Journal of Marine and Island Cultures

Open Access Journal — ISSN 2212-6821

Home Garden Plant Diversity and Local Knowledge of Plant Species Supporting Biocultural Resilience in a Coastal Village of Northeastern Bali

Siti Fatimah Hanum Research Center for Biota Systems, National Research and Innovation Agency (BRIN) orcid.org/0000-0001-8600-494X

Ayyu Rahayu Research Center for Applied Botany, National Research and Innovation Agency (BRIN) orcid.org/0000-0003-4251-693X

Putri Kesuma Wardani Research Center for Applied Botany, National Research and Innovation Agency (BRIN) orcid.org/0009-0002-9149-5020

Muhammad Bima Atmaja Research Center for Ecology, National Research and Innovation Agency (BRIN) orcid.org/0000-0002-7376-826X

Received 30 April 2025, Accepted 3 November 2025, Available online 28 December 2025
10.21463/jmic.2025.14.3.15

Abstract

Home gardens in the coastal–island landscape of northeastern Bali play a vital role in sustaining local livelihoods, biodiversity, and traditional ecological knowledge. This study analyzed the diversity and cultural significance of home garden plants in Dukuh Village, a coastal community situated on the northeastern slope of Mount Agung, Bali. Field surveys and semi-structured interviews (n = 9) were conducted in three hamlets differing in elevation and proximity to the coast. A total of 115 plant species across 47 families were recorded, including many species with multiple livelihoods and ritual uses. Ritual plants such as Cocos nucifera (used for offerings and temple decorations), Cordyline fruticosa (used in purification rituals), and Plumeria sp. (used for daily offerings) demonstrate the integration of home gardens with Balinese Hindu practices. Multipurpose species such as Gliricidia sepium and Indigofera sp. are used for livestock forage during the dry season, supporting household resilience amid changing climate conditions. Home gardens thus complement coastal livelihoods, including cashew and lontar palm cultivation, as well as small-scale tourism, while reinforcing cultural identity through the use of traditional plants. Despite the small sample size, the findings highlight how home gardens function as socio-ecological systems that link biodiversity, livelihood security, and biocultural knowledge in island communities.

Keywords

biocultural diversity, climate adaptation, coastal livelihoods, home gardens, Balinese Hindu rituals, traditional knowledge

1. Introduction

Balinese life society is inseparable from its local wisdom. The Nyegara Gunung philosophy is a local wisdom related to conservation activities used in Bali. This activity aims to integrate conservation from upstream (mountains) to downstream (sea). This philosophy serves as the primary foundation for the social forestry program in Dukuh Village, Karangasem. This concept is implemented concretely through collaboration between Dukuh Village (mountains) and Tulamben Village (coastal). Through the Nyegara Gunung approach, forest management in Dukuh Village (upstream) is integrated with marine ecosystem management in Tulamben Village (downstream), to create a healthy and sustainable ecosystem from mountains to sea (Anonim, 2022).

Dukuh Village, located in Kubu District, Karangasem Regency, has a unique geographical location in a mountainous region and forms part of the upstream ecosystem. Dukuh Village, located upstream of Tulamben near Mount Agung, is an arid area during the dry season, so the majority of the community has to buy water for their daily needs (Mahardika et al, 2022).

Forest conservation in Dukuh Village is crucial for maintaining water availability, which also impacts the marine ecosystem in Tulamben. This concept ensures that upstream conservation actions will benefit downstream areas. The social forestry program in Dukuh Village goes beyond physical forest management by planting various tree species to restore biodiversity and the ecological function of forests previously damaged by fires and logging. It also integrates the cultural and philosophical values of Nyegara Gunung (mountain state) to create holistic and sustainable conservation (Anonim, 2022).

Besides forests, a common land use in Dukuh Village settlements is home gardens, which have the potential to preserve biodiversity and maintain hydrology in the upstream area. However, information regarding plant species and their role in community life remains limited.

Home gardens are the open spaces around the house, which are also defined as an agroforestry system that is rich in various species of perennial and annual crops with a multisrata vertical structure and often combined with livestock (Kaswanto et al., 2016). Home garden (or pekarangan in Indonesia) is the oldest land use system management. This system is considered to have significant implications for local livelihoods, biodiversity conservation, and sustainable development because of the diversity of flora and fauna (Luo et al., 2024). Home gardens have been used throughout the world as an important additional source of food to improve household food security and nutritional diversity (Saediman et al., 2021). In Bali, particularly in Dukuh Village located on the northeastern coastal slope of Mount Agung, these gardens play a vital role in linking upland agriculture with coastal livelihoods. The village lies within a coastal–island transition zone, where people depend on terrestrial and marine resources. Many households combine farming with cashew, lontar palm, and small-scale tourism or trade along the nearby coast.

Climate change is a change of climate attributed directly or indirectly to human activity that alters the composition of the global atmosphere and natural climate variability observed in comparable time periods. Climate change causes floods, droughts, heat waves, cyclones, wildfires, and rising sea levels (Field et al., 2014). Climate change impacts on livestock will include effects on forage and feed, direct impacts of changes in temperature and water availability on animals, and indirect effects via livestock disease (Porter et al., 2014). In Balinese culture, home gardens reflect traditional ecological knowledge grounded in the Hindu philosophy of Tri Hita Karana—harmonious relationships among humans, nature, and the divine. Species selection is not only determined by ecological suitability but also by religious and cultural significance. Understanding the plant diversity and cultural use of home gardens in this coastal context is essential for developing climate-adaptive, culturally rooted conservation strategies.

This study aims to (1) document home garden plant diversity, (2) analyze their functional and cultural uses, and (3) examine their contribution to coastal and island livelihoods under changing climate conditions. This study helps policymakers scientifically understand the dynamics of home garden plants and related local knowledge, especially the potency of home gardens, to ensure their livelihood is maintained due to climate change. This study fills a research gap by investigating home garden plants in Dukuh villages.

2. Methods

2.1 Study area

The research was conducted in Dukuh Village, Karangasem Regency, northeastern Bali (256–660 m a.s.l.), during December 2022 (Figure 1). The area lies on the volcanic slope of Mount Agung, about 5 km from the coast, and is characterized by a dryland ecosystem with limited freshwater availability. The elevation ranges from 256-660 m asl, with an average annual temperature of 26.91 °C. The total area of Dukuh Village is 234.72 km² and has a resident population of approximately 88.631 people. Most inhabitants belong to the Balinese Hindu community. We selected three hamlets: Buana Kusuma, Bahel, and Pandan Sari. Buana Kusuma and Pandan Sari hamlets are located near the forest, while Bahel is in the middle of the village.

The map of the study area

2.2 Field survey

Nine home gardens were selected purposively to represent different elevations and distances from the coast. Each site contained two 20 × 20 m plots (Appendix 1). Plant species were recorded and identified, while local names and uses were confirmed through semi-structured interviews with adult household members (n = 9). The limited sample size reflects logistical constraints and the focus on accessible and well-maintained gardens.

2.3 Data analysis

The plants that have been identified are then tabulated, including families, vernacular names, habitus, number of individuals, and Summed Dominant Ratio (SDR). The dominant plant species were analyzed using the index of SDR (Chen et al., 2014; Rahayu et al., 2023; Whitney et al., 2018):

SDR (%) = \( \frac{RD + RF}{2} \)

SDR = summed dominance ratio,
RD (%) = relative density (sum of individuals of a plant species/sum of all individuals of all plant species) x 100%
RF (%) = relative frequency (frequency of certain plant species/ total frequency of all plant species) x 100%

The plant diversity index and dominance ratio were calculated in this study. The Shannon-Wienner diversity index was utilized to analyze plant diversity:

H’ = \( \sum_{i=1}^{s} pi \ln(pi) \)

H’ = Shannon-Wienner diversity index, pi = proportion of the number of individuals of a plant species (ni/N), ni = abundance of a plant species, N = total abundance of all plant species. Results of Shannon-Wienner diversity index calculation should be categorized below (Odum & Barrett, 2009), with a classification of biodiversity: High (H’>3), medium (1≤ H’≤3) and low (H’<1).

