Volume 4, Issue 2 pp. 143-153
RESEARCH ARTICLE
Open Access

Endemic Creature Under the Risk of Extinction: A Case Study on Gekko badenii in Vietnam

濒危特有物种案例研究:越南 金壁虎 (Gekko badenii)

Hai Ngoc Ngo

Corresponding Author

Hai Ngoc Ngo

Institute of Biology, Vietnam Academy of Science and Technology, Hanoi, Vietnam

Correspondence: Hai Ngoc Ngo ([email protected])

Contribution: Conceptualization, Formal analysis, Methodology, Software, Writing - original draft, Writing - review & editing

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Quyen Hanh Do

Quyen Hanh Do

Institute of Biology, Vietnam Academy of Science and Technology, Hanoi, Vietnam

Contribution: Conceptualization, Formal analysis, Methodology

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Thanh Phuong Thi Bui

Thanh Phuong Thi Bui

Institute of Biology, Vietnam Academy of Science and Technology, Hanoi, Vietnam

Contribution: Methodology

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Cuong The Pham

Cuong The Pham

Institute of Biology, Vietnam Academy of Science and Technology, Hanoi, Vietnam

Contribution: Conceptualization, Funding acquisition

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Truong Quang Nguyen

Truong Quang Nguyen

Institute of Biology, Vietnam Academy of Science and Technology, Hanoi, Vietnam

Graduate University of Science and Technology, Vietnam Academy of Science and Technology, Hanoi, Vietnam

Contribution: Conceptualization, Writing - original draft, Writing - review & editing

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Huy Quoc Nguyen

Huy Quoc Nguyen

Institute of Biology, Vietnam Academy of Science and Technology, Hanoi, Vietnam

Chengdu Institute of Biology, Chinese Academy of Sciences, Chengdu, China

University of Chinese Academy of Sciences, Beijing, China

Contribution: Methodology

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Laurenz Rafael Gewiss

Laurenz Rafael Gewiss

Federal Agency for Nature Conservation, CITES Scientific Authority, Bonn, Germany

Contribution: Conceptualization, Funding acquisition, Writing - original draft, Writing - review & editing, Methodology

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Mona van Schingen-Khan

Mona van Schingen-Khan

Federal Agency for Nature Conservation, CITES Scientific Authority, Bonn, Germany

Contribution: Conceptualization, Funding acquisition, Methodology, Writing - original draft, Writing - review & editing

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Thomas Ziegler

Thomas Ziegler

Institute of Zoology, University of Cologne, Cologne, Germany

Cologne Zoo, Cologne, Germany

Contribution: Conceptualization, Funding acquisition, Writing - review & editing

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First published: 18 April 2025

Editor-in-Chief & Handling Editor: Ahimsa Campos-Arceiz

ABSTRACT

en

As one of 17 Gekko species known from Vietnam, the Golden gecko—G. badenii, a species endemic to the South of Vietnam, was discovered in Ba Den Mountain, Tay Ninh Province. The species is one of the most popular reptiles in local communities and media as a specialty food. The species is also subject of international trade. However, detailed information on the species' population status and potential threats are lacking. Day and night excursions were carried out along 15 transects on Ba Den Mountain. A total of 883 geckos were captured by the research team and local hunters during 45 survey hours, with an average capture rate of about 20 individuals per hour and a person. The density of G. badenii was calculated at up to 450 individuals per square kilometer, indicating a relatively high abundance in suitable habitats. Furthermore, we investigated local and international use and trade in the species for food consumption and as pet. According to our interviews with hunters, a single hunter may be able to capture approximately 1500 to 3000 individuals per month. Based on reported reduced capture yields of local hunters, a decline in abundance of 40% to 60% in the species' type locality is assumed in recent times. Large quantities of specimens are sold at restaurants as specialty and offered for sale online as food. Regarding the pet trade, the LEMIS data documented the import of more than 11,000 live individuals of G. badenii into the United States from 2018 to 2023, with a majority of wild caught individuals originating from Vietnam. Online investigations recorded the presence of G. badenii on 28 websites of pet shops advertised for the commercial sale in the United States and several European countries. Together with habitat fragmentation and degradation (e.g., due to road construction, tourism and forest fires), the wild population of G. badenii has declined sharply and will presumably continue to decline in the future, even facing the risk of extirpation at its type locality. Thus, concrete conservation measures are highly essential to protect the wild population of G. badenii in Ba Den Mountain.

摘要

zh

作为越南已知17种壁虎之一, 金壁虎 (Gekko badenii) 是越南南部的特有物种, 最初发现于西宁省巴登山 (Ba Den Mountain, Tay Ninh Province) 。该物种既是当地社区和媒体中广为人知的特色食材, 也是国际贸易的对象。然而, 其种群现状与潜在威胁尚缺乏系统研究。

研究团队与当地猎手在巴登山设置15条样线进行昼夜调查, 45小时内共捕获883只个体, 人均捕获率约20只/小时。估算显示, 其适宜栖息地密度高达450只/平方公里, 表明当前局部种群仍较丰富。进一步调查发现, 该物种被用于食用 (本地及国际市场) 和宠物贸易。据猎人访谈, 单月捕获量可达1,500至3,000只;基于捕获量下降趋势推测, 模式产地种群近年已减少40%-60%。大量个体通过餐馆 (特色菜肴) 和网络渠道 (食品) 交易。宠物贸易方面, 2018-2023年美国LEMIS数据库记录显示, 逾11,000只活体从越南 (主要为野生个体) 输入美国;另在线监测到28家欧美宠物商店网站公开售卖。

