Journal of Ecology and Environment

pISSN 2287-8327 eISSN 2288-1220


Home Article View


Published online December 21, 2022

Journal of Ecology and Environment (2022) 46:33

Developing habitat suitability index for habitat evaluation of Nannophya koreana Bae (Odonata: Libellulidae)

Hong Geun Kim , Rae-Ha Jang , Sunryoung Kim , Jae-Hwa Tho , Jin-Woo Jung , Seokwan Cheong and Young-Jun Yoon *

Research center for Endangered Species, National Institute of Ecology, Yeongyang 36531, Republic of Korea

Correspondence to:Young-Jun Yoon

Received: September 29, 2022; Revised: December 5, 2022; Accepted: December 5, 2022

This is an Open Access article distributed under the terms of the Creative Commons Attribution Non-Commercial License ( which permits unrestricted non-commercial use, distribution, and reproduction in any medium, provided the original work is properly cited.

Background: The Korean scarlet dwarf, Nannophya koreana Bae (Odonata: Libellulidae), is anendangered dragonfly with an increasing risk of extinction owing to rapid climate changes and human activities. To prevent extinction, the N. koreana population and their habitat should be protected. Therefore, suitable habitat evaluation is important to build the N. koreana restoration project. The habitat suitability index model (HSI) has been widely used for habitat evaluation in diverse organisms.
Results: To build a suitable HSI model for N. koreana, 16 factors were examined by seven experienced researchers. A field survey for N. koreana observed sites and spatial analysis were conducted to improve the model. Five factors were finally selected by this procedure (crown density, open water surface, water depth, pioneer plant cover, and type of water source). Finally, the N. koreana HSI model was generated with the five adjusted factors based on interview, field survey, and spatial analysis. This model was validated by a current N. koreana habitat in 2021. With this model, 46 sites in Uljin-gun, Korea, were surveyed for N. koreana habitats; five sites were identified as core habitats and seven as potential core habitats.
Conclusions: This model will serve as a strong foundation for the N. koreana restoration project and as a reference for future studies on N. koreana and other endangered insect populations. Further analysis and long-term data will improve the efficacy of this model and restore endangered wildlife.

Keywords: endangered species, habitat suitability index, endemic species, Nannophya koreana, Libellulidae

Nannophya koreana Bae is a small dragonfly recently described based on morphology and mitochondrial cytochrome oxidase C subunit I (COI) gene sequences (Bae et al. 2020). A total of seven dragonflies in the Genus Nannophya (Pygmyflies), including N. koreana, are reported worldwide. Of these, four species in Australia, one in the Himalayas, and N. pygmaea have been reported worldwide (Steinmann 1997; Theischinger and Fleck 2003). N. pygmaea is distributed in Australia, tropical and subtropical areas of Southeast Asia, China, Japan, and India (Bae et al. 2020; Kim et al. 2010; Kim 2020; Steinmann 1997; Theischinger and Fleck 2003). Based on morphological and molecular studies, the Korean population of N. pygmaea was recently described as N. koreana in 2020 because it was distinguished from other populations of N. pygmaea originally described in Indonesia and China (Bae et al. 2020; Kirby 1889). N. koreana is distributed throughout South Korea except Jeju Island. However, its habitat is very limited as it prefers small wetlands located in flat areas on the mountains or hills. They often fly near water surfaces with their small body sizes, increasing the risk of local extinction caused by predators and human activities including changes of fallow paddies (Bae et al. 1999). Therefore, N. koreana has been categorized by the Ministry of Environment of South Korea since 1998 as one of the 26 endangered insect species to protect its population and habitat. Because N. koreana is enlisted as an endangered species, suitable habitat is critical for its survival at the risk of climate change and to restore its population size.

N. koreana is known as the smallest dragonfly. The nymph of N. koreana is approximately 7.3 mm long, and the adult body length is ca. 11 mm; thus, it is known as the smallest dragonfly (Bae et al. 1999). After emerging as adults, the male keeps its territory and copulates with the females that enter the territory. After copulation, the female oviposits on the surface of open water (Yabu and Nakashima 1997). After most of the N. koreana eggs have hatched during late spring and early summer, the nymphs stay underwater until they emerge as adults in late spring (Kim et al. 2010).

