Biodiversity Data Journal :
Data Paper (Biosciences)
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Corresponding author: Minh Duc Le (le.duc.minh@hus.edu.vn), Anh Tuan Nguyen (tuananhnguyen@hus.edu.vn)
Academic editor: Chelmala Srinivasulu
Received: 28 Aug 2024 | Accepted: 14 Oct 2024 | Published: 17 Oct 2024
© 2024 Thanh Nguyen, Anh Luu, Hung Pham, Ha Nguyen, Tam Pham, Mai Nguyen, Minh Le, Anh Nguyen
This is an open access article distributed under the terms of the Creative Commons Attribution License (CC BY 4.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Citation:
Nguyen T, Luu A, Pham H, Nguyen H, Pham T, Nguyen M, Le M, Nguyen A (2024) Systematic camera trapping survey for terrestrial vertebrates in Xuan Lien Nature Reserve, Vietnam. Biodiversity Data Journal 12: e135746. https://doi.org/10.3897/BDJ.12.e135746
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Xuan Lien Nature Reserve was established in 1999 to protect important habitats and wildlife in the northern part of the Annamites in Vietnam. While Xuan Lien is home to many threatened species, it has experienced a high level of human disturbance over the last decades. To document and provide baseline data on the status and distribution of the terrestrial vertebrate fauna community in the region, we conducted a systematic camera trapping survey in Xuan Lien Nature Reserve in 2023. The data collected during the survey will help design proper conservation measures to better conserve the remaining species.
Our study investigates and updates the species richness of mid- to large-sized terrestrial vertebrates, thus providing essential information for developing conservation strategies in Xuan Lien Nature Reserve, Vietnam. As camera traps were set up in a grid-based design, our survey also generated the first-ever systematic data for terrestrial vertebrate fauna in the area. The study covers approximately 21,000 hectares (about 77% of the area), using 35 camera trap stations; each station consists of two cameras. In total, the final dataset consists of 6,276 trap nights, recording at least 46 species in 39 genera. The results suggest that Xuan Lien is a key stronghold for small carnivores, based on the diversity of such species groups in the Reserve. We failed to detect the previously documented Roosevelt’s muntjac (Muntiacus rooseveltorum Osgood, 1932) and we only documented a single record of the northern red muntjac (Muntiacus vaginalis Boddaert, 1785). Our survey confirms the severity of overhunting and other anthropogenic threats to the mammal fauna, especially ungulates, in the Reserve.
hunting threats, monitoring, muntjac, small carnivores
Camera trapping has been widely used recently to survey the terrestrial vertebrate fauna in Vietnam due to its efficiency in the detection of terrestrial animals (
Xuan Lien Nature Reserve, Thanh Hoa Province, Vietnam, is located in the northern part of the Annamites with approximately 27,000 hectares of forested area. Together with the nearby Pu Hoat Nature Reserve in Nghe An Province, it forms a contiguous protected landscape of around 115,000 hectares (
The survey is conducted to document the occurrence and distribution of terrestrial vertebrates in Xuan Lien Nature Reserve, Thanh Hoa, Vietnam, using a camera trap survey. The survey follows a repeatable, systematic grid-based design with the intention of providing baseline data and establishing a Camelot (
Systematic camera trapping survey for terrestrial vertebrates in Xuan Lien Nature Reserve, Vietnam.
Xuan Lien Nature Reserve is located in Thanh Hoa Province, Vietnam and it is located in the northern Annamite landscape. The Reserve was formally established in 1999 and there have been a number of biodiversity surveys in Xuan Lien since the late 1990s. It reportedly still supports several rare and threatened mammals, such as the gaur (Bos gaurus C.H. Smith, 1827), the northern pygmy slow loris (Xanthonycticebus intermedius Dao Van Tien, 1960), the Asiatic black bear (Ursus thibetanus G. Cuvier, 1823), the Indochinese grey langur (Trachypithecus crepusculus Elliot, 1909), the northern white-cheeked gibbon (Nomascus leucogeny Ogilby, 1840), the Owston’s civet (Chrotogale owstoni Thomas, 1912) and the stump-tailed macaque (Macaca arctoides I.Geoffroy Saint-Hilaire, 1831) (
This research has been done under the research project QG.22.72 of Vietnam National University, Hanoi.
