Review: Diversity, structure, and community composition of Bornean heath forest with a focus on Brunei Darussalam
IRSALINA M. IKBAL,
HAZIMAH H.M. DIN,
Wardah H. Tuah
et al.
Abstract:Abstract. Ikbal IM, Din HHM, Tuah WH, Jaafar SM, Ahmad N, Sukri RS. 2023. Review: Diversity, structure, and community composition of Bornean heath forest with a focus on Brunei Darussalam. Biodiversitas 24: 2814-2829. Tropical heath forests, a unique lowland forest ecosystem with high conservation value, are increasingly threatened by disturbances. Heath forests are characterized by trees of short stature and the presence of highly acidic, sandy soils with poor nutrient content. Bornean heath forests are widel… Show more
“…In Brunei Darussalam, C. filiformis is commonly found along the coastal highways where secondary heath ( Kerangas ) forests are located (Rosli, 2014 ; Tennakoon et al., 2016 ). In general, heath forests are characterized by their acidic, nutrient‐poor sandy soils and are home to Kerangas specialists, such as tropical conifers Agathis borneensis , Gymnostoma nobile , and Calophyllum ferrugineum (Ikbal et al., 2023 ; Sellan et al., 2022 ; Wong et al., 2015 ; Zoletto & Cicuzza, 2022 ). However, when disturbed, these forests are often dominated by native pioneer species, such as Rhodomyrtus tomentosa , Timonius flavescens , and Commersonia bartramia , and the exotic and highly invasive Acacia species, which pose a significant threat to the forest ecosystems (Din et al., 2015 ; Newbery, 1991 ; Tuah et al., 2020 ).…”
Hemiparasitic Cassytha filiformis commonly infects native host (Dillenia suffruticosa and Melastoma malabathricum) and introduced host (Acacia auriculiformis and Acacia mangium) species in threatened heath forests in Brunei. This study aims to investigate the impact of parasitism on the ecophysiology of these host species. This study addresses the research gap in understanding the ecophysiology of C. filiformis–host associations, particularly when native and introduced hosts were infected. We generated CO2 and light response curves to examine the effects of increasing CO2 and light levels of infected and uninfected hosts and examined gaseous exchange, mineral nutrients, and secondary bioactive compounds of host–parasite associations. Infected hosts were negatively impacted by C. filiformis as exhibited in the CO2 and light response curves, with C. filiformis–native host association performing better than introduced species. There were no significant differences in photosynthetic parameters between infected and uninfected hosts, except in D. suffruticosa. Certain nutrient contents showed significant differences, but total N, Ca, and K in uninfected hosts were similar to infected hosts. Total phenols and tannins were significantly higher in introduced hosts than native hosts. Our findings asserted that this hemiparasitic vine relies on both its photosynthetic efficiency and nutrient acquisition from its hosts. The parasitism did not significantly hinder the ecophysiological performance of infected hosts, suggesting a plausible co‐existence between the hosts and C. filiformis. This study provides essential ecophysiological information for future research on how C. filiformis can establish itself without negatively impacting the co‐habitating native hosts.