The habitat suitability index (HSI) was developed to evaluate the habitat environment for designated organisms in the 1980s; this index could be used to develop expectation models for organisms (U.S. Fish and Wildlife Service 1980). HSI can evaluate and predict the environmental factors that affect habitat status with quantified values to exclude any possible bias from different researchers or invalid assumptions (Gibson 2004). HSI has been applied to evaluate wildlife habitats and prevent wildfire (Brach and Kaczmarowski 2014) and landslides (Moayedi et al. 2019).

A total of 11 previous publications on the Nannophya koreana population in South Korea were retrieved by online bibliographic databases such as Google Scholar (Google) and Research Information Sharing Service with the keywords ‘Nannophya pygmaea’ and ‘Nannophya koreana’. From the previous studies, the distribution of N. koreana was reported throughout most of South Korea. N. koreana populations were observed from small mountainous wetlands and fallow paddies; their territory was comparably small (approximately 500 m2), and the home range was also small. Previous N. koreana habitats in Munkyeong and Buyeo have been reported as destroyed as well as N. koreana was observed at only five habitats in 2021 among 23 confirmed N. koreana habitats in 2017 (Oh et al. 2017). Moreover, previous N. koreana studies were limited to genetics (Bae et al. 2020), egg hatching temperature (Kim et al. 2006; Moayedi 2019), and habitat characteristics description (Cho et al. 2012; Kim et al. 2009a, 2009b; Lee et al. 2008; Kim et al. 2010; Kim et al. 2011; Kim et al. 2016; Ministry of Environment [MOE] 2009; Oh et al. 2017), because it resides and oviposits on few limited wetlands and it has been protected by government with small population size. Therefore, there is limited information available to build a model for habitat or species restoration projects.

This study developed an HSI model based on the current status of the N. koreana habitat, literature review, and interview with experienced N. koreana researchers. The developed HSI model was validated with known N. koreana habitats. In addition, 46 potential N. koreana habitats in Uljin-gun, Korea, were evaluated based on the developed HSI model. This N. koreana HSI model will serve as a primary foundation for habitat evaluation and restoration projects for endangered N. koreana in South Korea.

Research sites

Five research sites were selected to analyze habitat characteristics. Nannophya koreana was observed at these sites, and the distance between each site was at least ca. 20 km. The five research sites were located in Incheon-si (Site 1), Jincheon-gun (Site 2), Chungju-si (Site 3), Daejeon-si (Site 4), and Gokseong-gun (Site 5) (Fig. 1). N. koreana population was confirmed at all the research sites in 2021. In addition, 46 sites (30 mountainous wetlands, 5 previously observed N. koreana sites, and 11 recently fallow paddies) without current N. koreana population in Uljin-gun, Korea, were evaluated by the HSI model as potential N. koreana habitats for restoration projects. However, detailed information on the study sites is not disclosed to protect the endangered insect population.

Figure 1. Study sites of N. koreana Bae.

Selection of environmental variables

The N. koreana habitat characteristics were selected based on previous studies provided in Table 1. A total of 11 factors were identified by experienced researchers (Table 1). The experienced researchers were selected based on three criteria: individuals with a Ph.D. in insect science or related areas and at least five years of research experience in insect biology. Based on these criteria, seven experienced researchers were selected. The first round of interview was focused on the overall adequacy and importance of the selected variables as well as checking for missed variables. The second round of interview was conducted for checking the adequacy for selected habitat variable from field survey and the first round of interview. In both interviews, the priority of each variable was checked by each interviewee.

Table 1 . Environmental variables for N. koreana habitat characteristics analysis.