除栖息地碎片化与退化 (道路建设、旅游业及森林火灾等) 外, 过度利用已导致 金壁虎野生种群急剧衰退, 模式产地甚至面临区域性灭绝风险。 亟需采取具体保护措施以维持巴登山种群的存续。

简明语言摘要

zh

金壁虎 (Gekko badenii Szczerbak & Nekrasova, 1994) 作为地方特色食材广为人知, 同时也是国际贸易对象。该物种已被IUCN红色名录评估为濒危物种, 但因其种群数量与受胁状况缺乏详细数据, 制约了保护措施的有效性。本研究通过在雨季初期对巴登山15条样线开展野外调查, 系统评估了该物种的种群丰度、种群结构及活动规律。目前 金壁虎在当地仍保持相对较高的种群密度。然而调查发现:大量个体被作为特色食材在餐馆销售并通过网络交易;过去五年仅美国就进口了逾11,000只活体;28家欧美宠物商店网站公开售卖活体。叠加栖息地破碎化与退化等因素, 野生种群数量急剧下降, 未来甚至面临区域性灭绝风险。为此, 我们提出了确保该物种长期存续的系统性保护方案与具体实施措施。

Summary

en

The Golden gecko, G. badenii Shcherbak & Nekrasova, 1994, has become widely known as a local specialty food and also subject of international trade. The species has been assessed as Endangered in the IUCN Red List, while the lack of detailed information on the species abundance and threats limits the efficacy of conservation actions. Thus, in this study, field surveys were carried out along 15 transects in Ba Den Mountain during the early wet season to assess the abundance, population demography and activity pattern of Gekko badenii in Ba Den Mountain. Currently, G. badenii can still be described as relatively abundant in Ba Den Mountain. However, large quantities of specimens are sold at restaurants as specialty and offered for sale online as food, more than 11,000 live individuals of G. badenii have been imported in the United States for the last 5 years, and 28 websites of pet shops advertised for the commercial sale in the United States and several European countries. Together with habitat fragmentation and degradation, the wild population of G. badenii has been declining sharply, even facing the risk of extirpation in the future. Thus, adequate conservation schemes and practical activities are proposed to safeguard Gekko badenii in the long term.

  • Practitioner Points

    • Provide information on the abundance, population demography and activity pattern of an endangered species of Gekko badenii at its type locality of Ba Den Mountain, Tay Ninh Province, southern Vietnam.

    • Investigate local and international use and trade in Gekko badenii for food consumption and as pet.

    • Propose adequate conservation schemes and practical activities to safeguard Gekko badenii in the long term.

实践者要点

zh

  • 提供濒危物种 金壁虎 (Gekko badenii) 在模式产地——越南南部西宁省巴登山的种群丰度、种群统计特征及活动规律等基础数据

  • 调查 金巴登壁虎在食用与宠物贸易领域的本地及国际利用情况

  • 提出长期保护 金巴登壁虎的科学方案与具体措施

1 Introduction

Overexploitation referring to the unsustainable use or harvest of wildlife may lead to significant population declines, loss of genetic diversity or to local extinction (Marshall et al. 2020). Vietnam is globally known as a source, destination and transit hub of reptiles to domestic and international markets including the pet trade, food consumption and traditional medicine (Janssen and Indenbaum 2019; Luong 2022). Janssen and Indenbaum (2019) raised concerns that some endemic reptiles from Vietnam may be especially vulnerable to overexploitation because of their restricted ranges and small population sizes. Among all reptiles in Vietnam, a total of 78 species have been assessed as globally threatened by the IUCN Red List (as Critically Endangered—21 species, Endangered—22 species, and Vulnerable—35 species), whereof 31 species (40%) are endemic to Vietnam. It is noteworthy that a total of 21 threatened gekkonid species in the IUCN Red List are endemic to Vietnam (IUCN 2024). One of these endemic species, Cnemaspis psychedelica, can be only found on two offshore islands in southern Vietnam, and has been observed at European fairs and online markets, sold for high prices of up to 3000 EUR/pair shortly after its discovery (Auliya et al. 2016; Ngo, Nguyen, et al. 2016). The unsustainable exploitation of the range-restricted species Goniurosaurus luii and G. araneus (up to 10,000 individuals during the summer in 1996), shortly after their formal description in 1999, led to the local extirpation at their type locations (Grismer et al. 1999; Yang and Chan 2015; Lindenmayer and Scheele 2017). Overexploitation, combined with further threats such as habitat destruction, can threaten wild reptile populations in Vietnam, bringing them closer to the brink of extinction (Gewiss et al. 2020; Lindenmayer and Scheele 2017; Ngo, Le, et al. 2019; Nijman 2010; Stuart et al. 2006). This growing threat underscores the critical need for stronger conservation efforts. Consequently, an increasing number of gecko species from Vietnam such as Goniurosaurus spp. and Cnemaspis psychedelica have been recently listed in CITES Appendices to address the issue of overexploitation by improving the regulation of international trade. However, most species are understudied so far, while information on the conservation status and impact of potential threats are crucial for adequate conservation actions.

With 107 species, the Gekkonidae family represents nearly 20% of reptile species recorded in Vietnam, making it the most diverse reptile family in the country (Uetz et al. 2024). As a result of taxonomic reassessments of gekkonid species complexes and extensive surveys from remote areas, a total of 36 new gecko species have been discovered in Vietnam only during the last decade (Uetz et al. 2024). At the same time, the systematics of gekkonids are not yet being fully understood.