Dominance is analyzed using Simpson’s Dominance Index:

C = \(\sum (pi)^2\)

C = Simpson dominance index, pi = proportion of the number of individuals of a plant species (ni/N). If the dominance index value (C) is close to 0, it means there are no dominant species, but if the dominance index value (C) is close to 1, it means there are dominant species. (Odum & Barrett, 2009)

The Use Value (UV) assesses the usage and abundance index of a species. The calculation formula for the Use value is expressed as follows (Hoffman and Gallaher, 2007; Phillips and Gentry, 1993):

UVs = \( ({\sum \mathrm{UV} \space \mathrm{is}}) / (\mathrm{ni})\)

UVs = Sum the informant used values for a species and divide by the total number of informants.
ni = total number of informants interviewed for species s.

The research results included plant identification, SDR calculation, diversity index, dominant index value, categories of plant function and comparison between plants in home garden and local knowledge were then analyzed descriptively.

3. Results and discussion

3.1 Home garden plants diversity

The survey recorded 115 plant species (Appendix 1), encompassing 47 families (Figure 2). This number is greater than the number of plant species growing in other villages in Indonesia, such as in the Samin Sub-Das, Central Java, with 88 species (Muliawati et al., 2018), in the Kemukiman Lueng Putu, Bandar Baru District, Pidie Jaya Regency with 79 species (Zufahmi et al., 2020), in Singai Bakar Village, Bajuin District, Tanah Laut Regency, South Kalimantan Province, 54 species (Husnawaty et al., 2022) and 79 species of plants were found in the home garden of the Antibar Village community, Mempawah Timur District, Mempawah Regency, West Kalimantan (Andriansyah et al., 2015). The environmental conditions, personal needs, local traditions, and environmental conditions, as well as their very local nature, influence the composition of home garden plants (Hadi et al., 2016). Besides, the gardens adjacent to houses provide life necessities or commercial products with knowledge passed down from generation to generation (Pilgrim et al., 2018).

The common plant families discovered in these home gardens include Fabaceae (14 species), Euphorbiaceae (6 species), Amaranthaceae (5 species), Apocynaceae (5 species), and Poaceae (5 species). Many species of Fabaceae are also used for fodder, which is suitable for the occupation of the respondent as a breeder, such as Dalbergia latifolia (sonokeling), Gliricidia sepium (gamal), and Leucaena leucocephala (lamtoro). Besides that, Fabaceae also has the ability to fix nitrogen, which enhances the soil fertility in the regosol soil in Dukuh village. This result follows (Luo et al., 2024), who mention that Fabaceae plants play a vital role in providing food to assist local communities in addressing food insecurity.

Based on our survey, tree plants constituted 35.65% of total plant habitus, followed by herbaceous (31.30%), shrub (25.22%), and climber (8.7%). This shows that the home garden consists of multistrata. The choice of trees may be influenced by economic value. Woody plants have served as income for families in Central Ethiopia (Mammo & Dereje, 2025), while the choices of trees and shrubs in China are also economically important because of the provision of shade and shelter for housing purposes (Luo et al., 2024).

Number of plant families found in the home garden at Dukuh village

3.2 Homegarden Plants Diversity Index

Based on the analysis of the Shannon-Winner diversity index (H’), home garden plant diversity in Dukuh villages is in the high diversity category (H’=3.75). This shows the potency of home gardens to support community livelihoods and fulfill food needs. High species diversity can provide many uses for humans and support biodiversity (Ponton, 2021). Furthermore, the home garden is a means to meet Sustainable Development Goals 1 and 2 on no poverty and zero hunger, respectively (Abdoellah et al., 2020).

Although the soil fertility level is relatively low, it has been proven to support fulfilling community needs with high species diversity. The soil in Dukuh Village is Regosol, which is formed from volcanic material originating from the eruption of Mount Agung. It has a sandy soil texture and many macro pores that affect water storage and soil nutrients because they are easily leaching. Soil solum is also shallow (<50 cm), limiting the development of perennial plant roots.

3.3 Homegarden Plants Dominance Ratio

The Summed Dominant Ratio (SDR) is the sum of relative frequency and relative dominance. High SDR are plants that have a high frequency or can be recorded in many samples and have a higher number of individuals in the research location samples (Rahayu et al., 2023). Based on SDR analysis, the highest (SDR> 3,00) were found most commonly in the home garden of Dukuh village, consisting of Anacardium occidentale (cashew) (11.45), Amaranthus sp (spinach) (4.99), Musa sp (banana) (4.18), Mangifera indica (mango) (3,40), Cocos nucifera (coconut) (3.23), and Plumeria sp (frangipani) (3.03). Cashews and mangoes are highly prevalent because they are economically important plants that support livelihood. In contrast, bananas, coconuts, and frangipani are usually planted to support daily ceremony needs.

3.4 Local Knowledge of Dukuh village inhabitants towards Plants

Based on the results of interviews with the community in Dukuh village, there are 100 species of plants recorded, consisting of 19 species for medicine, 50 species for Hindu ceremonial plants, 6 species as starch food, 21 species for vegetables, 10 species for spices, 11 species for fruit, 7 species for building material, 12 species for cow forage, 6 species for goat forage, 5 species for pig forage and 7 species for bee forage. The Dukuh village community has more information on the use of ceremonial plants and vegetable plants in their daily life (Figure 3). This selection is presumably influenced by the religion/ belief of the community, which is the majority Hindu, and personal preference to choose vegetables to support their daily needs.

In daily Hindu religious ceremonies, people offer canang (woven trays made of lontar or coconut leaves filled with flowers, incense, holy water, and rarapan—simple offerings in the form of food or drink). These canang are then placed in sacred places, such as a pelinggih (a shrine), or in the house terrace. After that, the canang is sprinkled with holy water (tirta) and diayap (a movement of the fingers while reciting a mantra). Although no specific plant species are required, flowering plants are most commonly used, including Cananga odorata, Plumeria sp., Michelia alba, Gardenia jasminoides, Erythrina sp., Nerium oleander, and Nymphaea sp. The Balinese Hindu community believes that colors symbolize their Gods. Yellow flowers symbolize Mahadeva, black symbolizes Lord Vishnu, white symbolizes Lord Shiva, and red symbolizes Lord Brahma (Ristanto et al., 2020). In addition to daily ceremonial needs, flowers are used for other religious ceremonies, such as prayer, making tirta, preparing water for Kumkuman (fragrant water), and decoration for sacred dances (Darma et al., 2021). The other plant parts used in Hindu-Balinese religious rituals, such as leaves, tubers, stems, bark, fruits, and seeds, are also utilized as complementary materials in Hindu-Balinese ritual offerings. The plants used in Hindu religious ceremonies in the home garden are listed in Appendix 1.

Plant utilization by the local knowledge of the Dukuh village community

Meanwhile, the highest use value based on the interview is Cocos nucifera (3.9 %), Musa paradisiaca/ pisang sabe (3.9 %), Artocarpus heterophylla/ jackfruit (2.6%), Azadirachta indica/ intaran (2.6%), and Santalum album/ cendana (2.6%). These plants have the highest use value because they also have more than one plant function (multipurpose plants) (Appendix 2). Cocos nucifera (coconut) has various functions, including medicinal uses, ceremonial purposes, spices, construction materials, pig feed, and bee forage. Musa paradisiaca (pisang sabe) has a function as medicine, a ceremony, a vegetable, a fruit, cattle forage, and pig forage. Santalum album (cendana) has the function as a vegetable, cattle forage, goat forage, pig forage, and Artocarphus heterophyllus (jackfruit) has the function as a vegetable, fruit, and building, cattle forage. The crop combinations found in home gardens are strongly influenced by the specific needs and preferences of the household, as well as nutritional complementarity with other major food sources, alongside ecological and socioeconomic factors (Abdoellah et al., 2020).