DistributionMore than 23 habitats have been reported, but only five sites were recently confirmed.Retrieved
Habitat typeMountainous wetlands and fallow paddies.Retrieved
Habitat area113.4–1,153.1 m2. The average area was 500 m2, which is relatively small.Retrieved
Home rangeRecently emerged adults stay at the emerging site.
Adults have a relatively small area of activity; thus, the density of adults is high in a small area.
Air temperatureRelatively wide range between 16–27°CRetrieved
VegetationOpen area without shade and tall trees.
Early transitional vegetation structures include Juncus decipiens, Murdannia keisak, Persicaria thunbergii, Typha laxmannii, and Cyperaceae.
Vegetation types for the oligotrophic state, which is the early stage of eutrophication.
Water temperatureAbove 14.3°C during the hatching period.
Optimal growth temperature is 30–35°C, which is higher than that for other dragonflies.
Open water surfaceOpen wetland with direct sunlight for water touching ovipositing.Measured
Water depthGeneral water depth is 0–10 cm, and ca. 20 cm is also possible.
The water depth has limited fluctuation throughout the year.
Water qualityThe water quality might not affect the survival of N. koreana.Measured
Risk factorsWetland reduction because of drought.
Predation by natural enemies during nymphal stages with deep water depth.
Reduction of open water surface because of high crown density or tall vegetation.
Conversion of wetland to dry land caused by ecological succession.
Developing pressure because of private land.

The 11 factors were categorized into two groups; one for field survey data and the other to retrieved from spatial information. The detailed datasets for the spatial information were retrieved from the following institutes: weather information (Korea Meteorological Administration and WorldClim), soil information (Korea Soil Information system), continuous digital topographic map (National Geographic Information Institute), forest type map (Forest Geographic Information System), and vegetation index (Environment Bigdata Platform). The Aeronautical Reconnaissance Coverage Geographic Information System was used to analyze spatial information.

Field survey

The habitat characteristics were investigated from the current N. koreana observed sites to develop the HSI model. The field survey was conducted seven times from May to August 2021. Diverse factors (open water surface, crown density, water depth, pioneer crown density, floating-leaved plant cover, water source type, and others) that can affect the N. koreana habitat were examined. Water depth was measured by ruler at three different points. Open water surface was estimated with a tape measure by two different researchers. The height of plant was measured by a tape measure by two researchers at the three points on the each study site. Other factors were retrieved from spatial information.

Developing habitat suitability index model

The major habitat factors were selected based on interview with seven experienced researchers who were provided with basic environmental information from the current N. koreana habitat. In the second round of interview, each major habitat factor was weighted to develop a suitable index and prioritized to calculate the HSI (Table S1). The weighted value for each variable was divided by the summation of the all the weighted values for all the variables. The calculated suitability index (SI) was used for building HSI for N. koreana.

Habitat analysis

Literature review

N. koreana preferred open spaces without tall trees at the beginning of the ecological succession. Therefore, various grasses, including Juncus decipiens (Buchenau) Nakai, Murdannia keisak (Hassk.) Hand.-Mazz., and Persicaria thunbergii (Siebold & Zucc.) H. Gross were identified as the dominant plant species in these habitats.

The air temperature was in the range of 16–27°C during egg hatching period. The egg hatching threshold temperature of N. koreana was 14.3°C, which is relatively warmer than that of other dragonflies. The water level for the N. koreana habitat was 0–20 cm, with minimal fluctuation. Moreover, minimal water level fluctuation is required for N. koreana survival because ovipositing occurs on water surfaces. However, the water quality was not the major factor in the N. koreana habitat. The risk factors for N. koreana habitat includes wetland reduction caused by drought and deep-water level, as well as open water reduction caused by tall plants, wetland reduction, and anthropogenic activities.

