines. Severe infestations eventually cause mortality (
Figure 1D–F).
Systemic insecticides were developed for control as the EGW larvae feed within the plant tissue. Although chemical injection systems and soil drenches were shown to be effective in some cases, they were expensive and were not cost-effective treatments for all
Erythrina plantings or natural stands [
17,
18]. Conservation and chemical use was not feasible for the endemic
E. sandwicensis in its often-remote native forest habitat [
19]. The use of natural enemies was believed to be the most cost effective, sustainable, long-term solution to the EGW problem.
A classical biological control program was initiated by the Hawaii Department of Agriculture (HDOA) during December 2005.
Erythrina trees in Hawaii were rapidly declining from the EGW infestation so exploratory efforts were shared by the HDOA and the University of Hawaii (UH Manoa) to search the greatest area in the shortest possible time. The surveys were supported by funds from the Hawaii Department of Lands and Natural Resources. HDOA conducted explorations in Tanzania, Mozambique, and South Africa. HDOA had determined Tanzania to be the likely evolutionary origin of
Erythrina due to the high diversity of
Erythrina species native to the region (i.e., 15 species and subspecies, 75% of listed
Erythrina in Tanzania, [
10]. The UH made surveys in Madagascar, Mozambique, South Africa, west African countries of Benin, Ghana, Togo, and Nigeria. All field collections of galled leaves were sent back to the HDOA Insect Containment Facility for processing.
A dominant chalcidoid natural enemy of the gall forming
Quadrastichus spp. wasps found in the Morogoro region, Tanzania in January 2006. Specimens of this wasp were sent to a specialist Michael Gates at the United States Department of Agriculture-Systematic Entomology Laboratory (USDA-SEL) in Beltsville, Maryland for identification. It was determined to be a new species and was described as
Eurytoma erythrinae [
20]. This study reports on the biological attributes, host specificity, and release records of
E. erythrinae conducted by the HDOA Plant Pest Control Branch.
2. Materials & Methods
2.1. Plant propagation
The Indian coral tree, Erythrina variegata, was used for rearing EGW as it was the most abundant seed source of propagative material available and was observed to be an excellent host in Hawaii. Its seedlings were favored because of their rapid growth. Scarified using an electric file, with nearly 100% germination within seven days and produced usable 15–20 cm height seedlings in 3–4 weeks. Three seeds were planted in 10 cm square pots with potting mix (Miracle-Gro 6-Quart All-purpose Potting Soil Mix) and kept in outdoor screened cages (76 x 88 x 127 cm, 70 mesh ) and watered daily.
2.2. EGW propagation
Eight pots of
E. variegata plants (15–20 cm height, 3 plants/pot), each placed in a 13 cm Ø saucer, were put into a screened cage (30 x 30 x 60 cm, 70 mesh). A total of about 150 pairs EGW were placed into each cage during a three-day period. Honey (SUE BEE
® SPUN
® siouxhoney.com/sue-bee-spun- honey) was dotted on the inside of the cage to feed the wasps. Galls began appearing on the leaves and stems of the host plants within a week and adults began emerging in about 20 days (
Figure 1A and
Figure 2A). Plants were watered every other day and any excess water draining into the saucer was emptied to prevent EGW adults from drowning in it.
2.3. Origin of the parasitoid colony.
In December 2005–February 2006, HDOA collected gall wasps from Erythrina abyssinica Lam. ex DC. leaves in Tanzania that appeared to be a color variant of the EGW present in Hawaii. Tanzanian specimens from the Chalinze Village, Morogoro region, (6° 38′ 20.95” S, 38° 21′ 07.83” E, 212 m) were sent to an eulophid expert for identification (Dr. John La Salle, CSIRO, Entomology, Canberra, Australia, identification letter to HDOA), who confirmed the specimens as Quadrastichus erythrinae. Those were later found in other villages in the Rubungo, Bwawani, Morogoro region; and Masai camp, Arusha region; Tanzania. Therefore, we reared the parasitoids from the Tanzanian collection. Infested plant leaves were shipped to Hawaii where parasitoids emerged. Galled leaves and stem samples with evidence of parasitism were prepared for shipment to Hawaii collected from South Africa, Kenya, Ghana, Benin, Togo, and Nigeria. Hundreds of galled leaves and stems of nine Erythrina species (E. abyssinica Lam., E. caffra Thunb., E. crista-galli L., E. latissimi E. Mey., E. lysistemon Hutch., E. sacluxii Hua, Erythrina sp., E. variegate L., and E. variegata var. orientalis Murr.) were packed well with the cut ends of petioles wrapped in wet tissue paper and parafilm. Leaves were then folded between tissue paper to absorb the extra moisture, placed in perforated plastic bags, afterward in a cooler with blue ice packs (Igloo Ice Blocks). All bags were packed in cotton pillowcases then in cardboard box with the USDA shipping permit attached to it. Parcels were air shipped to the HDOA Insect Containment Facility in Honolulu and arrived in 2–6 days (FedEx and Airway Cargo). Experiments with the parasitoid started on the second generation in quarantine facility (mean ± SEM, temperature 21.8 ± 0.12 C°, mean RH 70.2 ± 2.4 %, Light 12:12, D:L).