“…In Brunei Darussalam, C. filiformis is commonly found along the coastal highways where secondary heath ( Kerangas ) forests are located (Rosli, 2014 ; Tennakoon et al., 2016 ). In general, heath forests are characterized by their acidic, nutrient‐poor sandy soils and are home to Kerangas specialists, such as tropical conifers Agathis borneensis , Gymnostoma nobile , and Calophyllum ferrugineum (Ikbal et al., 2023 ; Sellan et al., 2022 ; Wong et al., 2015 ; Zoletto & Cicuzza, 2022 ). However, when disturbed, these forests are often dominated by native pioneer species, such as Rhodomyrtus tomentosa , Timonius flavescens , and Commersonia bartramia , and the exotic and highly invasive Acacia species, which pose a significant threat to the forest ecosystems (Din et al., 2015 ; Newbery, 1991 ; Tuah et al., 2020 ).…”
Hemiparasitic Cassytha filiformis commonly infects native host (Dillenia suffruticosa and Melastoma malabathricum) and introduced host (Acacia auriculiformis and Acacia mangium) species in threatened heath forests in Brunei. This study aims to investigate the impact of parasitism on the ecophysiology of these host species. This study addresses the research gap in understanding the ecophysiology of C. filiformis–host associations, particularly when native and introduced hosts were infected. We generated CO2 and light response curves to examine the effects of increasing CO2 and light levels of infected and uninfected hosts and examined gaseous exchange, mineral nutrients, and secondary bioactive compounds of host–parasite associations. Infected hosts were negatively impacted by C. filiformis as exhibited in the CO2 and light response curves, with C. filiformis–native host association performing better than introduced species. There were no significant differences in photosynthetic parameters between infected and uninfected hosts, except in D. suffruticosa. Certain nutrient contents showed significant differences, but total N, Ca, and K in uninfected hosts were similar to infected hosts. Total phenols and tannins were significantly higher in introduced hosts than native hosts. Our findings asserted that this hemiparasitic vine relies on both its photosynthetic efficiency and nutrient acquisition from its hosts. The parasitism did not significantly hinder the ecophysiological performance of infected hosts, suggesting a plausible co‐existence between the hosts and C. filiformis. This study provides essential ecophysiological information for future research on how C. filiformis can establish itself without negatively impacting the co‐habitating native hosts.
“…In Indonesian Borneo (Kalimantan), heath forests occur in the provinces of West Kalimantan (Navratil 2013;Utari et al 2023), Central Kalimantan (Maimunah et al 2019;Kissinger 2022), East Kalimantan (Kartawinata 1980;Navratil 2013;Setiawan et al 2021), North Kalimantan (Agustiorini et al 2022) and South Kalimantan (Nugroho et al 2022b). Heath forests also occur in Brunei Darussalam (Din et al 2015;Ikbal et al 2023;Zaini and Sukri 2014) and Malaysian Borneo (Sabah and Sarawak) (Lim 2006). Besides occurring on the two islands, heath forests can be found in Peninsular Malaysia, such as in Terengganu (Syuharni et al 2014) and Pahang (Chua et al 1995), although according to (Kamoona et al 2023) in Pahang there is a high risk of disappearing or even in some locations it has not seen anymore.…”
Abstract. Soendjoto MA, Riefani MK, Diana S. 2023. Floristic diversity and composition of heath forest in Kuala Tambangan Village, Tanah Laut District, Indonesia. Biodiversitas 24: 5418-5427. Heath forest (kerangas) is a unique ecosystem characterized with sandy soil with poor nutrients. This harsh condition makes heath forest has unique vegetation diversity as well as vulnerable to disturbances. In South Kalimantan, there is a heath forest located in Kuala Tambangan, Tanah Laut District which has never been explored. The research aims to analyze the diversity and composition of vegetation community in heath forest in Kuala Tambangan and identify factors that have the potential to damage the forest. Data was collected using the transect method placed at three sites in the heath forest. Along each transect, 10 observation plots with size 20 m × 20 m were established to record woody plants at the tree level. Within this plot, nested plots with size of 10 m × 10 m was created to record plants at pole level, 5 m × 5 m for saplings and herbaceous plants and 2 m × 2 m for seedlings, ferns and grasses. In total, there were 85 plant species across all observation plots with 79 species were found in the heath soils. Some typical heath forest species were found such as Melaleuca sp., Baeckea frutescens L. and Cratoxylum formosum (Jack) Benth. & Hook.fil. ex Dyer. Important Value Index (IVI) as well as Shannon-Wiener diversity index (H') varied, both by plant group and by study site. For example, the highest IVI of the tree group belonged to Acacia crassicarpa A.Cunn. ex Benth. and Acacia mangium Willd., and for pole level was Melaleuca sp. The lowest diversity occurred at Site B, while the highest was at Site C. The results on vegetation diversity, structure and composition suggest that this forest is in degraded condition. Fires and land conversion are factors that threaten the existence of heath forest in Kuala Tambangan. Our findings recommend the needs of efforts to protect and restore this unique ecosystem.
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