Field survey

The N. koreana habitats were measured as water depth (12.20 ± 8.04 cm [mean ± standard deviation {S.D.}]), open water ratio (60.00 ± 14.14% [mean ± S.D.]), average plant height (16.00 ± 8.22 cm [mean ± S.D.]), and percentage of pioneer crown density (2.00 ± 2.74% [mean ± S.D.]). For spatial analysis, the N. koreana habitats were summarized as altitude (163.00 ± 108.57 m [mean ± S.D.]), annual average temperature (11.40 ± 1.07°C [mean ± S.D.]), the average temperature in June (21.81 ± 0.60°C [mean ± S.D.]), the average temperature in July (21.85 ± 0.90°C [mean ± S.D.]), annual precipitation (1,662.40 ± 249.83 mm [mean ± S.D.]), precipitation in the driest month (26.80 ± 3.19 mm [mean ± S.D.]), heat index (92.27 ± 9.05 [mean ± S.D.]), and vegetation index (0.76 ± 0.03 [mean ± S.D.]) (Table 2). Based on these analyses, the N. koreana habitat was confirmed as a shallow wetland with a wide-open water surface originating from surface runoff and precipitation where Poaceae and Cyperaceae were the dominant vegetation.

Table 2 . Analysis for N. koreana habitat characteristics.

Habitat variablesSite 1Site 2Site 3Site 4Site 5Data source
Water depth (cm)310101325FS
Open water surface (%)5050705080FS
Vegetation height (cm)1510101530FS
Dominant vegetationFDPTPTEUPJFS
Pioneer crown density (%)05050FS
Water sourceSR, PSR, PSR, PSR, PSR, PFS
Altitude (m)28234306136111FS
Annual average temperature (°C)12.5410.1210.4112.1111.84KMA
June average temperature (°C)21.8821.2121.3422.7221.92KMA
July average temperature (°C)23.0920.7621.322.3221.8KMA
Annual precipitation (mm)1,405.071,698.751,505.961,643.232,058.98KMA
Warmth index102.2881.3984.3898.6894.62KMA
The driest month’s precipitation (m)2326252931WC
Normalized difference vegetation index-0.800.760.730.73KIGAM

MW: mountainous wetland; FP: fallow paddy, FS: field survey; UFL: unstocked forest land; FD: Fimbristylis dichotoma; PT: Persicaria thunbergii; EU: Eleocharis ussuriensis; PJ: Phragmites japonica; SR: surface runoff; P: precipitation; KMA: Korea Meteorological Administration; WC: WorldClim; KIGAM: Korea Institute of Geoscience and Mineral Resources.

Developing N. koreana HSI

Generating major factors for HSI

Based on the literature review and field survey, 16 habitat factors for N. koreana were presented to seven researchers. After the second round of in-depth interview, five factors: forest density, open water surface, water depth, percentage of pioneer crown density, and water source type were selected as major habitat factors (Table 3). Although fallow paddy was an important N. koreana habitat, it is a subtype of mountainous wetlands and is not an official term in the wetland classification system (Kim et al. 2013); therefore, wetland types were excluded from the major habitat factors. The vegetation height was excluded because it was highly related to the open water surface determined by crown density rate. The annual average temperature was also excluded based on comments made by the experienced researchers. In addition, the monthly average temperature for June and July (N. koreana egg hatching period), annual precipitation, and precipitation in the driest month were not selected as major habitat factors because of large annual fluctuation and insufficient research to support these factors.

Table 3 . Selecting major variables for N. koreana habitat analysis.

VariablesResult of in-depth interview with experienced researchers
Crown densityMajor factor for light reflectionAppropriate
Open water surfaceMajor factor for water touching ovipositionAppropriate
Water depthMajor factor for natural enemyAppropriate
Pioneer crown densityMajor factor for ecological succession and wetland conversionAppropriate
Water sourceMajor factor for temperatureAppropriate
Wetland typeNot suitable for wetland classification systemInappropriate
Vegetation heightOpen water surface is more important vegetation heightInappropriate
Annual average temperatureNot important because of nationwide distributionInappropriate
Monthly average temperature in June or JulyToo big annual fluctuation and lack of studiesLack of research
Annual precipitationToo big annual fluctuation and lack of studiesLack of research
Precipitation in the driest month (mm)Draught might be important but need more studiesLack of research

Developing suitable indices for major habitat factors

The suitable indices for major habitat factors were generated by in-depth interview based on the literature review and field survey (Fig. 2).