As one of 17 Gekko species known from Vietnam, Gekko badenii Shcherbak and Nekrasova (1994), was first discovered on Ba Den Mountain, Tay Ninh Province, which is the species' type locality. Shortly thereafter, G. ulikovskii was described from Kon Tum Province (Darevsky and Orlov 1994), but the species was subsequently considered as a junior synonym of G. badenii (Nguyen et al. 2010). Due to its small range and an inferred decline in the overall population size, the species has been assessed as Endangered under criterion B1ab(v) in the IUCN Red List, while detailed information on the species abundance and threats are lacking (N. S. Nguyen et al. 2018). Recently, the Vietnamese name of G. badenii—“Than lan nui ba den” has become widely known in local communities and media since its type locality, Ba Den Mountain, a national historical relic and scenic site, became one of the most famous spiritual tourist destinations in southern Vietnam in 2006. At the same time, G. badenii became a specialty food there. Due to its golden color pattern referenced to by its common name “golden gecko,” the species has also been subject to the international pet trade.

This study aims to provide information on the abundance, population demography, and activity pattern of G. badenii at its type locality where it is subject to exploitation. We further investigated potential threats to the species and its habitat through interviews, online surveys and direct observations in Ba Den Mountain. Specifically, we noted the domestic use for food consumption and international trade to evaluate potential impacts of harvest to the species. These data are crucial to propose adequate conservation measures and set up practical activities to safeguard the golden gecko in the long term.

2 Materials and Methods

2.1 Field Surveys

The study site was selected within the known distribution range of G. badenii, viz. around the type locality in Ba Den Mountain, Tay Ninh Province, southern Vietnam based on previous observations, literature, and interviews with local people. This granite-rocky mountain is up to 986 meters above sea level (asl), covered by evergreen forests (Supporting Information S1: Figure S1A) and characterized by a monsoon sub-equatorial climate with constant annual temperatures, but with a distinct climatic difference between a dry and a wet season with heavy rains (General Statistics Office of Vietnam 2016; Ngo et al. 2018; Sterling et al. 2006). The species is frequently observed on granite rocks, cliffs and caves, as well as often found on trunks or small branches at night.

Field surveys were carried out by two survey teams in Ba Den Mountain during the early wet season in August 2024. Each team consisted of two researchers marking, collecting and noting data and one local guide catching animals. Following the suggestion of local rangers, we mainly conducted day excursions (11 days) between 14:00 h and 18:00 h, when G. badenii is resting and hiding inside rocky caves, but actively react to prey (e.g., insects). To lure animals out of their hiding spots, we used a long stick with a prey organism (e.g., beetle) attached. Furthermore, four-night excursions were undertaken after sunset between 19:30 and 24:00 h. During the night excursions, we captured animals by hand or by using the same noose-stick without a prey organism because well-fed animals tend not to react to prey at night. A total of 11 transects were surveyed, whereof nine transects (T1–T9) were selected for day excursions and two different transects (T14–T15) were selected for night excursions (Supporting Information S1: Figure S1C). Each day-transect covered a forest area of about 200 m2, characterized by a suitable microhabitat of granite rocks, cliffs, and caves and the mandatory presence of Ficus lacor trees, as geckos feed on ripe fruits too (Supporting Information S1: Figure S1). Night transects were set at different elevations (e.g., 200, 400, 500, and 700 m asl.) along the fire-rescue routes in Ba Den Mountain, containing similar microhabitat structures. Coordinates and elevations for each transect were recorded with a GPS Garmin 64. Individuals were released at the capture site after taking measurements, photos, determining the sex of each gecko, and marking with a permanent pen to identify re-captured animals.

2.2 Population Analysis

The total number of individuals per transect was counted based on direct observation. We further calculated rates of captured geckos per hour (inds/hour) and adults per hour (adults/hour) per person as the proxy for catch per unit effort. To assess the demographic structure, geckos were categorized into three age classes based on their snout–vent lengths (SVL ≤ 60 mm = juvenile, 60 mm < SVL < 75 mm = sub-adult, and SVL ≥ 75 mm = adult). Each gecko was measured with a digital slide-caliper to the nearest 0.1 mm. The sex in subadults and adults was determined by the presence of precloacal pores in males, and their absence in females (Figure 1). For testing significant differences in the age and sex structures between day and night that may give insights into sex or age-related activity patterns, we used a Chi-square test.

Details are in the caption following the image
Appearance and distinction of male and female golden geckos, Gekko badenii A. Light yellow body and tail of a Male; B. Brown and Gray body of a Female; C. Precloacal pores of a Male; and D. Absent or indistinct precloacal pores of a Female.

2.3 Sexual Dimorphism

The sexual dimorphism index (SDI) was calculated to identify the pattern of sexual size dimorphism (SSD) using the revised formula that was first suggested by Lovich and Gibbons (1992), in which SDI = (mean size of males/mean size of females) – 1. Accordingly, SDI is a positive value when males are the larger sex (SDI > 0) as a male-biased pattern, a negative value when females are the larger sex (SDI < 0) as a female-biased pattern and zero when the sexes are equal in size (SDI = 0) as unbiased pattern. Student t-tests were performed to determine the difference in the snout-vent length (SVL) and weight between males and females. Inter-sexual color variation of G. badenii was further examined based on photos of each individual taken in the field. For all tests, we applied p-value = 0.05. Statistical analyses were carried out in R v 3.1.2 (RStudio Team 2018).