Based on local knowledge, the largest proportion of plant species belongs to the Fabaceae family, comprising 10 species, followed by the Euphorbiaceae family, which includes four plant species (Figure 4). Several species of Fabaceae are grown because they have more than one function. The function of vegetables such as undis (Cajanus cajan), komak (Lablab purpureus), red beans (Phaseolus vulgaris), tuwi (Sesbania grandiflora) and asam (Tamarindus indica). The function of ceremony plants such as kemerakan (Caesalpinia pulcherrima), dadap (Erythrina subumbrans), red beans (Phaseolus vulgaris) and the function as forage cattle such as sonokeling (Dalbergia latifolia), gamal (Gliricida sepium), and lamtoro (Leucaena leucocephala).

The plant family of local knowledge of the Dukuh village community from the interview

3.5 Analysis of differences in local knowledge with the species found in the home garden

Based on the results of interviews and plant inventory, it was found that there was a difference in the number and function of plants, as determined by local community knowledge, compared to those found in the home garden (Table 1). From the results of the interviews, as many as 100 species of plants are known to the public. Meanwhile, from the inventory results in the community's home garden, the home garden collected 115 plant species. However, not all species of plants in the home garden are known to have potential by the community, and not all the species of plants whose potential is known by the community are planted in the home garden. Only about 39% or as many as 45 plant species in the home garden have the potential to be known and utilized by the community of Dukuh village. It is estimated that 45 plant species are deliberately planted to help meet their daily needs. The factor that influences this is presumably related to the total area of the home garden and the preference of plant selection from the community (dietary requirement, economic value, or religion/ beliefs).

Comparisons between the results of the plant inventory and interviews
The criteria The number of plants from the interview (species) The number of plants found in the home garden (species)
The number of plant species 100 45
Plant function
Vegetable 21 12
Fruit 11 4
Spice 10 3
Starch 6 2
Medicine 19 7
Livestock forage 30 15
Building 7 7
Hindu ceremony 50 23

Furthermore, the religious/ cultural beliefs, customs, and taboos of the villagers influence the composition/ diversity of home gardens (Kumar & Nair, 2004). Presumably, the area of the home garden also determines the type of plants.

3.6 Impact of Climate Change on the Community Livelihoods

Almost everyone in Dukuh village depends on a life that interacts directly with nature. The two main plantation commodities of the Dukuh village community are cashew (Anacardium occidentale) and lontar (Borassus flabellifer). During the dry season, the community harvests the fruits of their garden crops, including cashews (Anacardium occidentale), lontar (Borassus flabellifer), and mangoes (Mangifera spp.). Meanwhile, during the rainy season, the community initiates activities for rainfed farmers, such as planting pumpkin, beans, and tuber crops. Some of these agricultural commodities are sold and partly used to meet the needs of people’s own households. The community also planted a small part of their home garden with cattle forage, such as elephant grass (Cenchrus purpureus), gamal (Gliricida sepium), Indigofera (Indigofera sp.), and sonokeling (Dalbergia latifolia). Some livestock the community raises include cows, goats, pigs, and chickens. In the rainy season, when there is still a stock of water from the rain, people can still harvest forage cattle. However, during the rainy season, people usually purchase forage outside Dukuh village to supplement their cattle's needs. Livestock products such as goats and cows are sold during the Islamic ceremony (Eid al-Adha). Meanwhile, pigs and chickens are usually only sold when there is an urgent need. Some are also used in Balinese Hindu ceremonies.

In 2021, the dry month (with no rain) lasted for four months, from June to September. In 2022, there were fluctuations in rain, during which the originally dry months experienced rain. Meanwhile, in 2023, the rain distribution pattern is similar to that of 2021, but it only entered the dry season in August (Figure 2). According to respondents, the rain causes the quality of the seeds to be poor (the color of the seeds becomes darker and smaller), and the production becomes low because the flowers fall off and cause them to fail to become fruit. Almost all respondents stated that the climate in Dukuh Village has shifted, causing a significant decrease in their main commodity, cashew production.

The climate condition in Dukuh village from 2021-2023

3.7 Homegarden Management Strategy to Climate Change

The Hindu community in Bali has a unique character that is the identity of the Hindu community in Bali (Suwena, 2018). The concept of Tri Hita Karana gives the mandate to maintain a harmonious relationship, namely between humans and God; humans and humans; and humans and nature. Along with the division of the Tri Mandala space, there are three main areas: the Main Mandala, where humans interact with God; the Madia Mandala, where humans interact with humans; and the Nista Mandala, where humans interact with the environment. Its existence is universal and easy to recognize and understand (Raka et al., 2017). This is done consciously to ensure that local knowledge is passed down to the next generation, including plants used in Hindu ceremonies in Bali (Surata et al., 2015).

Conservation is a very urgent necessity to develop the spirit or personality of a participatory community. A form of work that cannot be carried out alone. The activities include maintenance following the situation and conditions of the local village (Samedi, 2021). Conservation efforts are prioritized for plants with high utility index values and suitable habitats. A previous study found that the sustainability of home garden management can be achieved by involving the local community, implementing education programs, providing economic incentives, and offering training to increase land productivity (Hakim et al., 2018). Conservation priorities are based on types that support food security, have high utilization value, and are suitable for the climate conditions of Dukuh Village. Some alternative food crops that meet these criteria, such as corn, peanuts, soybeans, and sorghum, can survive with little water. During the long dry season, the people of Dukuh Village face difficulty obtaining forage stocks for their livestock. So far, the community has relied only on fodder from Gamal (Gliricidia sepium) leaves, Sonokeling (Dalbergia latifolia), and elephant grass (Cenchrus purpureus) that they plant around the garden.

During the dry season, Gamal (Gliricida sepium) and Sonokeling (Dalbergia latifolia) trees shed their leaves, while the availability of alternative feeds, such as those from elephant grass, is also very limited. So far, the community has only relied on fodder from Gamal (Gliricida sepium) leaves, Sonokeling (Dalbergia latifolia), and elephant grass (Cenchrus purpureus) that they plant around the garden. Previous research has revealed that planting silvopastoral-oriented fodder plants, when planned properly and appropriately, can be a viable solution (Chaudhry et al., 2011). Programs that can be carried out include developing community capacity to survive drought by creating innovations in fodder sources. This can also create a source of high-quality grass, shrub, and fodder tree seeds that are sustainable for future rehabilitation. We recommend some plants as fodder sources, such as Indigofera and Brachiaria humidicola (also known as coroivia grass), as an alternative forage substitute during the dry season to improve the welfare of farmers, as they do not need to buy feed for their livestock. The nutrient content in Indigofera leaves has been qualified as fodder and green concentrate for ruminants and could be substituted for poultry (Antari et al., 2022; Nadir et al., 2024). The plant is also tolerant of drought and waterlogging and is resistant to salinity. Recent research indicates that the growth of Indigofera sp. is very good during the rainy season, with no significant difference in growth compared to the dry season (Arniaty et al., 2015). Brachiaria humidicola grass is also one of the superior types of grass, as it has a high production rate and is preferred by livestock. Brachiaria humidicola grass is a plant resistant to seasonal changes, tolerant of poor irrigation, and heavy grazing (Hernandez et al., 2017; Loi et al., 2019; Maia et al., 2014). Therefore, these two plants are suitable for development as cattle forage alternatives in Dukuh Village. The research focused on selecting and managing drought-tolerant plants, as well as livestock nutritional needs during the dry season, and other methods to reduce environmental degradation must also continue to be carried out.