Figure 2. Suitable indices for major variables of N. koreana habitat.

(1) Crown density (SI 1)

Based on literature review and expert interview, N. koreana habitat was concluded to be found in wetlands without shade from trees. Moreover, the habitat was open to sunlight without vegetation from the past to the present. Therefore, the suitable N. koreana habitat was selected as a wetland open to sunlight (Table 4). The index was determined considering mountainous wetlands with low crown density where sunlight could reach the water surface.

Table 4 . Categories for crown densities.

ClassCrown density
LowStands where trees occupy less than 50% of the canopy area
MediumStands where trees occupy 51%–71% of the canopy area
HighStands where trees occupy more than 71% of the canopy area
NoneNon forest

Data from Forest Geospatial Information System of Korea Forest Service.

(2) Open water surface (SI 2)

During the N. koreana emerging period, the temperature was relatively high, and the adults oviposited while touching the water surface. Therefore, the exposure to open water surface was selected as the major habitat factor rather than crown density because adults also oviposited among the Poaceae and Cyperaceae stem, which did not completely cover the water surface. Based on the field survey on the five N. koreana observed sites, the exposure to open water surface was more than 50% for N. koreana habitat. Therefore, it seems that the suitable habitat should have exposure to open water surface of at least 40% during the dry season conditions.

(3) Water depth (SI 3)

Based on the literature review, the water depth of the N. koreana habitat was confirmed as less than 20 cm. The water depth is an important factor because the water temperature is closely related to the water depth during oviposition period and the possibility of fish appearance (one of the major threats to N. koreana survival). Based on field survey, the deepest water depth was confirmed as 25 cm at the Wolbongjae in Gokseong-gun, Korea. Water depth could be changed due to diverse factors, including drought, heavy rainfall, and seasonal fluctuation; therefore, the suitable water depth was presented as 30 cm and confirmed by experienced researchers.

(4) Pioneer crown density (SI 4)

Based on literature review, most of the N. koreana habitats were found in fallow rice paddies, and N. koreana preferred the early stage of the vegetation succession. Annual grasses are first introduced and followed by perennial grasses such as Juncaceae and Typhaceae at the early stage of vegetation succession in fallow rice paddies. From the field survey, perennial grasses, including Lamp rush (Juncus decipiens [Buchenau] Nakai) and Japanese moor grass (Molinia japonica Hack.), were dominant species near the flooded area, whereas short plants, including Korean persicary (Persicaria thunbergii [Siebold & Zucc.] H. Gross) and Ussuri spikerush (Eleocharis ussuriensis G. Zinserl), were located near the N. koreana habitats. The transition of fallow rice paddies to land was considered one of the major threats to N. koreana protection in previous studies; therefore, pioneer vegetation (willows and alders) cover serving as an indirect indicator for the transition of fallow rice paddy was selected as a major factor and it was examined for suitability by experienced researchers.

(5) Water source (SI 5)

Among diverse water sources, surface runoff, including runoff from spring water, was selected as a suitable water source for the N. koreana habitat, and it was examined by experienced researchers. From the literature review, N. koreana could be a tropical dragonfly, so the optimum growth temperature and low and high-temperature threshold for N. koreana were higher than that for other dragonflies. Moreover, N. koreana showed high density in a limited area with slow movement and small activity. In addition, the newly emerged adults often stay where they emerged. Therefore, the water temperature is one of the major factors for the N. koreana habitat. However, wetlands with spring water are generally low in temperature, so they are unsuitable for N. koreana. Therefore, surface runoff was suggested as a suitable water source for the N. koreana habitat.

Developing HSI model

The importance of each factor for the selected SI model was examined by experienced researchers (Table 5), and their relationship with the HSI model was established by weighting them (Equation 1).

Table 5 . Weighting on the major habitat variables based on the interview with experienced researchers.

