Introduction
Ulleungdo is a tholoid volcanic island located 130.3 km to the east of the Korean mainland (Kwon, 2012). It spans approximately 73 km2 and is divided into three administrative divisions of 3 eup/myeon and 9 ri. Its unique characteristics sustain a native ecosystem through various indigenous and anagenesis-driven species (Choi et al., 1998; Takayama et al., 2013; Yang et al., 2019). Regular investigations of the island’s diverse biota have been conducted since the 1950s (Byun et al., 1996; Choi et al., 2022; Kim & Kwon, 2013; Lee et al., 2006; Lim et al., 2013). Approximately seven comprehensive surveys conducted between 1955 to 2012 revealed a wide variety of insect fauna on Ulleungdo, with a total of 18 families, 179 genera, and 1,177 species. The Lepidoptera, Coleoptera, and Hemiptera orders exhibited high diversity (Lim et al., 2013). A total of 124 species of Hymenoptera have been recorded, including 8 species of social wasps across 3 genera (Lim et al., 2013).
Approximately 5,000 species of Vespidae have been recorded worldwide (Carpenter, 1982), with 98 species in 3 subfamilies found in Korea (KSAE & ESK, 2021). Of these, 30 social species (including 3 subspecies) of Vespinae and Polistinae are documented (Choi et al., 2013; Kim, 2023). Social wasps, as apex predators, play a role in regulating the insect ecosystem balance (Sumner et al., 2018). However, they are recognized as dangerous and troublesome insects to humans often using their poisonous stings to attack in groups when threatened (Choi 2021; Choi et al., 2019). As urban gardens and green parks expand, the presence of social wasps in areas populated by humans has grown, posing an increased threat (Choi et al., 2012; Kim et al 2019; Komonen et al., 2020). According to Choi et al. (2019), between 2010 and 2014 in Korea, the average annual number of wasp nest removals by 119 rescue teams was 96,647, the number of wasp sting injuries was 15,772, and the number of wasp sting-related fatalities was 9.8, constituting a significant public health concern.
Moreover, as a representative predator of honey bees, the genus Vespa has sparked various social problems and inflicted severe economic damage on the beekeeping industry (Laurino et al., 2020). Since the invasive hornet Vespa velutina nigrithorax du Buysson invaded Korea in 2003, its impact has increased dramatically (Choi et al., 2012; Kim et al., 2006). Despite the widespread impact of social wasps across South Korea, there has been no previous investigation into their diversity, impact, or the introduction of invasive alien wasps on the remote island of Ulleungdo.
Therefore this study collected wasps from all areas of Ulleungdo to assess species diversity and their effects in the Ulleungdo region. Additionally, the study analyzed the number of requests for wasp nest removal made to Ulleungdo emergency services call centers (ESCCs) and incidents of attacks on humans to understand the impact of social wasps.
Materials and Methods
Sample collection
A total of six wasp collection events were conducted on Ulleungdo. Wasp traps were installed at 12 locations from May 18 to 20, 2022, and collected monthly thereafter. The traps were removed after the last collection between October 22 and 24, 2022.
Regarding survey points, one or two traps were installed for each ri to evenly survey the entire area, including Seonginbong Peak, Ulleungdo’s iconic mountain. Initially, four traps (Trap No. 1-4) were installed around the trail from Dodong to Seonginbong, and the remaining traps (Trap No. 5-12) were allocated to each ri (Fig. 1).
Collection method
The wasp traps were installed by drilling a square hole (5×5 cm) in the upper half of a 2 L plastic barrel, into which a mixture of grape juice (500 mL) and yeast was added. Captured wasps were washed with water, immersed in 95% alcohol for preservation, and subsequently identified. Moreover, after collecting the wasp traps, any wasps not captured by the traps were collected through a 30-minute sweeping effort using an insect net in the grassy areas surrounding the traps. Furthermore, we scoured for wasp nests by visually inspecting the eaves of nearby houses, cracks in walls, grassy terrain, and cliffs.
Emergency call data
Information regarding calls for wasp nest removal in the Ulleungdo area was provided by the ESCCs under the National Fire Service. The data encompassed the past five years (2018-2022) and was categorized by year, month, and location. This data was subsequently analyzed and mapped. Additionally, the number of reports was analyzed in relation to unit area and population. Reports concerning other bees, such as bee swarms, were excluded from the dataset, focusing solely on reports pertaining to the removal of social wasp nest.
