Journal of Threatened
Taxa | www.threatenedtaxa.org | 26 June 2025 | 17(6): 27110–27115
ISSN 0974-7907 (Online) | ISSN 0974-7893 (Print)
https://doi.org/10.11609/jott.9529.17.6.27110-27115
#9529 | Received 09 April 2024 | Final received 21 April 2025 | Finally
accepted 25 April 2025
A pioneer study of orchids on
Nusa Barung Island of Indonesia
Toni Artaka
1, Bina Swasta Sitepu
2, Fajar Dwi Nur Aji 3, Suryadi 4 & Tri Atmoko 5
1 Bromo Tengger
Semeru National Park, Ministry of Forestry, Malang,
East Java, 65126, Indonesia.
2,5 Research Center for Ecology and
Ethnobiology, National Research and Innovation Agency (BRIN), Cibinong, Bogor, West
Java, 16911, Indonesia.
3 Division of Natural Resources
Conservation (BBKSDA) Jawa Timur,
Ministry of Forestry, Surabaya, East Java, 61253, Indonesia.
4 Yayasan Pakarti,
Malang, East Java, 65154, Indonesia.
5 Research Center for Applied
Zoology, National Research and Innovation Agency (BRIN), Cibinong, Bogor, West
Java, 16911, Indonesia.
1 toniartaka@yahoo.com, 2 bina004@brin.go.id,
3 fajardwinuraji@gmail.com, 4 gondrongsuryadi66@gmail.com,
5 tri.atmoko@brin.go.id (corresponding author)
Editor:
Pankaj Kumar, Department of Biology, Health and Wellness, Miami Dade College,
Miami, Florida, USA. Date
of publication: 26 June 2025
(online & print)
Citation:
Artaka, T., B.S. Sitepu,
F.D.N. Aji, Suryadi &
T. Atmoko (2025). A pioneer study of orchids on Nusa Barung
Island of Indonesia. Journal
of Threatened Taxa 17(6): 27110–27115. https://doi.org/10.11609/jott.9529.17.6.27110-27115
Copyright:
© Artaka et al. 2025. Creative Commons
Attribution 4.0 International License. JoTT allows
unrestricted use, reproduction, and distribution of this article in any medium
by providing adequate credit to the author(s) and the source of publication.
Funding: This study was funded by the National Research and Innovation Agency of Indonesia (BRIN) and the Educational Fund Management Institution (LPDP), Ministry of Finance of Indonesia, through the Riset dan Inovasi untuk Indonesia Maju (RIIM) 2023 scheme (Contract Number: B-3838/II.7.5/FR.06.00/11/2023). Tri Atmoko was assigned the funding as the principal Investigator and coordinator of the project.
Competing interests: The authors declare no competing interests.
Author details: Toni Artaka: Forest Ecosystem Controller (PEH) for wild flora and breeder manager of in situ orchids for ex-situ conservation in Bromo Tengger Semeru National Park. Bina Swasta Sitepu: Botanist and junior researcher for forest ecology at the National Research and Innovation Agency of Indonesia. Fajar Dwi Nur Aji: Forest Ecosystem Controller (PEH) for wild flora and fauna at Division of Natural Resources Conservation (BBKSDA) Jawa Timur. Suryadi: Nature enthusiasts are interested in orchids and other ornamental plants at Yayasan Pakarti. Tri Atmoko: Principal researcher of wildlife bio-ecology and nature conservation at the National Research and Innovation Agency of Indonesia.
Author contributions: Toni Artaka conceptualised research, methodology, data curation, and writing. Tri Atmoko was a principal investigator, conceptualised the methodology, served as supervisor, data curation, writing lead, and funding recipient. Bina SS, Suryadi, and Fajar DNA were involved in data curation and writing.
Acknowledgements: The authors sincerely thank BRIN and LPDP for funding support of this work. We acknowledge the kind support of the Head of BBKSDA Jawa Timur for issuing the research and sample collection permit (Permit number SI.889/K.2/BIDTEK.1/KSA/5/2024 and SK.21/K2/BIDTEK.1/KSA/6/2024). We express our gratitude to the Nusa Barung Research Team, Yayasan Pakarti, Yayasan BBC, and the local community for supporting us in our field surveys.