The support of the Indonesian Conservation Foundation (KI) in helping to obtain management rights for the Dukuh village forest also indirectly contributes to supporting community income. The community can also utilize the village forest to plant fodder crops, provided they are not allowed to cut down existing trees. Thus, the Dukuh community can focus on planting their home garden with plants to support food security, while meeting the needs for fodder can be achieved by renting land in the village forest.

Home garden management efforts can still be optimized for economic, social, and ecological functions if they are associated with existing potential. Capacity-building collaboration between communities and scientific practitioners is essential to enable the exchange of traditional wisdom and modern scientific methods (Mallick et al., 2024). Several innovations in agricultural methods include applying more varied cultivation techniques such as hydroponics, aeroponics, and vertical culture. In addition, cultivation activities with a wider variety of plants can continue to be optimized as an effort to diversify various local resource-based materials. Local community knowledge regarding plant functions was obtained only from older respondents, so it needs to be improved again to ensure the existence and sustainability of local knowledge of the Dukuh Village community. The formation of associations involving the younger generation can be done so that existing local knowledge remains sustainable with support from the local government. This effort is oriented towards long-term goals, namely, to create a more independent community that meets subsistence needs in the future as a form of self-sufficiency resilience at the household level.

4. Conclusions

Home gardens in Dukuh Village represent a biocultural adaptation linking biodiversity, traditional ecological knowledge, and coastal livelihoods. The integration of ritual plants, food crops, and forage species ensures livelihood continuity and reinforces Balinese Hindu cultural identity. Despite the small sample size, this study demonstrates how island communities use home gardens to sustain food security, ritual practices, and ecological balance amid climate change.

Acknowledgments

The author would like to thank I Dewa Putu Darma for the suggestions and input in our research, I Made Iwan Dewantama and I Wayan Mahardika from Yayasan Konservasi Indonesia (KI), who facilitated the implementation of the research in Dukuh Village, I Wayan Soma Adi, I Ngurah Arka, and Pak Darma for their assistance and guidance in the research in the field. This work was done with the help of people from three hamlets of Dukuh Village.

References

  1. Abdoellah, O.S., Schneider, M., Nugraha, L.M., Suparman, Y., Voletta, C. T., Withaningsih, S., Parikesit, Heptiyanggit, A., Hakim, L., 2020. Homegarden commercialization: Extent, household characteristics, and effect on food security and food sovereignty in Rural Indonesia. Sustain. Sci. 15(3): 797–815. https://doi.org/10.1007/s11625-020-00788-9
  2. Andriansyah, S.N., Lovadi, I., Linda, R., 2015. Keanekaragaman jenis tanaman pekarangan di Desa Antibar Kecamatan Mempawah Timur Kabupaten Mempawah. J. Protobiont 4(1): 226–235.
  3. Anonim. 2020. Sosialisasi PAIR di HUtan Desa Dukuh. http://nyegaragunung.net/id/sosialisasi-pair-di-hutan-desa-dukuh/ Accessed on 12 Januari 2023.
  4. Antari, R., Anggraeny, Y.N., Putri, A.S., Sukmasari, P.K., Mariyono, N.H.K., Aprilliza, M.N., 2022. Nutritive and antinutritive contents of Indigofera zollingeriana: Its potency for cattle feed in Indonesia. Livest. Res. Rural Dev. 34(2).
  5. Arniaty, S., Rizmi, A., Ubaitussalihat, 2015. Resistance is planted in plant Indigofera sp. critical land on dry season as source of animal feed ruminant. J. Ilmiah Peternak. 23(2): 44–47.
  6. Chaudhry, P., Bohra, N.K., Choudhary, K.R., 2011. Conserving biodiversity of community forests and rangelands of a hot arid region of India. Land Use Policy 28(3): 506–513. https://doi.org/10.1016/j.landusepol.2010.10.005
  7. Chen, Y.-C., Wu, C.-F., Lin, S.-H., 2014. Mechanisms of forest restoration in landslide treatment areas. Sustainability 6(10), 6766–6780. https://doi.org/10.3390/su6106766.
  8. Darma, I.D.P., Sutomo, S., Hanum, S. F., Iryadi, R., Rahayu, A., 2021. Flowers and Value of Conservation in The Culture of Hindu Community in Bali. Biosaintifika: Journal of Biology & Biology Education, 13(1), 34-40. https://doi.org/10.15294/biosaintifika.v13i1.27054
  9. Hadi, E.E.W., Widyastuti, S.M., Wahyuono, S., 2016. Diversity and utilization of understorey in agroforestry system of Menoreh Hill, Kulon Progo Regency. J. Manusia Lingkung. 23(2): 206. https://doi.org/10.22146/jml.18792.
  10. Hakim, L., Pamungkas, N.R., Wicaksono, K.P., Soemarno, S., 2018. The conservation of Osingnese traditional home garden agroforestry in Banyuwangi, East Java, Indonesia. Agrivita J. Agric. Sci. 40(3). https://doi.org/10.17503/agrivita.v40i3.1605.
  11. Hernandez, A.C., Garay, A.H., Canul, A.J.C., Pedroza, S.I.M., Vera, S.R., Garcia, A.R.R., Rios, J.V., 2017. Components of the yield and nutritional value of Brachiaria humidicola cv Chetumal to different grazing strategies. Rev. Mex.Cienc. Agríc. 8(3): 599–610.
  12. Husnawaty, N.A., Peran, S.B., Fithria, A., 2022. Composition and diversity of plants on garden of Sungai Bakar Village in around the Social Forestry Program. J. Sylva Scienteae 5(4): 539. https://doi.org/10.20527/jss.v5i4.6138