No.Habitat variablesExpert assessment scoreWeight factor
1SI 1 (Crown density)11345332.85
2SI 2 (Open water surface)43534323.42
3SI 3 (Water depth)55434544.28
4SI 4 (Pioneer crown density)31225432.85
5SI 5 (Water source)55442243.71

HSI = 0.17 (SI 1) + 0.2 (SI 2) + 0.25 (SI 3) + 0.17 (SI 4) + 0.21 (SI 5) [Equation 1]

HSI: habitat suitability index; SI 1: crown density; SI 2: open water surface; SI 3: water depth; SI 4: pioneer crown density; SI 5: type of water source.

Habitat suitability assessment and key habitat selection

The potential 46 habitats in Uljin-gun, Korea, were evaluated based on the developed HSI. Only one potential habitat (Bongpyeong-ri (3) wetland) was evaluated as HSI point 1. Two potential habitats (Mt. Chunjuk (3) and Hwaseong-ri (2) wetlands) were confirmed as HSI point 0.9. Seven potential habitats, including Sillim-ri and Ssangjeon-ri wetlands, had the lowest HSI point of 0.38, except for nine habitats where the wetland was disturbed by human activities (Table 6).

Table 6 . HSI analysis for potential sites of N. koreana habitat in Uljin-gun.

LocationSI 1SI 2SI 3SI 4SI 5HSI
1Eumnam-ri wetland000.
2Mt. Cheonchuk (1) wetland00.
3Mt. Cheonchuk (2) wetland0.1700.
4Mt. Cheonchuk (3) wetland0.
5Mt. Cheonchuk (4) wetland0.1700.
6Osan-ri (1) wetland0.17000.170.210.55
7Osan-ri (2) wetland0.06800.
8Osan wetland (Uljin)0000.170.210.38
9Jinbok-ri (2) wetland0000.170.210.38
10Goseong-ri (2) wetland0.1700.
11Daeheung-ri wetland0.1700.
12Sillim-ri (1) wetland00000-
13Ssangjeon-ri (1) wetland000.
14Ssangjeon-ri (2) wetland00.
15Ssangjeon-ri (3) wetland00000-
16Wangpi-ri (1) wetland00.20.2500.210.66
17Wangpi-ri (2) wetland0000.170.210.38
18Sanpo-ri (2) wetland-
19Sanpo-ri (2) wetland-20.0680.
20Jinbok-ri (1) wetland0.0680.
21Sanpo-ri (1) wetland000.2500.210.46
22Nagok-ri (1) wetland00000-
23Nagok-ri (2) wetland000.2500.210.46
24Hujeong-ri wetland000.
25Yongjang wetland (Uljin)0.1700.
26Hwaseong-ri (2) wetland0.
27Bongpyeong-ri (1) wetland0000.170.210.38
28Bongpyeong-ri (2) wetland0.1700.
29Bongpyeong-ri (3) wetland0.
30Samsan-ri wetland0000.170.210.38
31Sadong-ri wetland00000-
32Ogok-ri (2) wetland0.1700.
33Deogin-ri (2) wetland-10.0680.
34Deogin-ri (2) wetland-
35Seongu-ri wetland00000-
36Seongu-ri (1) wetland0000.170.210.38
37Myeongdo-ri (1) wetland-100000-
38Myeongdo-ri (1) wetland-2000.
39Myeongdo-ri (1) wetland-30.0680.
40Myeongdo-ri (2) wetland00.
41Goseong-ri (1) wetland00000-
42Sillim-ri (2) wetland-100000-
43Sillim-ri (2) wetland-
44Myeongdo-ri (3)00000-
45Hwaseong-ri (1) wetland000.2500.210.46
46Ogok-ri (1) wetland0000.170.210.38

HSI: habitat suitability index; SI 1: crown density; SI 2: open water surface; SI 3: water depth; SI 4: pioneer crown density; SI 5: type of water source.

With rigorous habitat analysis, four habitats among the five N. koreana habitats observed in 2021 were evaluated as HSI point 1 (Table 7). The HSI for potential habitat in Incheon-si was evaluated as 0.83 because of the wrong scale of crown density data. Based on the field survey, the crown density was zero; thus, the HSI should be corrected.