Identification
Wasps collected via traps and insect nets were identified using identification keys from Archer (2012), Choi (2004), Kim (2001), Kim et al. (2006), and Matsuura and Yamane (1990). Additionally, as the information on the number of wasp nest removals was obtained from telephonic data, it was not used for species identification. However, some nests were reported via calls to 119 rescuers, and information on species at the genus level was secured through photo collation.
Results
Diversity of social wasps collected from Ulleungdo
A total of 5,068 individuals belonging to two genera and two species were collected through five trappings at 12 locations on Ulleungdo Island. Vespa simillima simillima Smith exhibited the highest count, with 3,961 individuals (78.2%) collected (Fig. 2A), followed by Vespula flaviceps flaviceps (Fig. 2C) with 1,107 individuals (21.8%; Table 1).
By location, 942 and 936 individuals were collected from traps 1 and 3, respectively (the largest number of individuals collected), whereas only 42 and 39 individuals were collected from traps 8 and 9, indicating a significant variation. Furthermore, the majority of individuals collected by sweeping were either V. simillima simillima or Vl. flaviceps flaviceps, although five individuals of Polistes snelleni de Saussure (Fig. 2D) were collected at location 5. Although nests were searched for under house eaves, between wall gaps, and on cliffs, no nest traces were found except one V. simillima simillima nest found on a cliff (Fig. 2B). Consequently, this survey yielded a total of 5,132 wasps representing three genera and three species.
Emergency call data for social wasp nest removal in Ulleungdo
Over the past five years (2018-2022), a total of 60 emergency calls were made for wasp nest removal on Ulleungdo. By year, in 2018, 2019, and 2022, the number of cases appeared similar (17-20), but it notably decreased in 2020 and 2021 with only two and four cases, respectively (Fig. 3).
Examining the monthly records, emergency calls initiated in June, peaked in August, and then decreased. In particular, the number of calls in July (18 cases), August (23 cases), and September (11 cases) accounted for 87% of the total reports (Fig. 4).
In terms of regions, the Dodong-ri area reported the most cases with 22, followed by Jeodong-ri with 10 cases. All other regions reported fewer than 10 cases, with Namseo-ri and Hyeonpo-ri recording the fewest cases, with two each (Fig. 5). When evaluating the number of reports per unit area, Dodong-ri had the highest ratio of 3.55, followed by Jeodong-ri with 1.35. However, in terms of the number of reports per population, Na-ri had the highest ratio of 3.00, followed by Namseo-ri with 1.00. Conversely, Dodong-ri and Jeodong-ri, which had the highest number of reports, exhibited very low numbers, with 0.51 and 0.53, respectively (Table 2).
Discussion
Diversity of social wasps in Ulleungdo
Since Cho (1955), when Vespidae species were first recorded on Ulleungdo, a total of nine species of three genera in two subfamilies have been documented in the list of social wasps on Ulleungdo to date (Table 3; Cho, 1955; Choi, 2023; Lee & Kwon, 1981; Lee et al., 2006; Lim et al., 2013; Won et al., 2023). However, as stated by Choi et al. (2013), the Vespidae species list in Korea has undergone significant revisions, with the inclusion of synonyms, new species, unrecorded species, and invasive species.
Consequently, when examining social wasp checklists in a specific area, entomologists and the general public (except some wasp taxonomists) often rely on outdated taxonomic information, potentially leading to errors in identification. This undermines the reliability of many of the recorded data for existing social wasps.
For instance, when reviewing the species list in Table 3, Vespula flaviceps lewisii Smith was reidentified as Vl. flaviceps flaviceps by Choi et al. (2013). Moreover, Vespula rufa schrenckii Radoszkowski is the rarest species in Korea, primarily found in the highlands of Gangwon-do and northern Gyeongbuk. Therefore, the presence of this species on Ulleungdo is highly unlikely.
Additionally, Polistes jadwigae jadwigae Dalla Torre was once considered a synonym for Polistes yokahamae Radoszkowski by Kojima and Hagiwara (1998). However, in the past, it was often misidentified as Polistes rothneyi koreanus van der Vecht (Choi et al., 2013). Therefore, most of the species categorized under the subgenus Gyrostoma are highly likely to be P. rothneyi koreanus.