2.4. Eurytoma erythrinae propagation
Galled plants were ready to be used for parasitoid propagation 14 days after exposure to the EGW females. This was conducted inside the containment facility. About 25 pairs of newly eclosed E. erythrinae were placed in each cage (30x30x60 cm, 70 mesh) containing eight pots of galled plants. The parasitoids were left in the cage for 14 days and then removed. A new generation of parasitoid adults began emerging in about 17 days. Daily emergence rates and sex ratios were monitored.
2.5. Life history study
Observations were made of ovipositional behavior by placing naïve mated females on a galled plant using a dissecting Nikon SMZ-745 259 stereomicroscope. Information on the duration of immature stages was obtained by periodical dissection of galls infested with immature EGW that were being preyed upon by E. erythrinae larvae. Mated E. erythrinae females were placed in a cage with pots of galled plants with parasitoids, using the same procedure as described for its propagation. After 24 hours, the females were removed. Gall dissections were made to determine the developmental stadia of E. erythrinae immature stages. Median developing period was reported since gall dissections were made every 2–3 days.
2.6. Longevity study and size of wasps
Adult longevity of host-deprived parasitoids was determined by making daily collections of newly emerged
E. erythrinae wasps and placing them in a wide-mouth clear Mason Jar (3.8 liter), with a cloth cover secured over the mouth of the jar with rubber bands. A few drops of honey were dotted inside the jar and water was provided in a glass bottle (30 ml) with a cotton wick. At least one wasp of each sex had to be present in the jar so that mating could occur. Wasps were checked daily for mortality. Front wing length, measured from tegula to the wing tip, and body length, measured from tip of head to tip of abdomen, were recorded for each dead adult [
21]. Measurements were made for laboratory individuals and field collected wasps were also compared with the size of EGW (Oahu island, October 10, 2023, ex.
E. variegata, n = 12).
2.7. Fecundity
Fecundity tests were conducted to determine the number of progeny a female could produce in her lifetime. One female and five male
E. erythrinae adults, all newly emerged, were placed in a large jar (cloth secured over open end) with one pot of 14-day-old, galled host plants and a few drops of honey and water was provided. Every three days, the pot of galled plants was removed from the jar and placed in a 30 cm
3, 70 mesh, screened cage to hold for daily recording of
E. erythrinae emergence. A new pot of galled plants was added to the jar and the procedure was repeated every three days until the
E. erythrinae female died. Wasps were checked daily for mortality. Upon the death, the female was dissected and the number of mature eggs (
Figure 2A) remaining in the ovaries were counted using a Nikon SMZ-745 259 stereomicroscope in the laboratory. Dissection for counting mature ovarian eggs of 1-d-old
E. erythrinae females was also done to determine potential fecundity of newly emerged female (n = 5). Dissections were made in saline solution [
22].
2.8. Host specificity testing
All host specificity testing for
E. erythrinae was conducted in the HDOA Insect Containment Facility (minimum temperature 18.7 C°, maximum temperature 24.1 C°, minimum RH 61.6 %, maximum RH 84.3 %, Light 12:12, D:L). Tests started on the second generation of parasitoid rearing. The objective was to determine if this parasitoid would attack any non-target gall-forming insects in Hawaii. Because
E. erythrinae attacks eulophids, we checked the Hawaiian eulophid fauna for possible nontarget host use. The endemic Hawaiian eulophid species listed in the Hawaiian Terrestrial Arthropod Checklist [
23], are not gall-formers, and therefore were not included in the tests [
24,
25].
