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All Journal Biodiversitas Journal of Biological Diversity
TEGUH HUSODO
Department of Biology, Faculty of Mathematics and Natural Sciences, Universitas Padjadjaran. Jl. Raya Bandung-Sumedang Km. 21, Jatinangor, Sumedang 45363, West Java, Indonesia
Agriculture, Biological Sciences & Forestry Biochemistry, Genetics & Molecular Biology

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Herpetofauna distribution in different land cover types of West Java, Indonesia ERRI NOVIAR MEGANTARA; JIRJIZ JAUHAN; SYA SYA SHANIDA; TEGUH HUSODO; DERRI ACHMAD FAUZI; RANDI HENDRAWAN; INDRI WULANDARI; YUANSAH YUANSAH
Biodiversitas Journal of Biological Diversity Vol. 23 No. 6 (2022)
Publisher : Society for Indonesian Biodiversity

Show Abstract | Download Original | Original Source | Check in Google Scholar | DOI: 10.13057/biodiv/d230626

Abstract

Abstract. Megantara EN, Jauhan J, Shanida SS, Husodo T, Fauzi DA, Hendrawan R, Wulandari I, Yuansah. 2022. Herpetofauna distribution in different land cover types of West Java, Indonesia. Biodiversitas 23: 2990-2999. Herpetofauna is very sensitive and can be used as a biodiversity indicator. Herpetofauna can experience environmental stress due to agricultural activities, tourism, and other disturbances that result in habitat loss. Herpetofauna can be found on various land covers, such as natural forests and human-modified land. This study revealed species associated with natural forests, human-modified land, and both. This study aims to investigate: 1) herpetofauna distribution based on land cover types and 2) the disturbance that threatens the herpetofauna habitat in West Java. Visual Encounter Survey combination with the Auditory Encounter Survey, was applied in this study. The result of this study, the species were found in the natural forest (53 species), human-modified land (63 species), and crater (2 species). Thirty-nine species were found both in the natural forest and human-modified land. The habitat disturbance potentially threatens the species, such as land clearing (it will affect the microclimate of land cover), roadkill, infrastructure development, and tourism activities.
Supporting food security through urban home gardening, Rancasari Sub-district, Bandung City, West Java, Indonesia INDRI WULANDARI; TEGUH HUSODO; DEDE MULYANTO; OEKAN S. ABDOELLAH; CIKA ASTI AMALIA; SHOFI SITI FARHANIAH
Biodiversitas Journal of Biological Diversity Vol. 24 No. 10 (2023)
Publisher : Society for Indonesian Biodiversity

Show Abstract | Download Original | Original Source | Check in Google Scholar | DOI: 10.13057/biodiv/d241043

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Abstract. Wulandari I, Husodo T, Mulyanto D, Abdoellah OS, Amalia CA, Farhaniah S. 2023. Supporting food security through urban home gardening, Rancasari Sub-district, Bandung City, West Java, Indonesia. Biodiversitas 24: 5618-5625. Urban areas are closely related to the increase in human population, which triggers increased demand for land for settlements or housing. The increase in human population is in line with the increase in daily food requirements. As agricultural land decreases, agricultural productivity decreases, but much agricultural land has been converted into non-agricultural land, leading to food insecurity. Urban farming through home gardening is one of the methods to maintain food security amidst limited open land. This study aimed to reveal urban farming as a role model for food security through home gardens in the Rancasari Sub-district, Bandung City, West Java, Indonesia. This study used a quantitative approach. Data were collected using purposive sampling in housing >20 years old in Manjahlega and Mekarjaya Village. Plants are divided based on their utilization, including ornamental, spice, medicine, and food plants. The results showed that 803 species and 20,366 individuals of 130 families were found in Manjahlega Village, while 680 species and 10,862 individuals were found in the Mekarjaya Village. In Manjahlega, mango (Mangifera indica L.) has the highest IVI value of 64.58, while in Mekarjaya, Chinese evergreen (Aglaonema commutatum Schott.) has the highest IVI value of 10.2. Based on their use, ornamental plants have the highest H and R values compared to food, medicines, and spice plants. Ornamental plants dominate home gardens in Rancasari Sub-district. Their home gardens tend to be aimed at providing aesthetic value and beauty rather than producing food, medicines, and spices in the household. Home gardening has not been fully effective in supporting urban farming in Rancasari Sub-district due to the selection of ornamental plants.
Blooming calendar and polliniferous plants in Djuanda Great Forest Park, West Java, Indonesia: Implication for beekeeping management TEGUH HUSODO; INDRI WULANDARI; YOLANI SYAPUTRI; HIKMAT KASMARA; WAWAN HERMAWAN; JOKO KUSMORO; SYA SYA SHANIDA; FADIAH KHAIRINA; M. RIFKY ALIF HAYDAR; M. NAUFAL ASYRAF; RIFKY ROCHIMAT FEBRIAN
Biodiversitas Journal of Biological Diversity Vol. 25 No. 7 (2024)
Publisher : Society for Indonesian Biodiversity

Show Abstract | Download Original | Original Source | Check in Google Scholar | DOI: 10.13057/biodiv/d250743

Abstract

Abstract. Husodo T, Wulandari I, Saputri Y, Kasmara H, Hermawan W, Kusmoro J, Shanida SS, Khairina F, Haydar MRA, Asyraf MN, Febrian RR. 2024. Blooming calendar and polliniferous plants in Djuanda Great Forest Park, West Java, Indonesia: Implication for beekeeping management. Biodiversitas 25: 3216-3229. Information was unavailable regarding the types of pollinator plants and their blooming periods in Djuanda Great Forest Park, West Java, Indonesia. Information about flower blooming seasons was useful for various purposes. These findings will provide a basis for understanding the importance of Apis cerana Fabricius, 1793 in plant pollination and plant species resources for honey bees so that beekeeping practices can be carried out sustainably. The blossoming period of a plant is determined by its blooming period at the time of observation. The blooming period is observed every month in the second and fourth weeks for six months (December 2021-May 2022). Pollen collection was carried out in August 2021 (dry season). Pollen identification was carried out using the acetolysis method, which involves dissolving the non-pollen components of a sample to reveal the pollen grains, thereby enabling accurate identification. An overview of the observation records revealed the presence of 249 plant species from 82 families. The Asteraceae family has the most abundant species richness. Most plants were identified as pollinator plants (30.52%), nectariferous plants (10.04%), and plants that produce both (18.47%). Flowering plants of melliferous plants for honeybees are available throughout the rest of the year, especially from December to May. Therefore, to optimize honey harvesting, it is important to establish multiple colonies during periods of large honey flows. Honeybees may use alternative sugar sources beekeepers provide, such as fruit juice, during nectar scarcity. We would like to know more about the year-round bloom calendar. Sharing knowledge with farmers about the availability of melliferous plants in certain months will empower them to make decisions for sustainable beekeeping.
Co-Authors CIKA ASTI AMALIA DEDE MULYANTO DERRI ACHMAD FAUZI ERRI NOVIAR MEGANTARA FADIAH KHAIRINA HIKMAT KASMARA INDRI WULANDARI INDRI WULANDARI JIRJIZ JAUHAN JOKO KUSMORO M. NAUFAL ASYRAF M. RIFKY ALIF HAYDAR OEKAN S. ABDOELLAH RANDI HENDRAWAN RIFKY ROCHIMAT FEBRIAN SHOFI SITI FARHANIAH SYA SYA SHANIDA SYA SYA SHANIDA WAWAN HERMAWAN YOLANI SYAPUTRI YUANSAH YUANSAH