Our survey was conducted from February 2023 to June 2023. The survey followed a systematic grid-based camera trapping design developed by Abrams et al. (2018). We intended to survey the entire Reserve area; however, due to the operation of the Cua Dat hydropower plant in the south-eastern part of the Reserve and the subsequent raised water level of the Chu River since 2010, some areas of Xuan Lien have been isolated for around 15 years. Subsequently, our survey only covered about 77% of the Reserve. However, the core zone of the Reserve was fully covered by our survey and such areas were believed to still harbour a high density of vertebrates (
In total, we deployed 70 camera traps at 35 locations, which were spaced about 2.5 km apart with a maximum acceptable deviation of 10% (approximately 250 m). Hence, the minimum distance between any camera station was 2.0 km. However, at one station, both cameras were lost and, therefore, we were only able to retrieve 68 cameras at 34 stations. Each camera-trap station consisted of two non-facing camera-trap devices (Reconyx Hyperfire) that were set within a 20 × 20 m plot. Cameras were placed on tree trunks 20–40 cm above the ground and were set up to take three bursts of photos per trigger without delay, recording the date and time of each photo. All cameras were set at a high sensitivity level and were working continuously during the survey. The cameras were deployed for an average of 92.2 ± 2.3 days.
To maximise wildlife records, we configured all cameras to be activated by motion and the sensitivity was set at very high level. Each camera took three photos per trigger, with picture interval in rapid-fire mode, which means the cameras took multiple shots in rapid succession. All cameras were set to run continuously with no rest period and the flash output was at high level.
To ensure the correct scientific name and common name of species, the taxonomic nomenclature followed the Catalogue of Life and GBIF Backbone Taxonomy. In addition, we used the IUCN Red List of Threatened Species and Vietnam Red Data Book 2007 to check the species' conservation status (
Collected data were copied into folders named by camera and station codes. Each photo was then identified and moved to a corresponding species sub-folder. The completely identified camera dataset was then checked and analysed using the camtrapR package (
Xuan Lien Nature Reserve, Thanh Hoa Province, Vietnam.
19.854 and 20.021 Latitude; 104.956 and 105.301 Longitude.
Mammals, birds and reptiles were identified to the species level, whenever possible.
Rank | Scientific Name | Common Name |
---|---|---|
class | Mammalia | Mammals |
class | Aves | Birds |
class | Reptilia | Reptiles |
2023-2-27 - 2023-6-09
Creative Commons Attribution Non-Commercial (CC-BY-NC 4.0).
The dataset is published on the Global Biodiversity Information Facility platform, GBIF (
Column label | Column description |
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occurrenceID | Unique identifier of the record. |
basisOfRecord | The specific nature of the data record. |
occurrenceStatus | A statement about the presence or absence of a taxon at a location. |
eventDate | Date and time when the occurrence occurred. |
kingdom | The full scientific name of the kingdom in which the taxon is classified. |
scientificName | The full scientific name, with authorship and date information, if known. |
taxonRank | The taxonomic rank of the most specific name in the scientificName. |
decimalLatitude | The geographic longitude at which the occurrence took place. |
decimalLongitude | The geographic longitude at which the occurrence took place. |