Hence, despite considerable efforts made throughout Ulleungdo to confirm the distribution of P. rothneyi koreanus, neither individuals nor any signs of nests were discovered. Although some information on its existence was obtained through photo comparisons of nest removal by rescue teams at the Ulleungdo fire station, further verification is necessary.
Polistes olivaceus De Geer is a species not naturally found in Korea, but its continuous recording for approximately 50 years poses questions regarding the reliability of species identification in the genus Polistes. Furthermore, as Polistes japonicus japonicus de Saussure and Polistes mandarinus de Saussure are representative species that are commonly misidentified by domestic entomologists, their records in Ulleungdo are also highly dubious.
In contrast, it appears quite unusual that V. simillima simillima and Vl. flaviceps flaviceps, which dominated the results of this survey, are absent from the collection records of Ulleungdo in the past. It remains uncertain whether this absence is due to past misidentifications by entomologists or if these species have been recently introduced from the mainland and have since thrived. Additionally, there is currently no way to ascertain whether the Polistes species recorded in the past were indeed misidentified or have vanished for specific reasons.
Therefore, the findings of this survey indicate that there are currently three species of social wasps belonging to three genera in Ulleungdo. Furthermore, additional species will need to be confirmed through further investigations.
Removal of wasp nests on Ulleungdo
Over the past five years, there have been 60 reports for wasp nest removals on Ulleungdo, averaging 12 per year. This number does not significantly differ from the mainland (Choi et al., 2012; 2019). The limited inflow and outflow of external wasp populations due to the geographical characteristics of islands likely contribute to the consistent number of wasp colonies that occur each year.
When we examine the yearly data, the numbers for 2018, 2019, and 2022 appear relatively high, while in 2020-2021, they dropped significantly. By region, it was observed that Dodong-ri and Jeodong-ri reported the highest numbers. As the number of wasp nest removals is not a measure of the number of natural occurrences of wasp nests, but the number of calls made, it is inevitably influenced by the activity of the individuals encountering the wasp nest. Consequently, given that the number of reports tends to be higher in areas with larger populations (Choi et al., 2019), it is reasonable to see higher reports in Dodong-ri and Jeodong-ri, which have the highest populations on Ulleungdo. Additionally, the sharp decline in 2020-2021 may be attributed to a significant reduction in tourist numbers and a decrease in opportunities to encounter wasp nests, as locals limited their outdoor activities because of COVID-19.
According to the life cycle of social wasps, queens emerge from winter hibernation in April to form embryonic nests, with the first workers appearing in June. The number of workers increases rapidly in July as the nest size increases. By August and September, the nest reaches its maximum size. As these nests, initially inconspicuous, become visible to the naked eye, the number of reports surges, particularly from July onwards.
Despite no reported cases of wasp stings in Ulleungdo over the past five years, it is important to note that V. simillima simillima and Vespula koreensis koreensis being the most populous native wasps in Korea, can engage in group attacks. These attacks typically occur when humans inadvertently disturb their nests or act threateningly near the nest entrance.
Therefore, if a nest is discovered in spring or early summer, it is necessary to ensure its swift removal by reporting it to the 119 rescue team. While the number of human casualties from wasp stings remains low in Ulleungdo, damage to marine products caused by yellowjackets is frequently reported. Ulleungdo is a significant hub for squid production in Korea, accounting for approximately 750 tons of squid as of 2018, which amounts to nearly 94% of Ulleungdo’s seafood sales (Kim, 2019). Yellowjackets contribute to the supply of protein to their larvae by hunting Lepidoptera larvae in the forests. However, they also collect the remains of terrestrial animals such as mammals, amphibians, fish, and annelids, as are the flesh of aquatic products such as fish, squid, and clams left on land (Matsuura & Yamane, 1990). In Ulleungdo, captured squids are left outdoors to naturally air-dry, attracting numerous yellowjackets that consume the squids’ flesh. This significantly diminishes the quality of squid products and leads to substantial economic losses (Cho, 2011). Given that these damages can persist as long as yellowjackets are present, preventive measures are imperative.
Furthermore, since 2017, only Jangwon honey bees, known as Korea’s premier beekeeping breed, have been reared, replacing the existing honey bees on Ulleungdo (Hong, 2017; Kim et al., 2015). V. simillima simillima has been documented as a major pest that preys on bees in apiaries (Choi & Kwon, 2015). However, the damage caused by this species is less severe than that inflicted by Vespa mandarinia Smith or V. velutina nigrithorax, which are typically found inland. Therefore to prevent negative impacts on beekeeping, it is necessary to continuously monitor the possible invasion of V. mandarinia or V. velutina nigrithorax, which have not been detected in Ulleungdo until now.