Abstract: This is the first study
specifically on orchids in the Nusa Barung Island
Wildlife Reserve. Nusa Barung Island has restricted
access. We conducted a 14-day exploration across seven transects, covering a
total distance of 12 km. Previous research only recorded five species of
orchids, whereas our findings identified 17 species, of which 80 % were new
records for this island. Three species of terrestrial orchids were found,
namely Eulophia picta,
Nervilia plicata, and N.
simplex, while the other 14 species were epiphytes/ lithophytes. Vanda
limbata is abundant and can be found growing on
cliffs, while other epiphytes can be found on tree trunks & branches in Jeruk Bay, and Kandangan Bay.
Keywords: Epiphytes, Orchidaceae,
small island, transects, terrestrial orchids, Vanda limbata,
wildlife reserve.
INTRODUCTION
Indonesia is an archipelagic country with more than 17
thousand islands (Indonesian Government 2024). Of that number, 111 are the
outermost small islands, one of which is Nusa Barung
Island (Presidential Decree of Indonesia 2017). The uninhabited Nusa Barung Island is a wildlife reserve that humans rarely
visit due to its relatively difficult accessibility. To reach it, one must
cross the Indian Ocean, which is known for its large waves, unpredictable
weather, and the island itself has limited freshwater sources. These are the
limiting factor for biodiversity research activities on this island, resulting
in a lack of data on its flora and fauna, including the orchid species (Orchidaceae).
Indonesia is one of the World’s orchid biodiversity
centers (Vitt et al. 2023). The country has a natural
distribution of more than 5,500 orchid species or about one-fifth of the
species in the world (Chase et al. 2017; Wati et al.
2023). Of these, 731 species are found on the island of Java, and 231 are
endemic (Comber 1990). Orchids are an important part of the ecosystem and have
high economic and conservation appeal with their morphological, ecological, and
adaptation to various environmental conditions (Sharma et al. 2024). Orchids
are able to survive and thrive in various habitats on Earth (Ziegler 2011).
Much research on orchid diversity on the island of
Java has been conducted in past (Comber 1990; Nurfadilah
et al. 2016; Rindyastuti et al. 2018; Sadili 2019), but these surveys were not conducted
specifically on Nusa Barung Island. General
information on plant diversity in Nusa Barung was
collected by Jacobs (1958) and Partomihardjo &
Ismail (2005). Both provided basic knowledge of the plant species in Nusa Barung Island, although their exploration area was limited.
The previous study (Partomihardjo & Ismail 2005),
only explored the coastal areas at limited locations. The present study
included several inland areas that had not been visited before. This
information is essential considering the unique ecosystem on Nusa Barung Island, which is a small island dominated by karst.
This biodiversity database provides invaluable
information that will serve as a foundation for managing conservation areas.
This study is hence, a valuable first step in gathering biodiversity data on
Nusa Barung Island for managers. This paper is the
result of the first study aimed at identifying and documenting orchid species
on Nusa Barung Island.
STUDY SITE AND METHODS
The study was conducted for two weeks in July 2024 on
Nusa Barung Island, a 76.4 km² wildlife reserve
located in the Indian Ocean. Administratively, it is located in Puger District, Jember Regency,
East Java (Figure 1). Based on DEM SRTM data (https://earthexplorer.usgs.gov/),
this island has an altitude ranging 0–279 m with flat as well as undulating
topography. Based on our general observations, forest types include coastal,
lowland, karst, and mangrove forests. Based on NASA POWER data
(https://power.larc.nasa.gov/) for the past 10 years, the weather patterns are
as follows: annual rainfall ranging 1,129–2,421 mm/ year, an average air
temperature of 26.9 0C (min-max: 24.1–28.8 0C), and an
average air humidity of 81.1 % (min-max: 77.3–85.1 %).
Exploration was carried out following a standard
methodology, for example, in field tracking was conducted on the observation
transects and its surroundings with a width of approximately 15 m from the
transect. Fourteen days were spent to cover seven routes with a total distance
of approximately 12 km, in Plirik-Monyetan (2,083 m),
Kedok Watu (2,508 m), Kandangan Bay (1,530 m), Jeruk
Bay (2,549 m), Ketimo (715 m), Pucung
Prau (1,140 m), and Cambah
Bay-Sumber Gempol (1,544
m). Observations were made on terrestrial and epiphytic orchids. The epiphytic
orchids on the high branches were observed with a binocular and documented with
DSLR digital camera with tele lens. This study was mostly limited to the
observation of individual orchids on high branches more than 20 m from the
ground. The orchids found were identified and documented; the number of
individuals/clumps was counted, and certain individuals were collected for
further identification in Herbarium Wanariset (WAN).