2.3.1 Trade

To obtain evidence of trade in G. badenii, we first screened online markets (e.g., online shops, internet platforms, forums, social media and local press) by using some Vietnamese, German and English keywords (e.g., Than lan ba den, buon ban than lan nui ba den, Golden gecko for sale, Gold gecko, gekko badenii (ulikovskii)). We assessed records of trade to the United States (US) from 2018 to 2023, which were collected by the United States Fish and Wildlife Service (USFWS) in their electronic database called the Law Enforcement Management Information System (LEMIS). The LEMIS database contained no entries under the scientific name Gekko badenii. Instead, the LEMIS database contained entries of wild imports from Vietnam under the common name “golden gecko” and labeled with the scientific name “Gekko auratus.” There is no valid species called “Gekko auratus.” It seems that besides the junior synonym Gekko ulikovskii, the name “Gekko auratus” is used as a trade name for Gekko badenii. Therefore, we considered LEMIS database entries for “Gekko auratus” as imports of Gekko badenii to the US. We further visited the largest reptile fair “Terraristika” in Hamm, Germany in March and September 2024, to check for the availability of G. badenii.

Oral interviews were conducted with local rangers, local communities, and hunters to obtain information on the origin, commercial prices, and the purpose of use and trade in G. badenii. We further questioned three local hunters about their hunting skills, seniority, hunting time and income. We accompanied four local hunters during their routine collection of geckos using the catch method with a stick attached with a prey organism, along four transects (T10–T13) and compared their quantities to numbers captured by our research team. All geckos were released afterward. Hunters were compensated for the released geckos. Interviewees' names are kept anonymous to ensure data privacy rights.

3 Results

3.1 Population Status

The presence of Gekko badenii was documented in all surveyed transects from the Ba Den Mountain, at various elevations from 60 to 700 m a.s.l. A total of 883 geckos were captured by the research team and local hunters during 2660 survey minutes, with an average capture rate of about 20 individuals per hour by a person (Table 1). During the day, our research team caught 565 geckos in 1190 min, with a rate of 28.49 individuals per hour and person, and local hunters caught a total of 238 individuals in 660 min with a lower rate of 21.64 inds/h and person (Table 1). Contrarily, the average rate of 20 adults/h and person captured by senior hunters was significantly higher than the rate of 16.64 adults/h and person, accomplished by our research team (Table 1). Among day-surveyed transects, a senior hunter collected the highest number of 90 individuals (including 85 adults) with rates of 25.71 individuals and 24.28 adults/h and person at transect T12, while our research team captured a lower maximum number of 55 individuals at transect T1. The highest capture rates were up to 72 individuals at transect T2, and 42 adults per hour and person at transect T4 (Figure 2; Table 1). We further noted that rates of captured geckos at elevations of above 600 m a.s.l in transects of T8 and T9 (10–13 inds/h and person), were significantly lower than those in transects at lower elevations (Figure 2; Table 1). Over a period of 810 min at night, 80 individuals of G. badenii were captured in total. The average night-capture rate was estimated notably low, at 5.93 individuals per hour and person (Figure 2; Table 1).

Table 1. Summary of captured individuals as well as rates of collected individuals and adults of Gekko badenii per hour and person in Ba Den Mountain, southern Vietnam (inds: individuals; dash indicating missing data; D: Day and N: Night; the total values are in bold).
Adult Sub-adult
Transect Day/night Elevation (m) Time (minutes) Total Male Female Total Male Female Juvenile Un-known Total Adults/hour Inds/hour
T1 D1 90 120 43 23 20 12 12 0 0 0 55 21.5 27.50
D2 90 60 12 4 8 12 9 3 1 22 47 12 47.00
D3 60 90 17 9 8 6 3 3 2 13 38 11.3 25.33
T2 D1 85 40 8 5 3 14 8 6 3 23 48 12 72.00
T3 D1 80 90 47 17 30 1 1 0 0 1 49 31.3 32.67
T4 D1 170 60 42 20 22 8 5 3 1 0 51 42 51.00
T5 D1 120 60 29 13 16 10 7 3 2 1 42 29 42.00
T6 D1 440 70 13 3 10 10 10 0 1 24 48 8.67 32.00
D2 440 90 22 6 16 3 3 0 0 23 48 14.67 32.00
D3 440 90 25 12 13 2 2 0 2 3 32 16.67 21.33
T7 D1 560 90 18 10 8 6 6 0 0 23 47 12 31.33
T8 D1 600 120 19 10 9 0 0 0 1 0 20 9.5 10.00
D2 700 90 15 9 6 0 0 0 1 0 16 10 10.67
D3 700 60 10 5 5 1 1 0 0 0 11 10 11.00
T9 D1 680 60 10 7 3 3 3 0 0 0 13 10 13.00
Total-Day 1190 330 153 177 88 70 18 14 133 565 16.64 28.49
T10 D1 120 34 34 17.00 17.00
T11 D1 120 43 43 21.50 21.50
T12 D1 100 210 85 5 90 24.28 25.71
T13 D1 120 210 58 13 71 16.57 20.29
Total-hunters D 660 220 18 238 20.00 21.64
T14 N1 270 3 2 1 2 2 0 10 0 15 0.67 3.33
N2 180 21 4 17 9 7 2 6 2 38 12.67 12.67
N3 210 15 4 11 1 1 0 1 0 17 4.3 4.86
T15 N1 150 3 1 2 4 4 0 3 10 1.2 4.00
Total-Night N 810 42 11 31 16 14 2 20 2 80 3.11 5.93
Total 2660 592 883 13.35 19.92
Details are in the caption following the image
The number of captured individuals during a day hour (blue) and a night hour (orange).