Sympiesis (
= Ophelinus)
mauiensis (Ashmead) is a parasitoid of Lepidoptera,
S. hawaiiensis (Ashmead), of unknown biology,
Pauahiana lineata Yoshimoto and
P. maculatipennis (Ashmead) attack lepidopterous leaf miners;
P. swezeyi Yoshimoto, a parasitoid of
Trioza, psyllids; and
P. metallica Yoshimoto is of undetermined habit [
26].
Not many gall forming insects occur in Hawaii and could be considered for nontarget testing. The seven gall-forming insects tested included one endemic Hawaiian psyllid, four beneficial species used for weed biological control (three fruit flies of Diptera: Tephritidae, and one eriococcid scale (Hemiptera: Eriococcidae), and two immigrant wasps, one agaonid (Hymenoptera: Agaonidae) and one eulophid (Hymenoptera: Eulophidae),
Table 1. Insect galls used in testing were exposed as whole plants infested in the laboratory or as fresh branch cuttings collected from the field. Galled plants were used for
Eutreta xanthochaeta ex.
Lantana (life cycle duration was 7–9 weeks),
Procecidochares alani ex. Hamakua pamakani (life cycle duration 5–7 weeks),
Procecidochares utilis ex. Maui pamakani (both life cycle duration 5–7 weeks), and
Tectococcus ovatus ex. strawberry guava (life cycle duration 4–6 weeks). Galled branch cuttings were used for
Josephiella microcarpa ex. Chinese banyan,
Ophelimus sp. ex. eucalyptus, and
Trioza sp. ex. ohia. The life cycle of gall-formers exposed as cuttings contained a range of immature stages (larva, pupae, pharate adults) revealed by microscopic dissections of some of these galls before exposure. Attempts to infest plants in the laboratory with the latter three insect species were unsuccessful. The control insect was laboratory reared EGW ex.
Erythrina variegata plants. All insects tested were exposed as live immatures in their galls. Plant cuttings were placed in glass bottles (30 ml) containing a nutrient solution (Floralife, 10 grams/liter distilled water,
www.floralife.com) to extend their freshness.
Host specificity evaluations were based on choice tests that would best represent the field situation. A plant or cutting infested with one of the seven non-target species (test) and an EGW-infested
E. variegata plant (control) were placed side-by-side in a screened cage (42 x 42 x 66 cm, 70 mesh screens). Five mated, naïve
E. erythrinae females ( ≤ 7 d old age) were taken from a laboratory colony and placed in the cage with honey as a food source and water provided. Counts were made of
E. erythrinae females visiting each plant and recorded separately as landing on the plant (leaves or galls). Six daily counts were made at successive hourly intervals for two consecutive days. Each count was made by observing the number of females on each plant only at that moment. The counts were started on the first day of exposure for six counts in the day (8:00 AM–2:00 PM). If any of the five parasitoids died within the first week of exposure, they were replaced with new ones. Parasitoids were then removed after two weeks, and the test and control plants were placed in separate cages to determine new parasitoid emergence. There were 4–5 replicates for each insect tested. After one month, all galls were dissected and examined under a Nikon SMZ-745 259 stereomicroscope for any evidence of parasitism by
E. erythrinae. Dead cadavers with parasitoid oviposition or feeding marks or the presence of parasitoid immatures, were revealed by dissection (
Figure 2C).
2.9. Colonization records on the islands.
A table of parasitoid release on the islands with numbers of wasps released on different host plants, dates of release, and dates of establishment is provided. Parasitoids were taken from the insectary in Honolulu in screen cover vials (33 ml) with about 20 pairs per vial, placed in a cooler for field release on different islands. Infested plants and total released wasps were recorded for every island. To follow up on parasitoid recovery, infested leaves were taken to the laboratory in paper bags and cooler to Honolulu and emerged parasitoids were tallied for establishment dates. None of the Hawaiian eurytomids parasitize the EGW and differ from
E. erythrinae in antennal and leg coloration and would thus be easily distinguished from
E. erythrinae. Emerging
E. erythrinae were confirmed by matching the morphological description: Female color mostly black except for the yellow scape, pedicel, pro-coxae, and meso-coxae; Male color black, yellow areas as described for female (
Figure 2B and
Figure 5C [
20]).