We identified the species by referring to the field guide provided by Comber
(1990) and Artaka (2019).
RESULTS AND DISCUSSION
During the survey, 17 species of orchids of 13 genera
were found (Table 1; Image 1). Three species found were terrestrial orchids,
namely, Eulophia picta
(Image 1F), Nervilia plicata (Image 1I), and N. simplex (Image 1J).
The other species include the epiphyte and lithophyte groups. Vanda tricolor
in Kandangan Bay uses the Bayur
Tree Pterospermum javanicum
as its host, while Luisia zollingeri (Image 1H), found around Kandangan
Bay, attaches to the trunk of the Dysoxylum
sp. The presence of Vanda limbata (Image 1P),
is abundant, growing on cliffs and rocks around Jeruk
Bay. Meanwhile, those around Kandangan Bay grow as
epiphytes with Rhynchostylis retusa (Image 1L), on the Syzygium
sp. as a host.
Although we did not create a permanent plot to
calculate abundance, based on individual/clump counting, several orchid species
were found in small numbers, such as Cymbidium sp., Dendrobium crumenatum, Liparis
parviflora, and Polystachya
concreta (Table 1). Protection and prevention of
illegal harvesting of this species needs to be done more because it has high
vulnerability and potential for local extinction.
Vanda limbata was most commonly found in this study mainly in Kandangan Bay and Jeruk Bay. That
is in line with the results of previous studies. During the exploration
activities, Jacobs (1958) also reported the discovery of V. limbata in Nusa Barung,
alongside species such as Taeniophyllum sp.
and Aerides sp. Partomihardjo
& Ismail (2005) conducted a survey and found V. limbata,
Dendrobium crumenatum, Phaius
flavus, and Taeniophyllum sp. among a
total of 282 flora species. We were unable to find Phaius
flavus in this survey.
Indonesia has a high diversity of Vanda. Out of 90
species of Vanda in the world (POWO 2025), 20 species grow naturally in
Indonesia (Metusala 2011). This is a species that was
initially known to be endemic to the island of Java until it was later found in
Bali, the Nusa Tenggara Islands, Sulawesi, and Maluku (Metusala
2011). This species exhibits a relatively diverse habitat distribution, ranging
from karst cliffs and seashores to attaching itself as an epiphyte on large
tree trunks at altitudes exceeding 500 m (Yulia &
Budiharta 2011). Setiawan
(2018) also noted the presence of V. limbata
as an epiphyte on tamarind trees Tamarindus
indica planted as shade trees in Bangkalan, Madura Islands (East Java).
Sempu Island, a small island also located south of Java
Island, has at least seven orchid species, one of which is also found on Nusa Barung Island, namely Dendrobium crumenatum
(Sadili 2019); other species are Ascochilus
emarginatus, D. subulatum,
Thrixspermum subulatum,
T. acuminatissimum (Rindyastuti
et al. 2018), Taeniophyllum biocellatum (Nurfadilah et
al. 2016), and Grosourdya appendiculata (Sadili 2019).
When compared to the closest location on the mainland of Java Island, as many
as five species of orchids in Nusa Barung are the
same as those found in Bromo Tengger Semeru National Park (Artaka
2019), and three species are the same as in Meru Betiri
National Park (Puspitaningtyas 2007). This phenomenon
shows that distribution of propagules from the main island affects the
biodiversity of Nusa Barung Island as a result of the
dispersion by biotic and abiotic agents, as well as native species that already
existed in this area when the island was separated from it due to rising sea
levels (Schrader et al. 2020).
This survey only covered a small part of Nusa Barung Island, hence it is assumed
that more orchid species may still exist on the island, waiting to be
discovered. Several obstacles during the survey included the limitation in
collecting epiphytic orchid species that grow attached to the crown of large
trees at a height of more than 20 m. Another obstacle was that only a few
orchid species were found flowering during the survey, which coincided with the
dry season in Indonesia (April–September) without flowers, which is a problem
for further identification at the species level. The specimens without flower
were identified only at the genus level, except for the species that have
important identification character on their vegetative organs (e.g., leaf, bulb
and root).