Considering the age structure, during the day surveys, the percentage of adults accounted for 76.39%, followed by subadults (20.37%) and juveniles (3.24%). During the night surveys, the age structure significantly differed from the day surveys with adults accounting for 53.85%, followed by juveniles (25.64%) and subadults (20.51%) (Chi-square = 54.332, df = 2, p-value = 1.592e-12 < 0.01; Supporting Information S1: Figure S2). Regarding the sex structure, we captured more female individuals, accounting for 59.09% (n = 195) during the day surveys and 77.59% (n = 33) during the night surveys (Supporting Information S1: Figure S2). The dominance of female individuals was consistently recorded across all survey transects (Table 1).

3.2 Sexual Comparisons

Regarding morphology, the mean SVL of adult males (93.0 ± 0.9 mm) was significantly higher than that of females (82.2 ± 0.3 mm) (Student-test, p-value < 0.001, Supporting Information S2: Table S1). In addition, our findings revealed that males (17.8 ± 0.54 g) are significantly heavier than females (12.2 ± 0.2 g) on average (Student-test, p-value < 0.001). The maximum recorded weight for males was 37 g, whereas the heaviest female weighted 22.34 g (Supporting Information S2: Table S1).

3.3 Interviews With Local Community Members

According to our interviewees from the local community at Ba Den Mountain, five local persons were known to rely on hunting the target species of G. badenii as their primary occupation. All five persons had more than 5 years of experience, and those with the longest tenure in the profession have been doing it for up to 20 years. Besides Golden gecko, the snail species, Cyclophorus saturnus, is also harvested by these hunters as supply for local food consumption. Those who hunt geckos and snails full-time, earn a maximum monthly income of approximately 4–7 million VND (160-290 USD) during the rainy season and up to 9 million VND (370 USD) during the dry season. Recently, the number of leisure and new hunters increased to 12 local persons, driven by rising unemployment after the covid epidemic period. However, most of them have been only hunting geckos and snails in smaller numbers for personal food use.

In the past, hunters employed a team-based approach to catch golden geckos, with one person using a noose-stick while the others used leaves to mimic insect-like sounds, effectively luring the geckos. Currently, beetles of the Scarabaeidae family are usually used as prey attached to the noose-stick to attract and catch the geckos (Figure 3A). Hunting generally takes place between 7:00 am and 17:00 pm, though some hunters prefer to hunt only in the afternoon from 13:00 pm to 17:00 pm. Another common method involves setting up a bucket trap at night, typically around 10 liters in size, without its lid, and with local ripe fruits of Ficus lacor as bait inside the bucket (Supporting Information S1: Figure S1B). Local hunters apply lubricant oil on the sides of the bucket trap to prevent geckos from escaping. Geckos are described to be more active and occur in higher densities on granite rocks around the trees during the ripe fruit season of F. lacor.

Details are in the caption following the image
Capture, use and trade of G. badenii A. Capture method used by local hunters: A. Noose-stick attached with a beetle to attract geckos; B. A pack of live individuals sold to local restaurants; C. Processed specimens stored in refrigerators in restaurants; D. Grilled geckos offered as food in restaurants; E. Field collected live golden geckos for sale on an international online platform.

According to the interviews, the previous average stick-hunting yield was about 4 kg of geckos (about 250 adults) in half a day by two senior hunters, depending on the weather conditions, with a significantly lower yield during heavy rain or extreme heat. Currently, the yield of G. badenii from Ba Den Mountain has markedly declined with usually 1.5–2 kg of geckos (about 100–150 adults) per half a day. The yield of catching geckos with buckets can rise up to 0.5 kg of geckos per night during the dry season, while only 5–6 individuals can be usually caught in bucket traps per night during the rainy season. Thus, hunters only applied the bucket trap in the dry season.

Primarily live adults and rarely sub-adults of G. badenii are selectively targeted by hunters from the wild. Subsequently, these can be sold directly to local restaurants at higher prices, but they are often purchased by local dealers. After processing, gutted geckos are typically sold as prepared food and stored in refrigerators, either to local restaurants or transported to restaurants in Binh Duong Province and Ho Chi Minh City (Figures 3 and 5). Additionally, we have noted that some hunters and traders advertise live, processed, and cooked geckos online for food consumption. In contrast, we did not record that the species is locally used as pet. We visited and interviewed eight local restaurants at Ba Den Mountain, four of which offered dishes containing G. badenii. Previously, the price paid by middlemen to local hunters ranged between 90,000 and 110,000 VND (3.5–5 USD) per kilogram of geckos. Meanwhile, the current price has increased to 170,000 VND (7 USD) per kilogram. Likewise, prices paid by local restaurants to middlemen increased from 200,000 to 250,000 VND (8–10 USD) per kilogram. The current prices for dishes containing prepared geckos at restaurants range from 350,000 to 700,000 VND (14–28.5 USD) per kilogram (Figure 5).