Table 7 . HSI analysis for the six recent N. koreana observed sites.

No.LocationSI 1SI 2SI 3SI 4SI 5HSI
1Uljin, Myeongdo-ri (2) wetland00.

HSI: habitat suitability index; SI 1: crown density; SI 2: open water surface; SI 3: water depth; SI 4: pioneer crown density; SI 5: type of water source.

In Uljin-gun, four N. koreana potential habitats among the five observed N. koreana habitats were disturbed by human activities, including construction and cultivation. However, the HSI point for Myengdo-ri 2 wetland (a previously confirmed habitat) where N. koreana was not observed in 2021 was 0.83. Therefore, potential habitats with an HSI point of more than 0.83 was categorized as core habitats for N. koreana. In addition, potential habitats in Uljin-gun with an HSI point of more than 0.8 were selected as potential core habitats for N. koreana (Fig. 3).

Figure 3. Five core habitats and seven potential core habitats of N. koreana in Uljin-gun.

This study developed an HSI model for endangered insects through literature review, field survey, and interview with experienced researchers to evaluate the core habitats of Nannophya koreana. Based on previous studies, the primary habitat factors were selected. Among the selected primary factors, crown density, open water surface exposure, water depth, pioneer crown density, and water source type were selected as habitat factors by experienced researchers and GIS data generation. The SI model was developed with these five habitat factors. Based on the SI model, the HSI model for N. koreana was developed. The developed HSI model for N. koreana was applied to the 46 potential N. koreana habitats in Uljin-gun. Five core habitats and seven potential core habitats were established based on the HSI model for N. koreana. Most of these selected sites were located in the middle and northern part of Uljin-gun, Korea, where the altitude is generally high, and new fallow paddies are increased because of the reduction of the human population.

Among 46 potential habitats for N. koreana in Uljin-gun, the HSI value was 1 for Bongpyeong-ri (3) wetland and the value was 0.9 for Mt. Cheonchuk (3) wetland and Hwaseong- ri (2) wetland. In addition, as the HSI value was 0.83 for Myeongdo-ri (2) wetland in Uljin-gun, where N. koreana was observed in the past, five potential habitats (Bongpyeong-ri (3) wetland, Mt. Cheonchuk (3) wetland, Hwaseong- ri (2) wetland, Deogin-ri (2) wetland-1, and Myeongdo-ri (2) wetland) with HSI value of 0.83 or higher were selected as the core habitat for N. koreana in Uljin-gun.

However, we determined seven potential habitats (Yongjang wetland, Bongpyeong-ri (2) wetland, Goseong-ri (2) wetland, Daeheung-ri wetland, Mt. Cheonchuk (4) wetland, and Ogok-ri (2) wetland) for N. koreana with the HSI value more than 0.8 because of the error range from the field survey as well as spatial data scale.

Based on this study, the potential and surrogate habitats for N. koreana could be more effectively evaluated with scientific evidence to protect this endangered insect population. However, the available habitat information on N. koreana habitats was insufficient to improve the quality of the HSI model because of the limited previous studies and possible study sites. Therefore, a long-term study on the current habitat and scouting for unknown populations will improve the efficacy of the current model. In addition, a verification study on the current model and development of restoration strategies for N. koreana should be followed to preserve vulnerable dragonflies in the ecosystem.

HGK did writing-original draft, review & editing, RHJ did investigation, data curation, writing-review. SK did investigation and data curation. JHT did methodology and writing review, JWJ did investigation and data curation. SC did conceptualization and writing-review & editing. YJY did conceptualization, investigation, and writing-review & editing.