  13. Field, C.B., Barros, V.R., Dokken, D.J., Mach, K.J., Mastrandrea, M.D., Bilir, T.E., Chatterjee, M., Ebi, K.L., Estrada, Y.O., Genova, R.C., Girma, B., Kissel, E.S., Levy, A.N., MacCracken, S., Mastrandrea, P.R., White, L.L., 2014. Climate Change 2014: Impacts, Adaptation, and Vulnerability Working Group II Contribution to the Fifth Assessment Report of the Intergovernmental Panel on Climate Change. Cambridge University Press, Cambridge.
  14. Kaswanto, Filqisthi, T.A., Choliq, M.B.S. 2016. Revitalization of rural landscape homegarden “Pekarangan” as landscape services provider to improve community welfare. J. Lanskap Indon. 8(1): 50–60.
  15. Kumar, B.M., Nair, P.K.R., 2004. The enigma of tropical homegardens. Agrofor. Syst., 61: 135–152.
  16. Loi, B.V., Mui, N.T., Giang, T.V., Thanh, P., Ba, N.X., 2019. Yield and nutritional value of Brachiaria humidicola grass planted in Thua Thien Hue Province, Vietnam. Int. J. Res. Agric. Sciences, 6(2): 40–45.
  17. Luo, J., Li, Q., He, J., Yan, J., Zhang, S., Chang, X., Wu, T., 2024. Local knowledge of homegarden plants in Miao ethnic communities in Laershan region, Xiangxi area, China. J. Ethnobiol. Ethnomed. 20(1): 37. https://doi.org/10.1186/s13002-024-00676-x.
  18. Mahardika, I. W., Santoso, H., & Somadi, I. (2022). Flora Hutan Desa Dukuh. Yayasan Konservasi Indonesia.
  19. Maia, G.A., de Pinho Costa, K.A., de Costa Severiano, E.D., Epifanio, P.S., Neto, J.F., Ribeiro, M.G., Fernandes, P.B., Silva, J.F.G., Gonçalves, W.G., 2014. Yield and chemical composition of Brachiaria forage grasses in the offseason after corn harvest. Am.J. Plant Sci. 05(07): 933–941. https://doi.org/10.4236/ajps.2014.57106.
  20. Mallick, M., Singh, P.K., Pandey, R., 2024. Harvesting resilience: Tribal home-gardens as socio-ecological solutions for climate change adaptation and sustainable development in a protected area. J. Clean. Prod. 445: 141174. https://doi.org/10.1016/j.jclepro.2024.141174.
  21. Mammo, S., Dereje, Y., 2025. Woody species diversity of homegarden agroforestry and their contribution to livelihoods improvement in Dendi District, Central Ethiopia. Agrofor. Syst. 99(3): 59. https://doi.org/10.1007/s10457-025-01157-0.
  22. Muliawati, E.S., Budiastuti, M.T.S., Suprayogo, D., Sutrisno, J., 2018. Agrobiodiversity in the rural home gardens as the food reserve for climate change adaptation (case study: Samin sub-watershed, Central Java, Indonesia). Bulg. J. Agric. Sci. 24(5): 759–767.
  23. Nadir, Syahrir, S., Munasirah, A.L., Warni, I., Sari, N., Satriani, Sulistiawati, A., Anugrah, M. P., 2024. Exploration of nutritional value of Indigofera shoot leaves based on different ages. Int. J. Chem. Biochem. Sci. 25(19). https://doi.org/10.62877/91-IJCBS-24-25-19-91.
  24. Pilgrim, E.S., Osborne, J., Winter, M., 2018. Evaluating the multiple benefits of multi-layered agroforestry systems. Int. J. Agric. Manag. 7(2).
  25. Ponton, K., 2021. The Role of Forest Gardens and Forest Gardeners in the UK’s Agroecological Transition [School of Natural Sciences]. Bangor University, Wales.
  26. Porter, J.R., Xie, L., Challinor, A.J., Cochrane, K., Howden, S.M., Iqbal, M.M., Lobell, D.B., Travasso, M.I., 2014. Food security and food production systems, in: Intergovernmental Panel on Climate Change (IPCC), Climate Change 2014 – Impacts, Adaptation and Vulnerability: Part A: Global and Sectoral Aspects: Working Group II Contribution to the IPCC Fifth Assessment Report. Cambridge University Press, Cambridge, pp. 485–534. https://doi.org/10.1017/CBO9781107415379.012.
  27. Rahayu, S.M., Hakim, L., Batoro, J., Sukenti, K., 2023. Plants diversity of Sasak Tribe homegarden in villages around Mandalika, Lombok Island, Indonesia. J. Mar. Island Cult. 12(3). https://doi.org/10.21463/jmic.2023.12.3.21.
  28. Raka, A.A.G., Parwata, I.W., Gunawarman, A.A.G.R., 2017. Bali in the perspective of culture and tourism. Pustaka Larasan, Denpasar.
  29. Ristanto, R. H., Suryanda, A., Rismayati, A. I., Rimadana, A., Datau, R., 2020. Etnobotani: tumbuhan ritual keagamaan hindu-bali. JPBIO (Jurnal Pendidikan Biologi), 5(1), 96–105. https://doi.org/10.31932/jpbio.v5i1.642
  30. Saediman, H., Gafaruddin, A., Hidrawati, H., Salam, I., Ulimaz, A., Rianse, I. S., Sarinah, S., Taridala, S.A.A., 2021. The contribution of home food gardening program to household food security in Indonesia: A review. WSEAS Trans. Environ. Dev. 17: 795–809. https://doi.org/10.37394/232015.2021.17.75.
  31. Samedi, S., 2021. Konservasi keanekaragaman hayati di Indonesia: rekomendasi perbaikan undang-undang konservasi. J. Hukum Lingkung. Indon. 2(2): 1–28. https://doi.org/10.38011/jhli.v2i2.23.
  32. Surata, I.K., Gata, I.W., Sudiana, I.M., 2015. Studi etnobotanik tanaman upacara Hindu Bali sebagai upaya pelestarian kearifan lokal. J. Kajian Bali 5(2): 265-284.
  33. Suwena, I.W., 2018. Dinamika kebudayaan Bali: Suatu kajian kebudayaan sebagai proses. Sunari Penjor: J. Anthropol. 2(2): 89–101.
  34. Whitney, C.W., Luedeling, E., Tabuti, J.R.S., Nyamukuru, A., Hensel, O., Gebauer, J., Kehlenbeck, K., 2018. Crop diversity in homegardens of southwest Uganda and its importance for rural livelihoods. Agric. Hum. Values 35(2): 399–424. https://doi.org/10.1007/s10460-017-9835-3.
  35. Zufahmi, Dewi, E., Maulinda, 2020. Keanekaragaman jenis tumbuhan pekarangan yang terdapat di kemukiman Lueng Putu Kecamatan Bandar Baru Kabupaten Pidie Jaya. J. Agroristek 3(2): 44–50. https://doi.org/10.47647/jar.v3i2.258.