3.4 International Pet Trade

According to the LEMIS database of imports into the United States (US), a total of 11,308 live individuals of golden geckos labeled as G. auratus, in 117 shipments were imported between 2018 and 2023 (Table 2). All shipments were reported for commercial purposes with a total profit of 11,363 USD (Table 2). The import of G. badenii into the US fluctuated annually with a mean number of 1,885 live individuals from an average of 20 shipments, amounting to 1894 USD per year (Figure 4; Table 2). All exported individuals of G. badenii were identified as originating from Vietnam, some of which were related to transit countries before shipping to the final destination of the US, including one shipment to Indonesia, three to Korea, three to Canada and one to France. The number of 10,253 individuals (90.7%) from 109 shipments were recorded as wild caught, whereas only 1055 geckos (9.3%) from 8 shipments were recorded as bred in human hands (Figure 4). The price for G. badenii varied from 0.7 to 8 USD per animal, with an average of 1.16 USD/ind (Table 2).

Table 2. Recorded imports of “golden gecko” as “Gekko auratus” by the Law Enforcement Management Information System (LEMIS) of the United States Fish and Wildlife Service (USFWS) between 2018 and 2023 (Inds: Individuals).
Years Shipments Total Quantity (Inds) Quantity/shipment (Inds) Total value (USD) Value/shipment (USD) Value/ind
2018 24 1753 1–200 (73) 1732 5–180 (72) 0.74–5 (1.66)
2019 27 2816 25–340 (104) 3229 20–984 (120) 0.75–8 (1.14)
2020 22 2198 30–400 (100) 2010 30–400 (91) 0.75–3.5 (1)
2021 19 2438 40–450 (128) 2385 38–338 (126) 0.75–1.5 (0.98)
2022 11 736 12–150 (67) 619 35–120 (56) 0.7–5 (1.16)
2023 14 1367 28–250 (98) 1388 34–300 (99) 0.8–1.4 (1.03)
Total 117 11,308 1–400 (95) 11,363 5–984 (94) 0.7–8 (1.16)
Details are in the caption following the image
Import data on trade of Gekko badenii derived from the wild and captivity from 2018 to 2023 in the United States; A. Number of annual shipments; B. Annual number of imported individuals; C. Annual value of shipments in USD. Source: LEMIS database of the United States Fish & Wildlife Service (2018–2023).

Our investigation on different online platforms of reptile trade recorded the presence of G. badenii on 28 websites of pet shops advertising for the commercial sale located in the US, United Kingdom of Great Britain and Northern Ireland, Romania, and Germany. Prices for sale of G. badenii ranged from 3.5 to 79.99 USD per individual, referring to an average of 28.5 USD/ind (Figure 5; Supporting Information S2: Table S2). The majority of offers related to animals that were wild-caught or whose origin was not specified. During two visits at the large reptile fair Terraristika in Hamm, Germany in March and September 2024, no Gekko badenii specimens were spotted for sale on the desks (pers. obs.).

Details are in the caption following the image
The network of local and international trade and food consumption of Gekko badenii.

3.5 Habitat Degradation

Ba Den Mountain is one of the most famous spiritual tourist destinations in southern Vietnam, situated approximately 100 km from Ho Chi Minh City, attracting millions of visitors each year. Through direct observations and interviews with local people, the development of cable car tourism in previous years, infrastructure for tourist locations on the mountain, and trekking visitors leaving garbage were identified as anthropogenic activities which degrade the forest and may impact the microhabitat quality of G. badenii at the Ba Den Mountain. Additionally, interviews with forest rangers revealed that small-scale forest fires have been sometimes occurring in the mountainous area during the dry season due to some local hunters using fire to obtain honey.

4 Discussion

4.1 Local Exploitation

Our surveys recorded a maximum of 90 individuals of G. badenii within a 200 m² area, indicating a potential density of up to 450 individuals per square kilometer. Local hunters reported that up to 200 adult geckos, weighing approximately 3 kg in total, can be captured within an area of less than 400 m², referring to a density of 500 inds/km2. In comparison, the average population density of a closely related species of G. canhi was calculated to be significantly lower with approximately 16.6 inds/km2 in northern Vietnam (Ngo et al. 2023). Similarly, other endangered geckos in Vietnam were found to occur at much lower densities, such as Cnemaspis psychedelica with an estimated density exceeding 120 individuals/km² in suitable habitats (Ngo, Nguyen, et al. 2016), Goniurosaurus catbaensis in Ha Long Bay reaching up to 60 individuals/km² (Ngo, Ziegler, et al. 2016; Ngo, Le, et al. 2019), and G. huuliensis with an estimated average density of 3.54 individuals/km². Therefore, based on the results of this study G. badenii can be described as a gecko species which occurs in high population densities in Ba Den Mountain. However, the present study indicates that the wild population in Ba Den Mountain has drastically declined during recent years. According to information provided by local hunters, some years ago, hunters were still able to capture an average of about 250 adult geckos in half a day. Nowadays, the yield has been reduced to about 100 to 150 adults in half a day. If this declining trend further continues, it may threaten G. badenii in Ba Den Mountain in the future. With the monthly income per hunter of approximately 4–9 million VND (160-370 USD) for hunting animals of G. badenii, we estimate that a hunter can capture approximately 1500 to 3000 individuals per month. The main driver for local declines seems to be the targeted harvest for food consumption.