2.10. Statistical analysis and vouchers
An analysis of variance was used to assess the potential significance of differences in the number of parasitoids produced by parasitism on the different hosts exposed to the wasps. Frequency of visits and parasitism were statistically analyzed using a One-Way ANOVA Test. Means were separated by Tukey’s standardized range honestly significant difference test and t-test at α = 0.05 level. Percentage data were arcsine square-root transformed before analysis. All analyses were conducted using SAS JMP Version 11 [
27].
Voucher specimens of Eurytoma erythrinae were deposited in the insect reference collection of the HDOA, the Bernice P. Bishop Museum, and UH insect collection, Honolulu, Hawaii. Additional Depositories are USNM (National Museum of Natural History, Smithsonian Institution, Washington, D.C.).
4. Discussion
Here we presented important results on reproductive biology of
E. erythrinae and the host specificity studies that provided supporting data for safe release in Hawaii. We used a Tanzanian strain of
Eurytoma erythrinae for this study. Variation in this wasp was found among specimens collected during the surveys from different regions in Africa. Females varied in length from 2.7–3.0 mm, larger than the laboratory reared colony. In females, the fuscous area on the pro-femur can form a band in the middle half of the femur. The pro-coxa and meso-coxa may be entirely dark brown. Some South African males have a more yellowish coloration to the facial setation, and the hind-femur having a brownish band in the medial half. Male specimens from Ghana and Nelspruit, South Africa’s collection were different in its completely brown meta-femur [
20].
Eurytoma erythrinae was collected in Tanzania during January 2006 from hosts appeared to be a color variant of EGW in Hawaii (i.e., males were typical, female wasps exhibited slightly longer ovipositor, yellow genae, yellow front coxae, and four setae on cercus, MMR Unpublished). Kim et al. (2004) [
1], in their description of EGW, recognized the color variation in specimens from Mauritius and Singapore. Therefore, we prioritized rearing a Tanzanian-origin colony of
E. erythrinae in the HDOA Insect Containment Facility.
Longevity studies showed
E. erythrinae adults to be relatively long-lived when fed honey. Females and males survived much longer than the survivorship of their hosts. When the females had access to honey and EGW galls for host-feeding, their longevity increased to an average of 51d. This is known in several hymenopteran that host-feeding parasitoids can replenish nutrients for enhanced fecundity and prolonged longevity during the adult stage [
32]. The nutrients provided by the host body fluids very likely contributed to this extended life. This observation was further proven by male longevity, which do not host-feed and lived shorter period than females.
The life cycle of E. erythrinae (18 d) was well synchronized with the EGW (20 d) such that parasitoids emerge when hosts are available. The 37-d oviposition period also allows the female to exert control over two generations of EGW. The ability of a larva to tunnel into adjacent gall chambers and feed on several prey is advantageous and probably contributes to the dominance of this parasitoid in the native lands. Host-feeding by E. erythrinae females and the resulting death of the host also add to EGW mortality.
A male biased sex ratio suggests that more males are needed for mating, because of their shorter life span, and females may mate several times. Polyandry is common among hymenopteran parasitoids under laboratory conditions [
33]. The higher percentage of males may also indicate that the female mated only once, and after the sperm was used, only unfertilized (male) eggs were deposited. Sex ratio of EGW was male biased in the field (15.6% females) and insectary colony (25.6% females), [3, 16, and unpublished field records].
Host specificity studies showed
E. erythrinae to attack only the EGW in Hawaii. Females had little attraction to plants with galls of non-target species and clearly preferred
Erythrina plants with EGW galls. No parasitoid emergence resulted from exposures of non-target species to the parasitoid. All dissections indicated no evidence of parasitism. Host range in Africa may include several
Erythrina gall formers as revealed from our collections and literature [
34]. Therefore, host rage testing in other countries may return different results from Hawaii and this should be carefully investigated when considering this parasitoid for introduction in new locations.
Examination of host-plant relationships of EGW using 71 different
Erythrina species in Botanical Gardens of Hawaii supported an African origin for EGW, excluding 11 countries of potential origin [
15]. However, Messing et al. 2009 [
15] disputed that the Tanzanian collections by HDOA surveys could not be resolved as the same EGW in Hawaii based on feeding studies conducted with
Q. erythrinae in Hawaii on its Tanzanian host plant species,
Erythrina abyssinica cultivated in Hawaii. Therefore, exotic natural enemies should be used cautiously [
35]. The African origin remains supported only by morphological identification [
5]. Lin et al. 2021, [
36] in their recent study of molecular phylogeny and DNA haplotype of several EGW samples to determine the origin of EGW suggested that the Tanzanian taxa of
Q. erythrinae is more primitive than the other taxa in their study. They support the hypothesis that
Q. erythrinae has an African origin and originated from Tanzania or its neighboring regions [
36].