Appendices

Appendix 1. Plant species at the home garden in Dukuh village, Karangasem

Plant species at the home garden in Dukuh village, Karangasem
No Scientific name / vernacular name Family Number of individuals Habitus H’ C RF RD SDR (%)
1 Acalypha wilkesiana Mull. Arg Euphorbiaceae 2 shrub 0.013 5E-06 0.61 0.22 0.41
2 Accacia mangium Willd. Fabaceae 1 Tree 0.007 1E-06 0.31 0.11 0.21
3 Agave sisalana Perrine Agavaceae 23 herbaceous 0.091 6E-04 1.53 2.47 2.00
4 Allamanda cathartica L. Apocynaceae 7 shrub 0.037 6E-05 1.23 0.75 0.99
5 Aloe vera (L.) Burm.f./ lidah buaya Asphodelaceae 3 herbaceous 0.019 1E-05 0.31 0.32 0.31
6 Alternanthera cultivar Amaranthaceae 1 herbaceous 0.007 1E-06 0.31 0.11 0.21
7 Alternanthera sp./ krokot Amaranthaceae 1 herbaceous 0.007 1E-06 0.31 0.11 0.21
8 Amaranthus sp/ bayam hijau Amaranthaceae 90 herbaceous 0.226 0.009 0.31 9.68 4.99
9 Amaranthus sp/ bayam merah Amaranthaceae 1 herbaceous 0.007 1E-06 0.31 0.11 0.21
10 Amaryllis sp. Amaryllidacaeae 4 herbaceous 0.023 2E-05 0.61 0.43 0.52
11 Amorphophallus muelleri Blume/ porang Araceae 14 herbaceous 0.063 2E-04 0.31 1.51 0.91
12 Anacardium occidentale L/ mete Anacardiaceae 153 tree 0.297 0.027 6.44 16.45 11.45
13 Ananas comosus (L.) Merr./ nanas bromeliaceae 45 herbaceous 0.147 0.002 1.23 4.84 3.03
14 Annona muricata L./ sirsak Annonaceae 1 tree 0.007 1E-06 0.31 0.11 0.21
15 Annona squamosa L./ srikaya Annonaceae 2 tree 0.013 5E-06 0.61 0.22 0.41
16 Antidesma bunius (L.) Spreng./ buni Phyllanthaceae 1 Tree 0.007 1E-06 0.31 0.11 0.21
17 Artemisia scoparia Waldst. & Kit. Asteraceae 19 herbaceous 0.079 4E-04 0.61 2.04 1.33
18 Artocarpus heterophyllus Lam/ jackfruit Moraceae 4 Tree 0.023 2E-05 0.92 0.43 0.68
19 Azadirachta indica A.Juss/ mindi Meliaceae 14 tree 0.063 2E-04 1.53 1.51 1.52
20 Bambusa vulgaris Schrad. ex J.C.Wendl/ bambu ampel Poaceae 2 tree 0.013 5E-06 0.31 0.22 0.26
21 Bauhinia purpurea L. Fabaceae 1 Tree 0.007 1E-06 0.31 0.11 0.21
22 Benincasa hispida (Thunb.) Cogn./ timun bligo cucurbitaceae 4 climber 0.023 2E-05 0.92 0.43 0.68
23 Borassus flabellifer L./ lontar Arecaceae 11 tree 0.052 1E-04 2.76 1.18 1.97
24 Bougainvillea sp. Nyctaginaceae 2 shrub 0.013 5E-06 0.61 0.22 0.41
25 Breynia androgyna (L.) Chakrab. & N.P.Balakr./ daun katuk phyllanthaceae 6 shrub 0.033 4E-05 0.92 0.65 0.78
26 Breynia oblonifolia Mull.Arg/ daun merr Phylanthaceae 8 shrub 0.041 7E-05 1.53 0.86 1.20
27 Brunfelsia uniflora (Pohl) D.Don Solanaceae 1 shrub 0.007 1E-06 0.31 0.11 0.21
28 Caesalpinia pulcherrima (L.) Sw. Fabaceae 1 shrub 0.007 1E-06 0.31 0.11 0.21
29 Cajanus cajan (L.) Huth/ kacang undis Fabaceae 2 herbaceous 0.013 5E-06 0.61 0.22 0.41
30 Cananga odorata (Lam.) Hook.f. & Thomson/ sandat Annonaceae 2 tree 0.013 5E-06 0.61 0.22 0.41
31 Capsicum frutescens L./ cabai rawit Solanaceae 9 herbaceous 0.045 9E-05 0.92 0.97 0.94
32 Carica papaya L./ pepaya Caricaceae 7 tree 0.037 6E-05 1.23 0.75 0.99
33 Caryota mitis Lour. Arecaceae 1 tree 0.007 1E-06 0.31 0.11 0.21
34 Casuarina junghuhniana Miq./ cemara geseng Casuarinaceae 2 tree 0.013 5E-06 0.31 0.22 0.26
35 Catharanthus roseus (L.) G.Don/ tapak dara Apocynaceae 1 herbaceous 0.007 1E-06 0.31 0.11 0.21
36 Cenchrus purpureus (Schumach.) Morrone/ elephant grass Poaceae 14 herbaceous 0.063 2E-04 2.15 1.51 1.83
37 Citrus sp./ jeruk Rutaceae 1 shrub 0.007 1E-06 0.31 0.11 0.21
38 Citrus × amblycarpa (Hassk.) Ochse/ jeruk limo Rutaceae 1 shrub 0.007 1E-06 0.31 0.11 0.21
39 Clerodendrum paniculatum L./ kembang pagoda Lamiaceae 12 shrub 0.056 2E-04 1.53 1.29 1.41
40 Cnidoscolus aconitifolius (Mill.) I.M.Johnst./ papaya jepang Euphorbiaceae 12 shrub 0.056 2E-04 1.23 1.29 1.26
41 Cocos nucifera L./ kelapa Arecaceae 23 tree 0.091 6E-04 3.99 2.47 3.23
42 Codiaeum variegatum (L.) Rumph. ex A.Juss./ puring Euphorbiaceae 7 shrub 0.037 6E-05 0.92 0.75 0.84
43 Cordyline fruticosa (L.) A.Chev. Asparagaceae 6 shrub 0.033 4E-05 1.23 0.65 0.94
44 Cucumis sativus L./ timun Cucurbitaceae 1 climber 0.007 1E-06 0.31 0.11 0.21
45 Curcuma domestica Valeton/ kunyit kuning Zingiberaceae 1 herbaceous 0.007 1E-06 0.31 0.11 0.21
46 Curcuma caesia Roxb/ kunyit hitam Zingiberacea 6 herbaceous 0.033 4E-05 0.31 0.65 0.48
47 Curcuma zedoaria (Christm.) Roscoe/ kunyit putih Zingiberacea 5 herbaceous 0.028 3E-05 0.61 0.54 0.58
48 Cyathula cultivar Amaranthaceae 16 herbaceous 0.07 3E-04 0.00 1.72 0.86
49 Cyclea barbata Miers/ daluman Menispermaceae 1 climber 0.007 1E-06 0.31 0.11 0.21
50 Cymbopogon citratus (DC.) Stapf/ sereh Poaceae 3 herbaceous 0.019 1E-05 0.31 0.32 0.31
51 Dalbergia latifolia Roxb/ sonokeling Fabaceae 8 tree 0.041 7E-05 1.23 0.86 1.04
52 Didymocheton gaudichaudianus A.Juss. Meliaceae 2 tree 0.013 5E-06 0.31 0.22 0.26
53 Dieffenbachia sp. Araceae 1 herbaceous 0.007 1E-06 0.31 0.11 0.21
54 Dioscorea bulbifera L./ mubu Dioscoreaceae 1 herbaceous 0.007 1E-06 0.31 0.11 0.21
55 Dioscorea sp. Dioscoreaceae 1 herbaceous 0.007 1E-06 0.61 0.11 0.36