On average, the research team caught more individuals per person and hour than an experienced full-time hunter. Nevertheless, the hunters captured more adults on average than the research team. These differences in capture rates may be due to the fact that, according to the interviews with local hunters, smaller-sized juveniles and sub-adults are not intentionally caught, and they are often released or completely disregarded during hunting. Our observations revealed that on survey days lasting less than 90 min, the catch rate per hour was quite high, reaching up to 72 individuals, except for routes at elevations above 700 m (Table 1). In contrast, the catch rate on days with survey durations of 120 min or more was lower (Table 1). Within an area limited to less than 200 m2, the encounter rate is likely to decrease after 2 h, once a large number of individuals has already been captured.

Online investigation and interviews indicated that the harvest of G. badenii is mainly intended for supplying food products in Vietnam, while no evidence was recorded that the species is used in the domestic pet trade. However, it may be assumed that the domestic pet trade with G. badenii still occurs in access-limited trade groups or by private transactions, and the quantity for these sales may be relatively small. Among gecko species in general, the herein identified main use of G. badenii as food for domestic consumption is relatively uncommon, as most geckos are generally considered too small to provide proper meat compared to larger reptile species in Vietnam. Regarding the morphology, G. badenii is characterized by a maximum snout-vent length (SVL) of 117.4 mm, which is significantly larger than that of C. psychedelica (maximum SVL: 75.4 mm) but lower than G. huuliensis reaching a maximum SVL of 132.2 mm (Grismer et al. 2010; Ngo et al. 2021). Overall, the size and weight of G. badenii (with a maximum of 37 g) are much lower than those of lizards commonly harvested for food consumption in Vietnam, such as the agamid species Physignathus cocincinus (SVL: 280 mm, and weight: 600 g) (Ngo et al. 2024). In contrast, other Vietnamese geckos (e.g., Cnemaspis psychedelica and five Goniurosaurus species) have been harvested for the main purpose of supplying the pet trade due to high prices that can be achieved there (Auliya et al. 2016; Ngo, Nguyen, et al. 2019). For example, 4–5 USD were paid to local hunters to collect an individual of Goniurosaurus species, and which was sold in local pet shops with approximately 35 USD (Ngo, Nguyen, et al. 2019). Individuals of C. psychedelica even fetched extremely high prices up to 2500–3000 Euro/pair on internet platforms (Auliya et al. 2016). Meanwhile, local hunters were only paid 6–10 USD/kg of G. badenii (meaning 0.1–0.17 USD/ind). The substantial commercial profits derived from the purpose of pet trade for small-sized Goniurosaurus species and C. psychedelica due to their beautiful color patterns and rarity in the wild likely explain why they are not exploited for food, in contrast to G. badenii, which is specifically targeted as a local food source and can be caught in larger quantities. The fact that G. badenii has been observed eating ripe fruits could also contribute to its commonness, and restaurants use this characteristic to advertise this as a sign of healthy and fresh food to consumers.

We were not able to detect a specific large demand for G. badenii in the European market, so that we consider the species as some kind of bycatch species, which is included in international shipments for the pet trade if available. The LEMIS data in the United States however, recorded imports of more than 11,000 live individuals of G. badenii between 2018 and 2023, with the majority of imports (90.7%) recorded as wild caught animals from Vietnam. Despite live animals of G. badenii may be only sold domestically with the quantity unit of kilogram for food advertising, local traders may purchase them for overseas export shipments. Our surveys on international online platforms recorded the lowest price at 3.5–5 USD and the highest at 79.99 USD per individual of G. badenii, with an average price of approx. 28.5 USD/ind. Meanwhile, with an average selling price of 0.17 USD/ind in Vietnam, and 1 USD/ind imported to the US, the profit of international retail trade is very high, with about 41-fold of shipment prices, and approximately 400-fold of the prices gained locally. The low prices for wild-caught animals in the local market in Vietnam could explain why there appears to be no significant trade in captive bred individuals, as captive breeding may not be economically viable. The highest price of 79.99 USD was recorded for bred offspring from an online retailer, while animals declared as wild-caught were already available at much lower prices. The relatively low prices for the sale of G. badenii in the international pet trade may be due to its somewhat less striking appearance, the availability in large quantities from the wild, and/or successful breeding in human hands.

4.2 Population Structure Shifted by Sexual Dimorphism

Regarding the sex ratio of G. badenii in Ba Den Mountain, the dominance of female individuals was recorded across all survey transects. This sex ratio imbalance naturally occurs in many reptile species and is linked to the territorial competition between males leading to a higher male mortality (Olsson and Shine 1996; Shine 1989; Stamps and Gon 1983). In this study, we recorded that males are significantly larger and heavier than females (Supporting Information S2: Table S1). An inter-sexual color variation was further observed. In particular, males show a bright yellow color at the dorsal body and tail (Figure 1A), while females present a brown dorsal body and light gray tail (Figure 1B). These observations approve the distinct sexual dimorphism in G. badenii following the male-biased pattern. According to interviews with local hunters, they only selectively catch adults of G. badenii and prefer light yellow individuals which can be identified as adult males because of their bigger size for food consumption yielding higher prices in sale. Observations and interviews with local hunters in this study in line with previous observations by Hofmann (2006) from the pet trade, noting an extremely biased ratio of 1:12 or smaller for females: males, respectively, suggest that the apparent sexual dimorphism of G. badenii leads to the targeted harvest of males for both the pet and consumptive trade. As in the case of the agamid species Physignathus cocincinus, we also consider the male-biased sexual dimorphism in sizes and colors of G. badenii as an important factor which might directly cause a decrease in the abundance of males (Gewiss et al. 2020; Ngo et al. 2024; T. Q. Nguyen et al. 2018). A continuous selective harvest could drastically shift the sex ratio of the wild population towards a significant reduction of adult males and thereby an unnatural imbalance.