Acknowledgements
This work was supported by the Korea Institute of Planning and Evaluation for Technology (IPET) in Food, Agriculture, Forestry, and Fisheries through the Agriculture, Food and Rural Affairs Convergence Technologies Program for Educating Creative Global Leaders (or Project), funded by the Ministry of Agriculture, Food, and Rural Affairs (MAFRA) (grant no. 321001-03). Additionally, this study was supported by grants from the Korea National Arboretum’s Scientific Research program (KNA1-1-25, 19-1). We would like to thank Mr. CH Ma for his invaluable assistance in collecting wasps on Ulleungdo. We also extend our gratitude to Ulleungdo Rescuer JW Kim for providing essential species information on wasp nest removals on Ulleungdo Island.
References
, , (2020) Annales Zoologici Fennici Annales Zoologici Fennici, 57, 41-46 https://doi.org/10.5735/086.
Figures and Tables
Table 1
Scientific name | Trap no. | Total | |||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|
|
|||||||||||||
1 | 2 | 3 | 4 | 5 | 6 | 7 | 8 | 9 | 10 | 11 | 12 | ||
Subfamily Vespinae | |||||||||||||
Genus Vespa | |||||||||||||
Vespa simillima simillima Smith |
875 | 95 | 518 | 27 | 34 | 503 | 803 | 42 | 22 | 223 (14) |
631 | 188 (3) |
3,961 (17) |
Genus Vespula | |||||||||||||
Vespula flaviceps flaviceps Smith |
67 | 182 | 418 (36) | 30 | 37 | 153 (3) |
28 | 0 | 17 | 42 (3) |
63 | 70 | 1,107 (42) |
Subfamily Polistinae | |||||||||||||
Genus Polistes | |||||||||||||
Polistes snelleni de Saussure |
(5) | (5) | |||||||||||
Total | 942 | 277 | 936 (36) |
57 | 71 (5) |
656 (3) |
831 | 42 | 39 | 265 (17) |
694 | 258 (3) |
5,068 (64) |
Table 2
Administrative district |
Number of emergency calls | Population (100 units) |
Area (km2) | n/population | n/area |
---|---|---|---|---|---|
Dodong-ri | 22 | 43 | 6.2 | 0.51 | 3.55 |
Jeodong-ri | 10 | 19 | 7.4 | 0.53 | 1.35 |
Sadong-ri | 6 | 8 | 7.9 | 0.75 | 0.76 |
Namyang-ri | 5 | 8 | 8.7 | 0.63 | 0.57 |
Namseo-ri | 2 | 2 | 7.6 | 1.00 | 0.26 |
Taeha-ri | 3 | 7 | 10.9 | 0.43 | 0.28 |
Cheonbu-ri | 7 | 8 | 9.1 | 0.88 | 0.77 |
Na-ri | 3 | 1 | 9.2 | 3.00 | 0.33 |
Hyeonpo-ri | 2 | 5 | 6 | 0.40 | 0.33 |
Total | 60 | 101 | 73 |
Table 3
Scientific name | 1955* | 1981† | 2006‡ | 2013§ | 2023a∥ | 2023b¶ | This study |
---|---|---|---|---|---|---|---|
Subfamily Vespinae | |||||||
Genus Vespa | |||||||
Vespa simillima simillima Smith | ○ | ○ | ○ | ● | |||
Genus Vespula | |||||||
Vespula flaviceps flaviceps Smith | ○ | ○ | ● | ||||
Vl. flaviceps lewisii Smith | ○ | ||||||
Vl. rufa schrenckii Radoszkowski | ○ | ? | |||||
Subfamily Polistinae | |||||||
Genus Polistes | |||||||
Polistes jadwigae jadwigae Dalla Torre | ○ | ○ | X | ||||
P. rothneyi koreanus van der Vecht | ▲ | ||||||
P. japonicus japonicus Saussure | ○ | ○ | ? | ||||
P. mandarinus Saussure | ○ | ○ | ○ | ? | |||
P. olivaceus Geer | ○ | ○ | ○ | X | |||
P. snelleni Saussure | ○ | ○ | ○ | ● |