geodeticDatum | Spatial reference system upon which the geographic coordinates given in decimalLatitude and decimalLongitude are based. |
countryCode | ISO code of the country in which camera location occurs. |
dataGeneralizations | Generalisation measures taken to make the shared coordinates less specific than in their original form. High quality data are available upon reasonable request. |
class | Full scientific name of the class in which the taxon is classified. |
family | Full scientific name of the family in which the taxon is classified. |
genus | Full scientific name of the genus in which the taxon is classified. |
coordinateUncertaintyInMeters | The horizontal distance (in metres) from the coordinates given in decimalLatitude and decimalLongitude describing the smallest circle containing the whole of the location. |
individualCount | The number of individuals present at the time of the occurrence. |
organismQuantity | A number or enumeration value for the quantity of the organism. |
organismQuantityType | The type of quantification system used for the quantity of organismQuantity. |
dynamicProperties | IUCN Red List status of the taxon. |
minimumElevationInMeters | The lower limit of the range of elevation in metres. |
maximumElevationInMeters | The upper limit of the range of elevation in metres. |
A total of 1,002 independent records of at least 46 species, including 21 mammals, 24 birds and one reptile, were documented in our survey. For mammals, 19 taxa were identified to species level and two taxa were only identifiable to genus level (Table
Class |
Family |
Species |
IUCN |
Vietnam Red Data Book 2007 |
Independent detection |
Recorded station |
Naïve occupancy |
Mammalia |
Tupaiidae |
Tupaia belangeri Wagner, 1841 |
LC |
29 |
14 |
0.412 |
|
Cercopithecidae |
Macaca arctoides I.Geoffroy Saint-Hilaire, 1831 |
VU |
VU |
42 |
11 |
0.324 |
|
Macaca assamensis McClelland, 1840 |
NT |
VU |
4 |
2 |
0.059 |
||
Macaca mulatta Zimmermann, 1780 |
LC |
LR |
4 |
2 |
0.059 |
||
Mustelidae |
Martes flavigula Boddaert, 1785 |
LC |
20 |
16 |
0.471 |
||
Melogale spp. I.Geoffroy Saint-Hilaire, 1831 |
LC |
257 |
26 |
0.765 |
|||
Lutra sp. Brisson, 1762 |
1 |
1 |
0.029 |
||||
Viverridae |
Paguma larvata C.E.H. Smith, 1827 |
LC |
6 |
3 |
0.088 |
||
Paradoxurus hermaphroditus Pallas, 1777 |
LC |
31 |
17 |
0.500 |
|||
Viverra zibetha Linnaeus, 1758 |
LC |
21 |
9 |
0.265 |
|||
Herpestidae |
Herpestes urva Hodgson, 1836 |
LC |
36 |
14 |
0.412 |
||
Felidae |
Prionailurus bengalensis Kerr, 1792 |
LC |
22 |
13 |
0.382 |
||
Prionodontidae |
Prionodon pardicolor Hodgson, 1841 |
LC |
VU |
16 |
7 |
0.206 |
|
Suidae |
Sus scrofa Linnaeus, 1758 |
LC |
15 |
11 |
0.324 |
||
Cervidae |
Muntiacus vaginalis Boddaert, 1785 |
LC |
VU |
1 |
1 |
0.029 |
|
Bovidae |
Capricornis milneedwardsii David, 1869 |
NT |
EN |
3 |
3 |
0.088 |
|
Hystricidae |
Hystrix brachyura Linnaeus, 1758 |
LC |
10 |
7 |
0.206 |
||
Atherurus macrourus Linnaeus, 1758 |
LC |
1 |
1 |
0.029 |
|||
Sciuridae |
Callosciurus erythraeus Pallas, 1779 |
LC |
15 |
6 |
0.176 |
||
Dremomys rufigenis Blanford, 1878 |
LC |
20 |
5 |
0.147 |
|||
Manidae |
Manis javanica Desmarest, 1822 |
CR |
EN |
4 |
2 |
0.059 |
|
Aves |
Phasianidae |
Arborophila chloropus Blyth, 1859 |
LC |
19 |
2 |
0.059 |
|
Arborophila brunneopectus Blyth, 1855 |
LC |
13 |
6 |
0.176 |
|||
Arborophila rufogularis Blyth, 1849 |
LC |
9 |
5 |
0.147 |
|||
Gallus gallus Linnaeus, 1758 |
LC |
49 |
15 |
0.441 |
|||
Lophura nycthemera Linnaeus, 1758 |
LC |
LR |
49 |
12 |
0.353 |
||
Polyplectron bicalcaratum Linnaeus, 1758 |
LC |
27 |
8 |
0.235 |
|||
Columbidae |