4.3 Conservation

Currently, G. badenii can still be estimated as relatively abundant on Ba Den Mountain. However, under severe impacts of long-term harvesting (e.g., for food consumption and pet trade) and habitat fragmentation and degradation (e.g., due to road construction, tourism, and forest fires), the wild population of G. badenii has declined sharply. Demographic assessments of other endangered Vietnamese lizards revealed a drastic reduction in their wild populations, particularly Shinisaurus crocodilurus in Vietnam and China with up to 90% declines, even local extirpation in Goniurosaurus luii and G. araneus, and an increased risk of extinction in Cnemaspis psychedelica, mainly driven by over-harvesting and habitat loss (Grismer et al. 1999; Huang 2008; Ngo, Nguyen, et al. 2016; Ngo, Le, et al. 2019; Stuart et al. 2006; van Schingen et al. 20142016). To prevent unsustainable exploitation and habitat degradation, concrete measures of conservation are highly essential to protect the wild population of G. badenii at its type locality in Ba Den Mountain. Globally threatened species, G. badenii (Endangered) together with other geckos such as Cyrtodactylus nigriocularis (Critically Endangered) and C. badenensis (Vulnerable) should be considered as high-profile flagship species to highlight the value of biodiversity in Ba Den Mountain. And, we have evidence that there occurs more so far overlooked, seemingly micro-endemic biodiversity in there, making the site even more important for upgraded conservation measures. This should be prioritized with regard to conservation policies to protect forest habitats of Ba Den Mountain rather than favoring only economic development. To address the overharvest of the species, banning the entire harvest for food use and pet trade of G. badenii may not be the most effective solution, as it has a significant role in supporting the livelihoods of some local people. Instead, encouraging the participation in forest patrol teams or providing additional jobs in relation to local tourism activities could provide sustainable livelihoods for hunters. A proper adaptive management that allows certain regulated and limited harvest and sustainable use of the species based on quotas, designated harvest areas or size restrictions should be implemented by considering the livelihoods of local people and incentivizing the long-term protection of the species. Alternatively, certain quotas for the sale of wild specimens in restaurants could be discussed to thereby increase prices for dishes from wildlife. To achieve that the species needs to be included in the national governmental decree as a protected species. Furthermore, a CITES Appendix III listing could be considered to collect reliable data on the extent and impact of international trade.

We further intend to partner with the Ba Den Mountain management board to implement a program raising community awareness and engaging tourists on the importance of local biodiversity. Recently, this involved designing and placing signboards and leaflets at tourist sites, to introduce the conservation status of G. badenii and other threatened geckos from Ba Den Mountain. As part of concrete measures against habitat loss, regular patrols should be conducted by rangers to detect forest fires timely before spreading in Ba Den Mountain. In an effort to reduce plastic waste from tourist activities, waste bins were recently placed along trekking routes and tourist sites. Some parts of the forest encompassing suitable habitats for the species should be entirely protected from human access. Establishing in-country breeding programs could aid building up reserve populations, which can facilitate future releases if needed to support the recovery of disturbed wild populations. Furthermore, it could aid to supply demand for the species and contribute to local livelihoods.

Author Contributions

Hai Ngoc Ngo: conceptualization, formal analysis, methodology, software, writing – original draft, writing – review and editing. Quyen Hanh Do: conceptualization, formal analysis, methodology. Thanh Phuong Thi Bui: methodology. Cuong The Pham: conceptualization, funding acquisition. Truong Quang Nguyen: conceptualization, writing – original draft, writing – review and editing. Huy Quoc Nguyen: methodology. Laurenz Rafael Gewiss: conceptualization, funding acquisition, writing – original draft, writing – review and editing, methodology. Mona van Schingen-Khan: conceptualization, funding acquisition, methodology, writing – original draft, writing – review and editing. Thomas Ziegler: conceptualization, funding acquisition, writing – review and editing.

Acknowledgments

We thank the authorities and forest protection departments in Ba Den Mountain National Tourist Area, Tay Ninh Province for support of our field work and issuing relevant permits (permit No. 1197/STTNSV issued on 18 July 2024). For the fruitful cooperation within joint research projects, we cordially thank Le H. A, Nguyen H. H, Nguyen T. T. (IB, Hanoi), as well as T. Pagel and C. Landsberg (Cologne Zoo). The project, allocation number 35 24 55 05 00, “Determination of the population situation and potential threat posed by trade in the golden gecko, Gekko badenii in Vietnam as a basis for potential CITES listing,” assigned to the German Vietnamese work group “biodiversity research and conservation projects Vietnam,” Cologne Zoo, was funded by the Federal Agency for Nature Conservation, BfN, Germany. Conservation based gecko research and improved gecko conservation measures in Vietnam are further supported by the Zoo Species of the Year 2024 Conservation Campaign - The Gecko.

    Ethics Statement

    The research followed the principles of ethical animal treatment. No animals were intentionally harmed during this study. Relevant permits for the field work were obtained from the responsible provincial authorities (see acknowledgments).

    Conflicts of Interest

    The authors declare no conflicts of interest.

    Data Availability Statement

    The data that support the findings of this study are available from the corresponding author upon reasonable request.

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