56 Dracaena angustifolia (Medik.) Roxb./ kayu sugih Asparagaceae 5 shrub 0.028 3E-05 1.23 0.54 0.88
57 Dracaena fragrans (L.) Ker Gawl./ hanjuang Asparagaceae 5 shrub 0.028 3E-05 0.61 0.54 0.58
58 Dracaena sp. Asparagaceae 1 herbaceous 0.007 1E-06 0.00 0.11 0.05
59 Dracaena trifasciata (Prain) Mabb./ lidah mertua Asparagaceae 1 herbaceous 0.007 1E-06 0.31 0.11 0.21
60 Erythrina sp./ dadap Fabaceae 1 shrub 0.007 1E-06 0.31 0.11 0.21
61 Erythrina subumbrans (Hassk.) Merr./ dadap tis Fabaceae 3 shrub 0.019 1E-05 0.92 0.32 0.62
62 Euphorbia sp. Euphorbiaceae 2 shrub 0.013 5E-06 0.31 0.22 0.26
63 Ficus benjamina L./ beringin moraceae 3 tree 0.019 1E-05 0.31 0.32 0.31
64 Ficus sp. / bunut Moraceae 1 tree 0.007 1E-06 0.31 0.11 0.21
65 Ficus variegata Blume/ ara Moraceae 4 tree 0.023 2E-05 0.31 0.43 0.37
66 Gardenia jasminoides J. Ellis/ jempiring Rubiaceae 1 shrub 0.007 1E-06 0.31 0.11 0.21
67 Gliricidia sepium (Jacq.)Kunth/ gamal Fabaceae 28 tree 0.105 9E-04 2.45 3.01 2.73
68 Gmelina arborea Roxb. ex Sm/ jati belanda Lamiaceae 21 tree 0.086 5E-04 2.45 2.26 2.36
69 Hibiscus rosa sinensis Linn./ kembang sepatu Malvaceae 5 shrub 0.028 3E-05 1.23 0.54 0.88
70 Indigofera suffruticosa Mill./ tarum Fabaceae 3 shrub 0.019 1E-05 0.61 0.32 0.47
71 Ixora javanica (Blume) DC./ soka Rubiaceae 1 shrub 0.007 1E-06 0.31 0.11 0.21
72 Justicia gendarussa Burm.f. Acanthaceae 1 shrub 0.007 1E-06 0.31 0.11 0.21
73 Kalanchoe pinnata (Lam.) Pers /cocor bebek Crassulaceae 3 herbaceous 0.019 1E-05 0.61 0.32 0.47
74 Lablab purpureus (L.) Sweet/ kacang komak Fabaceae 2 herbaceous 0.013 5E-06 0.61 0.22 0.41
75 Lannea coromandelica L./ santen Anacardiaceae 10 tree 0.049 1E-04 1.53 1.08 1.30
76 Leucaena leucocephala (Lam.) de Wit/ lamtoro Fabaceae 4 tree 0.023 2E-05 0.92 0.43 0.68
77 Ligustrum glomeratum Blume/ padi-padi Oleaceae 1 tree 0.007 1E-06 0.31 0.11 0.21
78 Magnolia champaca (L.) Baill. ex Pierre Magnoliaceae 2 tree 0.013 5E-06 0.31 0.22 0.26
79 Mangifera indica L./ mangga Anacardiaceae 29 tree 0.108 1E-03 3.68 3.12 3.40
80 Manihot esculenta Crantz/ singkong Euphorbiaceae 16 shrub 0.07 3E-04 3.07 1.72 2.39
81 Manilkara kauki (L.) Dubard/ sawo Sapotaceae 1 tree 0.007 1E-06 0.31 0.11 0.21
82 Marantha sp. Maranthaceae 1 herbaceous 0.007 1E-06 0.31 0.11 0.21
83 Melochia umbellata (houtt.) Stapf./ bentenu Meliaceae 15 tree 0.067 3E-04 3.07 1.61 2.34
84 Momordica balsamina L./ pare Cucurbitaceae 9 climber 0.045 9E-05 2.15 0.97 1.56
85 Moringa oleifera Lam./ kelor Moringaceae 3 tree 0.019 1E-05 0.61 0.32 0.47
86 Musa sp./ pisang Musaceae 52 tree 0.161 0.003 2.76 5.59 4.18
87 Passiflora edulis Sims / pasi Passifloraceae 1 climber 0.007 1E-06 0.31 0.11 0.21
88 Phaseolus vulgaris L. / kacang merah Fabaceae 2 herbaceous 0.013 5E-06 0.61 0.22 0.41
89 Phyllanthus sp. Phyllanthaceae 1 shrub 0.007 1E-06 0.31 0.11 0.21
90 Piper sp./ sirih Piperaceae 3 climber 0.019 1E-05 0.92 0.32 0.62
91 Plukenetia volubilis L./ sacca inci Euphorbiaceae 9 climber 0.045 9E-05 0.92 0.97 0.94
92 Plumeria pudica Jacq./ Frangipani japan Apocynaceae 1 shrub 0.007 1E-06 0.31 0.11 0.21
93 Plumeria rubra L./ yellow frangipani Apocynaceae 1 tree 0.007 1E-06 0.31 0.11 0.21
94 Plumeria sp./ frangipani Apocynaceae 25 tree 0.097 7E-04 3.37 2.69 3.03
95 Psidium guajava L./ jambu batu Myrtaceae 2 tree 0.013 5E-06 0.92 0.22 0.57
96 Rosa sp./ mawar Rosaceae 2 herbaceous 0.013 5E-06 0.61 0.22 0.41
97 Roystonea regia (Kunth) O.F.Cook/ palem raja Arecaceae 1 tree 0.007 1E-06 0.31 0.11 0.21
98 Saccharum officinarum L./ tebu Poaceae 5 shrub 0.028 3E-05 0.92 0.54 0.73
99 Santalum album L./ cendana Santalaceae 8 tree 0.041 7E-05 1.23 0.86 1.04
100 Schefflera sp./ kayu tulak Araliaceae 3 shrub 0.019 1E-05 0.61 0.32 0.47
101 Selenicereus monacanthus (Lem.) D.R.Hunt/ buah naga cactaceae 2 climber 0.013 5E-06 0.61 0.22 0.41
102 Sesbania grandiflora (L.) Poir. / turi Fabaceae 2 tree 0.013 5E-06 0.61 0.22 0.41
103 Sicyos edulis Jacq./ labu jepang cucurbitaceae 2 climber 0.013 5E-06 0.31 0.22 0.26
104 Smilax sp./ banah Smilacaceae 1 climber 0.007 1E-06 0.31 0.11 0.21
105 Solanum torvum Sw./ takokak Solanaceae 2 herbaceous 0.013 5E-06 0.61 0.22 0.41
106 Strobilanthes crispa/ kejibeling Acanthaceae 1 shrub 0.007 1E-06 0.31 0.11 0.21
107 Swietenia mahagoni (L.) Jacq./ mahoni Meliaceae 2 tree 0.013 5E-06 0.31 0.22 0.26
108 Syzygium aqueum (Burm.f.) Alston/ jambu air Myrtaceae 5 tree 0.028 3E-05 1.23 0.54 0.88
109 Tagetes erecta L./ gemitir Asteraceae 2 herbaceous 0.013 5E-06 0.31 0.22 0.26
110 Talinum paniculatum (Jacq.) Gaertn./ ginseng Talinaceae 1 herbaceous 0.007 1E-06 0.31 0.11 0.21
111 Tamarindus indica L./ asem Fabaceae 1 tree 0.007 1E-06 0.31 0.11 0.21
112 Tectona grandis L.f./ jati lamiaceae 2 tree 0.013 5E-06 0.61 0.22 0.41
113 Tradescantia spathaceae Sw. / adam hawa Commelinacaea 22 herbaceous 0.089 6E-04 0.61 2.37 1.49
114 Urena lobata L. Malvaceae 9 shrub 0.045 9E-05 0.92 0.97 0.94
115 Zea mays L./ jagung Poaceae 10 herbaceous 0.049 1E-04 1.53 1.08 1.30
Total 930 3.756 0.051