Several species, although not with generative organs,
can still be identified at the species level based on the special vegetative
characteristics they have, such as the Eulophia
picta species. That species is easily recognized
even when it is not flowering because it has a distinctive habitus and tubers
(pseudobulbs). The E. picta was only found
with as many as eight individuals growing on sandy coastal soil media shaded by
the canopy of the Hibiscus tiliaceus tree in Jeruk Bay. The tubers have a depth of 5–-7 cm in the sandy
soil and are characterized by fine-haired roots.
Dendrobium macrostachyum is commonly found attached to trees around the
rain-fed lake (Sumber Gempol).
This species is recognized because of its distinctive habitat, and it always
grows hanging. Preferring shady and windy habitats, it grows together with Polystachya concreta,
Luisia zollingeri,
and Taeniophyllum hasseltii.
The Cymbidium species was found dead on the forest
floor. The genus Cymbidium is recognized from its oval pseudobulbs
covered by leaf sheaths. It is very difficult to determine the species without
a flower. Same is the case with Taeniophyllum
sp., which was also found in vegetative phase.
Further surveys are recommended during the transition
from the rainy to the dry season (October–March) to obtain more complete
information on orchid species with possibly different phenological times.
Several terrestrial orchids typical of the lowlands primarily grow with
completed generative parts during these seasons (Artaka
2019). Expansion of the exploration area is also needed to reach the inland
forest areas that have not been visited yet. This study also supports area
managers for an updated biodiversity database, primarily as a source of natural
orchid germplasm to support cultivation.
Table 1. Species and
distribution of orchids in the Nusa Barung Island
Wildlife Reserve, Indonesia.
|
|
Species |
Habitus |
Individuals/ Clump |
|||||
|
A |
B |
C |
D |
E |
F |
|||
|
1 |
Aerides odorata Lour. (Image 1A) |
Epiphytic |
6 |
40 |
18 |
|
|
|
|
2 |
Arachnis sulingi (Blume) Rchb.f.
(Image 1B) |
Lithophytic |
|
|
18 |
|
|
|
|
3 |
Cymbidium sp. (Image 1C) |
Epiphytic |
|
|
|
1 |
|
|
|
4 |
Dendrobium crumenatum Sw. (Image 1D) |
Epiphytic |
|
|
|
1 |
|
|
|
5 |
Dendrobium macrostachyum Lindl. (Image 1E) |
Epiphytic |
|
|
4 |
|
|
|
|
6 |
Eulophia picta (R.Br.) Ormerod (Image 1F) |
Terrestrial |
|
|
|
|
8 |
|
|
7 |
Liparis parviflora (Blume) Lindl.
(Image 1G) |
Epiphytic |
|
|
|
2 |
|
|
|
8 |
Luisia zollingeri Rchb.f. (Image 1H) |
Epiphytic |
7 |
|
1 |
|
|
|
|
9 |
Nervilia plicata (Andrews) Schltr.
(Image 1I) |
Terrestrial |
|
|
23 |
|
|
|
|
10 |
Nervilia simplex (Thouars) Schltr. (Image 1J) |
Terrestrial |
|
8 |
|
4 |
|
|
|
11 |
Polystachya concreta (Jacq.) Garay
& H.R.Sweet (Image 1K) |
Epiphytic |
|
|
2 |
|
|
|
|
12 |
Rhynchostylis retusa (L.) Blume (Image 1L) |
Epiphytic |
4 |
|
26 |
|
|
|
|
13 |
Taeniophyllum hasseltii Rchb.f. (Image 1M) |
Epiphytic |
18 |
|
3 |
|
|
|
|
14 |
Taeniophyllum sp. (Image 1N) |
Epiphytic |
|
|
6 |
|
|
2 |
|
15 |
Thrixspermumra ciborskii J.J.Sm. (Image 1O) |
Epiphytic |
|
|
|
|
2 |
8 |
|
16 |
Vanda limbata Bl. (Image 1P) |
Lithophytic, Epiphytic |
66 |
|
|
|
abundant |
|
|
17 |
Vanda tricolor Lindl. (Image 1Q) |
Epiphytic |
4 |
15 |
2 |
|
|
|
A—Kandangan Bay | B—Plirik-Monyetan | C—Cambah Bay-Sumber Gempol | D—Kedok Watu | E—Jeruk Bay | F—Pucung Prau.
For figure & images - -
click here for full PDF
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