The parasitoid also had variant coloration.
Eurytoma erythrinae was collected from several countries in Africa during our surveys (South Africa, Tanzania, Ghana). However, the parasitoids were associated with different
Quarastichus species across this range, and these were probably parasitoids of
Q. gallicola Prinsloo & Kelly and
Q. bardus Prinsloo & Kelly, having been reared in association with both species. Some of the parasitoids were already known in the South African National Collection of Insects and were considered inquilines of unknown habits [
34].
The success of the released parasitoid was exceptional in Hawaii and considered by some biocontrol researchers as the best in decades, with the added benefit that it improved the public perception of classical biocontrol in Hawaii [
37,
38]. Results of several year of post-monitoring showed the parasitoid is well established and naturally dispersing everywhere on the islands reducing the impact of EGW on the native wiliwili (
Figure 5A–F, photos before and after release [
39].
Eurytoma erythrinae saved
E. sandwicensis trees from destruction and possible extinction, without expensive toxic chemical control [
39,
40]. The successful biocontrol of EGW in Hawaii offers opportunities for other countries to import this parasitoid. Japan was the first to introduce
Eurytoma erythrinae from Hawaii for biocontrol program in the islands of Sumuzy, Isigaci, and Irimuti, where the flower of
E. variegata is the symbol of the Okinawa Region [
35]. The mainland USA has two native
Erythrina species attacked by EGW (
E. herbacea L. &
E. flabelliformis Kearney) in need of biocontrol introductions. The neotropics are a center of endemism for
Erythrina and 24 species are native to Mexico. They are susceptible to EGW and should be considered at risk [
41].
Figure 5.
A Dried wiliwili forest Erythrina sandwicensis O.Deg, Lahaina Lua, Maui Island, December 2008; B) Massive infestation on Ulupalakua Maui Island, December 2008; C) Lateral habitus of Eurytoma erythrinae released, female (upper), male (lower); D) Infestation on flowers and seedpods of wiliwili still needs higher parasitism, reason for release a second parasitoid; E) wiliwili recovery after wasp establishment at Koko Head crater, Oahu Island, December 8, 2015; F) wiliwii yellow flowering tree Koko Head crater, Oahu Island, December 2020 photo. Photos credited to Mach Fukada, Maui Island Entomologist (A, B), Walter Nagamine (C), and Juliana Yalemar (D-F). .
Figure 5.
A Dried wiliwili forest Erythrina sandwicensis O.Deg, Lahaina Lua, Maui Island, December 2008; B) Massive infestation on Ulupalakua Maui Island, December 2008; C) Lateral habitus of Eurytoma erythrinae released, female (upper), male (lower); D) Infestation on flowers and seedpods of wiliwili still needs higher parasitism, reason for release a second parasitoid; E) wiliwili recovery after wasp establishment at Koko Head crater, Oahu Island, December 8, 2015; F) wiliwii yellow flowering tree Koko Head crater, Oahu Island, December 2020 photo. Photos credited to Mach Fukada, Maui Island Entomologist (A, B), Walter Nagamine (C), and Juliana Yalemar (D-F). .
Kaufman, et al. 2020 [
39] in their monitoring study of
E. erythinae in Hawaii, highlighted the limited rates of parasitism of galls on flowers and seedpods (
Figure 5D) and supported the release of a second parasitoid,
Aprostocetus nitens. An application with the HDOA for final permits allowing the release of
A. nitens from the Containment Facility is in progress at time of writing. Studies have shown no adverse effects of
A. nitens on any nontarget species in Hawaii.
Author Contributions
Conceptualization, W.N, J.Y, M.R. and M.W.; methodology, W.N., M.R; software, WN, M.R; validation, M.R. and W.N; formal analysis, M.R. and W.N.; investigation, W.N, J.Y., M.R., and M.W.; resources, M.R., and M.W; data curation, M.R., and W.N.; writing—original draft preparation, W.N., and M.R.; writing—review and editing, W.N., J.Y., M.R, and M.W.; visualization, W.N. and M..R.; supervision, W.N, and J.Y.; project administration, W.N.; funding acquisition, M.W.; All authors have read and agreed to the published version of the manuscript.