Appendix 2. Plant utilization based on respondent local knowledge

Utilization of plant species in the study area
No Scientific name / vernacular name Suku Utilization Total FR
M C St V Sp F BM CF GF PF BF
1 Alstonia scolaris/ pole Apocinaceae 1 1 0.006
2 Antidesma bunius L. Spreng/ boni Euphorbiaceae 1 1 2 0.013
3 Acorus calamus L./ jangu Zingiberaceae 1 1 0.006
4 Aleurites moluccanus (L.) Willd./ tingkih Euphorbiaceae 1 1 0.006
5 Allium cepa L./ Bawang merah Amaryllidaceae 1 1 2 0.013
6 Allium sativum L./ kesuna Amaryllidaceae 1 1 2 0.013
7 Alpinia galanga / isen Singiberaceae 1 1 0.006
8 Amaranthus spinosus L./ bayem Amaranthaceae 1 1 0.006
9 Amorphophallus sp/ ketil bara Araceae 1 1 0.006
10 Anacardium occidentale/ mente Anacardiaceae 1 1 1 3 0.019
11 Ananas comosus (Linn) Merr/ nanas Bromeliaceae 1 1 0.006
12 Annona muricata L./ sirsak Annonaceae 1 1 0.006
13 Areca catecu/ buah kinang Arecaceae 1 1 0.006
14 Artocarpus heterophyllus Lamk./ jackfruit Moraceae 1 1 1 1 4 0.026
15 Azadirachta indica A. Juss./ intaran Meliaceae 1 1 1 1 4 0.026
16 Baccaurea racemosa (Reinw. Ex Bl.) M.A./ kepundung Euphorbiaceae 1 1 0.006
17 Borassus flabellifer L./ ental Arecaceae 1 1 1 3 0.019
18 Bougainvillea spectabilis/ kembang kertas Nyctaginaceae 1 1 2 0.013
19 Caesalpinia pulcherrima (L.) Swartz/ kemerakan Fabacaeae 1 1 0.006
20 Cajanus cajan (L.) Huth. / kacang undis Fabaceae 1 1 2 0.013
21 Cananga odorata (Lam.) Hook.f. & Thomson/ sandat Annonaceae 1 1 0.006
22 Capsicum annuum L./ tabia Solanaceae 1 1 0.006
23 Carica papaya L./ gedang Caricaceae 1 1 1 3 0.019
24 Citrus × amblycarpa (Hassk.) Ochse/ jeruk limo Rutaceae 1 1 0.006
25 Citrus aurantifolia (Christm.) Swingle/ jeruk lengis Rutaceae 1 1 0.006
26 Citrus sp./ semaga Rutaceae 1 1 0.006
27 Cnidoscolus aconitifolius (Mill.) I.M.Johnst./ daun propil Euphorbiaceae 1 1 0.006
28 Cocos nucifera L./ kelapa Arecaceae 1 1 1 1 1 1 6 0.039
29 Codiaeum variegatum (L.) A.Juss./ puring Euphorbiaceae 1 1 0.006
30 Colocasia esculenta (L.) Schott/ keladi Araceae 1 1 2 0.013
31 Colubrina asiatica (L.) Brongn./ daun pepe Rhamnaceae 1 1 0.006
32 Commelina sp./ daun dakdak Commelinaceae 1 1 0.006
33 Cordyline terminalis/ andong gadang Asparagaceae 1 1 0.006
34 Cordyline terminalis bicolor/ andong bang Asparagaceae 1 1 0.006
35 Cucurbita moschata Duchesne ex Poir./ waluh Cucurbitaceae 1 1 0.006
36 Curcuma domestica Val./ kunyit Zingibraceae 1 1 2 0.013
37 Curcuma sp./ temu agung Zingiberaceae 1 1 0.006
38 Cynodon dactylon (L.)Pers./ padang lepas Poaceae 1 1 0.006
39 Dalbergia latifolia Roxb./ sonokeling Fabacaceae 1 1 1 3 0.019
40 Dioscorea sp./ ubi awung/ mubu Dioscoreaceae 1 1 0.006
41 Dolichos sp / komak Fabaceae 1 1 0.006
42 Durio zibethinus Murr./ duren Bombacaeae 1 1 0.006
43 Erythrina hypaphorus Boerl./ dadap tis Fabaceae 1 1 2 0.013
44 Erythrina subumbrans (Hassk) Merr./ Dadap Fabaceae 1 1 0.006
45 Ficus benjamina L./ beringin Moraceae 1 1 0.006
46 Foeniculum vulgare Mill./ adas Apiaceae 1 1 0.006
47 Garcinia mangostana Linn/. manggis Clusiaceae 1 1 2 0.013
48 Gardenia jasminoides Ellis/ jempiring Rubiaceae 1 1 0.006
49 Gigantochloa sp./ tiing sudamala Poaceae 1 1 0.006
50 Gigantocloa apus (Bl.) ex Schult.f.) Kurz/ tiing tali Poaceae 1 1 0.006
51 Gliricidia sepium; Walp.,/ gamal Fabacaceae 1 1 2 0.013
52 Gmelina arborea/ jati putih Verbenaceae 1 1 2 0.013
53 Gossypium herbaceousccum L./ kapas Malvaceae 1 1 0.006
54 Hibiscus rosa-sinensis L./ pucuk Malvaceae 1 1 0.006
55 Impatiens balsamina L./ pacah Lamiaceae 1 1 0.006
56 Imperata cylindrata / ambengan Poaceae 1 1 0.006
57 Ipomoea batatas Lamarck/ sele bun Convolvulaceae 1 1 2 0.013
58 Kaempferia galanga (Linn.)/ cekuh Zingibraceae 1 1 2 0.013
59 Lablab purpureus (L.) Sweet/ kacang komak Fabaceae 1 1 0.006
60 Leucaena leucocephala (Lamk.) de Wit./ lamtoro Fabaceae 1 1 1 3 0.019
61 Mangifera indica L./ poh Anacardiaceae 1 1 1 3 0.019
62 Mangifera spp./ poh santen, poh dodol, poh amplem Anacardiaceae 1 1 0.006
63 Manihot uttilissima Mull.Arg/ kesele sawi Euphobiaceae 1 1 2 0.013
64 Manilkara zapota (L.) P. Royen/ sabo Sapotaceae 1 1 2 0.013
65 Melochia umbellata/ bentenu Sterculiceae 1 1 0.006
66 Michelia alba DC./ cempaka putih Magnoliaceae 1 1 0.006
67 Moringa oleifera Lam./ kelor Moringaceae 1 1 1 3 0.019
68 Musa paradisiaca L./ pisang sabe) Musaceae 1 1 1 1 1 1 6 0.039
69 Nephelium lappaceum L./ buluan Sapindaceae 1 1 2 0.013
70 Nerium oleander L./ kenyeri Apocynaceae 1 1 0.006
71 Nymphaea sp./ tunjung Nymphayaceae 1 1 0.006
72 Oryza sativa L.f./ padi Poaceaae 1 1 0.006
73 Paederia foetida L./ kesimbukan Rubiaceae 1 1 0.006
74 Pandanus sp./ pandan meduwi Pandanaceae 1 1 0.006
75 Pangium edule Reinw. Ex Blume/ pange Achariaceae 1 1 0.006
76 Pennisetum purpureum/ padang gajah Poaceae 1 1 0.006
77 Phaseolus vulgaris L./ kacang merah Fabacaceae 1 1 0.006
78 Phyllanthus buxyfolius Reinw/ kayu sisih Phyllanthaceae 1 1 0.006
79 Piper bettle L./ base Piperaceae 1 1 2 0.013
80 Piper nigrum L./ mica Piperaceae 1 1 0.006
81 Plumeria alba L./ jepun Apocinaceae 1 1 2 0.013
82 Psidium guajava L./ sotong Myrtaceae 1 1 2 0.013
83 Punica granatum L. / delima Punicaceae 1 1 0.006
84 Saccharum officinarum L./ tebu cemeng Poaeae 1 1 0.006
85 Salacca edulis Reinw/ salak Arecaceae 1 1 0.006
86 Santalum album L/ cendana* Santalaceae 1 1 1 1 4 0.026
87 Sauropus androgynous/ kayu manis Euphorbiaceae 1 1 2 0.013
88 Schefflera elliptica (Blume)/ kayu tulak Araliaceae 1 1 0.006
89 Schleichera oleosa Merr/ kosambi/ kecacil Sapindaceae 1 1 0.006
90 Sechium edule (Jacq.) Swartz./ jepang Cucurbitaceae 1 1 0.006
91 Sesbania grandiflora (L.) Pers./ tuwi Fabaceae 1 1 0.006
92 Solanum melongena L./ terong ungu Solanaceae 1 1 0.006
93 Syzygium aromaticum (L.) Merr.&Perry/ cengkeh Myrtaceae 1 1 0.006
94 Syzygium cumini /juwet Myrtacaeae 1 1 0.006
95 Tagetes erecta L./ gumitir Asteraceae 1 1 0.006
96 Tamarindus indica L./ asam Fabaceae 1 1 0.006
97 Tectona grandis L/ jati Verbenaceae 1 1 0.006
98 Vigna radiate/ kacang hijau Fabacaceae 1 1 0.006
99 Zea mays L./ jagung Poaceae 1 1 0.006
100 Zingiber officinale Roscoe/ jahe Zingibraceae 1 1 2 0.013
Total 19 50 6 21 10 11 7 12 6 5 7 154 1
Notes: M=Medicine; C=Ceremony; St=Starch; V=Vegetable; Sp=Spices; F=Fruit; BM=Building material, CF=Cow fodder, GF=Goat fodder, PF=Pig fodder, BF=Bee fodder