  1. Bae YJ, Yum JH, Cha JY, Yoon IB. Morphology, habitat, and distributional records of Nannophya pygmaea Rambur (Libellulidae, Odonata). Korean J Entomol. 1999;29(4):287-90.
  2. Bae YJ, Yum JH, Kim DG, Suh KI, Kang JH. Nannophya koreana sp. nov.(Odonata: Libellulidae): a new dragonfly species previously recognized in Korea as the endangered pygmy dragonfly Nannophya pygmaea Rambur. J Species Res. 2020;9(1):1-10.
  3. Brach M, Kaczmarowski J. Suitability of the HSI model for the analysis of the forest fire spread. Sylwan. 2014;158(10):769-78.
  4. Cho KT, Kim HW, Kim HR, Jeong HM, Lee KM, Kang TG, et al. Landscape ecological characteristics of habitat of Nannophya pygmaea Rambur (Libellulidae, Odonata), an endangered species for conservation. J Wetl Res. 2012;14(4):667-74.
  5. Gibson LA, Wilson BA, Cahill DM, Hill J. Modelling habitat suitability of the swamp antechinus (Antechinus minimus maritimus) in the coastal heathlands of southern Victoria, Australia. Biol Conserv. 2004;117:143-50.
  6. Kim DG. Research history of Nannophya Rambur (Odonata: Libellulidae): a recently discovered species in addition to Nannophya koreana Bae in Korea. Korean J Environ Biol. 2020;38(2):308-14.
  7. Kim DG, Oh KC, Lee HG. Mujechi-swamp, a new nest of Nannophya pygmaea Rambur. Changwon: Ministry of Environment (MOE); 2016.
  8. Kim DG, Yoon TJ, Oh CG, Kim JG, Lee EH, Bae YJ. Laval growth rate of Nannophya pygmaea (Odonata: Libellulidae), an endangered dragonfly in Korea. Korean J Ecol Environ. 2009b;42(3):290-4.
  9. Kim DG, Yum JW, Yoon TJ, Bae YJ. Effect of temperature on hatching rate of Nannophya pygmaea eggs (Odonata: Libellulidae). Korean J Appl Entomol. 2006;45(3):381-3.
  10. Kim MH, Han MS, Choi CM, Bang HS, Jung MP, Na YE, et al. Flora and life form of habitats for Nannophya pygmaea Rambur. Korean J Environ Agric. 2010;29(2):206-13.
  11. Kim TS, Jeong JW, Moon SK, Yang HS, Yang BG. Introduction to national mid-term fundamental plan for wetlands conservation and management. J Wetl Res. 2013;15(4):519-27.
  12. CrossRef
  13. Lee EH, Jang HK, Park MY, Yoon JH, Kim JG, Bae YJ. A preliminary study on a restoration of habitats for Nannophya pygmaea Rambur (Odonata: Libellulidae). Korean J Environ Ecol. 2008;22(1):35-42.
  14. Moayedi H, Osouli A, Bui DT, Foong LK, Nguyen H, Kalantar B. Two novel neural-evolutionary predictive techniques of dragonfly algorithm (DA) and biogeography-based optimization (BBO) for landslide susceptibility analysis. Geomat Nat Hazards Risk. 2019;10(1):2429-53.
  15. Oh KC, Ro KH, Lee HG, Kim DG. Suggestions for protecting and preserving the level II endangered species Nannophya pygmaea in Korea. Korean J Environ Biol. 2017;35(4):545-8.
  16. Steinmann H. World catalogue of Odonata. Vol. 2, Anisoptera. Berlin: Walter de Gruyter; 1997.
  17. Theischinger G, Fleck G. A new character useful for taxonomy and phylogeny of Anisoptera (Odonata). Bull Soc Entomol Fr. 2003;108(4):409-12.
  18. U.S. Fish and Wildlife Service. Habitat as a basis for environmental assessment: 101 ESM. Washington, D.C: Division of Ecological Services U.S. Fish and Wildlife Service; 1980.
  19. Yabu S, Nakashima A. Ecological studies on the conservation of Nannophya pygmaea Rambur populations and habitats. J Jpn Inst Landsc Archit. 1997;60(4):324-8.

Share this article on :

Related articles in JEE

Close ✕

Journal of Ecology and Environment

pISSN 2287-8327 eISSN 2288-1220