Chalcophaps indica Linnaeus, 1758 |
LC |
38 |
7 |
0.206 |
||
Pitta soror R.G.W.Ramsay, 1881 |
LC |
40 |
19 |
0.559 |
|||
Pitta elliotii Oustalet, 1874 |
LC |
29 |
5 |
0.147 |
|||
Corvidae |
Dendrocitta formosae Swinhoe, 1863 |
LC |
2 |
1 |
0.029 |
||
Cissa hypoleuca Salvadori & Giglioli, 1885 |
LC |
1 |
1 |
0.029 |
|||
Dicruridae |
Dicrurus macrocercus Vieillot, 1817 |
LC |
2 |
1 |
0.029 |
||
Turdidae |
Zoothera citrina Latham, 1790 |
LC |
8 |
5 |
0.147 |
||
Zoothera dauma Latham, 1790 |
LC |
32 |
10 |
0.294 |
|||
Muscicapidae |
Myophonus caeruleus Scopoli, 1786 |
LC |
101 |
6 |
0.176 |
||
Larvivora cyane Pallas, 1776 |
LC |
1 |
1 |
0.029 |
|||
Copsychus malabaricus Scopoli, 1786 |
LC |
1 |
1 |
0.029 |
|||
Leiotrichidae |
Garrulax castanotis Ogilvie-Grant, 1899 |
LC |
3 |
2 |
0.059 |
||
Garrulax leucolophus Hardwicke, 1816 |
LC |
2 |
2 |
0.059 |
|||
Pellorneidae |
Pellorneum tickelli Blyth, 1859 |
LC |
10 |
5 |
0.147 |
||
Schoeniparus rufogularis Mandelli, 1873 |
LC |
1 |
1 |
0.029 |
|||
Timaliidae |
Erythrogenys hypoleucos Blyth, 1844 |
LC |
1 |
1 |
0.029 |
||
Scolopacidae |
Scolopax rusticola Linnaeus, 1758 |
LC |
1 |
1 |
0.029 |
||
Ardeidae |
Gorsachius melanolophus Raffles, 1822 |
LC |
1 |
1 |
0.029 |
||
Reptilia |
Varanidae |
Varanus salvator Laurenti, 1768 |
LC |
EN |
4 |
4 |
0.118 |
Examples of records from our survey at Xuan Lien Nature Reserve, Thanh Hoa Province, Vietnam. From top left, clockwise: the Sunda pangolin (Manis javanica), the stump-tailed macaque (Macaca arctoides), the northern red muntjac (Muntiacus vaginalis), the large Indian civet (Viverra zibetha Linnaeus, 1758), the grey peacock-pheasant (Polyplectron bicalcaratum Linnaeus, 1758), the silver pheasant (Lophura nycthemera Linnaeus, 1758), the Asian water monitor (Varanus salvator Laurenti, 1768) and the Chinese serow (Capricornis milneedwardsii).
Interestingly, we documented a number of various small carnivore species, including the large Indian civet (Viverra zibetha Linnaeus, 1758), the masked palm civet (Paguma larvata C.E.H. Smith, 1827), the spotted linsang (Prionodon pardicolor Hodgson, 1841), the Asian palm civet (Paradoxurus hermaphroditus), the crab-eating mongoose (Herpestes urva Hodgson, 1836), the leopard cat (Prionailurus bengalensis Kerr, 1792) and the yellow-throated marten (Martes flavigula) (Table
The most recent field survey on mammal diversity for Xuan Lien Nature Reserve was published in 2013 (
Amongst our records, the Sunda pangolin is the least expected species, as Xuan Lien falls within the distribution range of the Chinese pangolin (Manis pentadactyla Linnaeus, 1758) (
During our survey, we documented several signs of ongoing human disturbances inside the Reserve, including four illegal logger camps, small mammal traps and snare lines. Some of those activities were spotted deep inside the Reserve and interviews with local people revealed that exploitation of forest products, while illegal, still happened occasionally in Xuan Lien. Accessibility to the Reserve from the dam and the road systems may facilitate illicit activities (Fig.
This research has been conducted under the research project QG.22.72 of Vietnam National University, Hanoi. The authors thank the management board and staff of Xuan Lien Nature Reserve and other local authorities for their support. This work would have been impossible without the enthusiastic help of local people and field assistants in Xuan Lien.
MDL, TVN and ATN designed the study; TVN and ATN led on fieldwork, data analysis and writing; MDL, ATL and HVP acquired funding and supported the fieldwork and writing; HMN, TAP and MTN supported the fieldwork and writing.