Spatial distribution of mangrove vegetation species, salinity, and mud thickness in mangrove forest in Pangarengan, Cirebon, Indonesia

Purwanto, Ris Hadi; Mulyana, Budi; SATRIA, RYAN ADI; YASIN, EMAD HASSAN ELAWAD; Putra, Ilham Satria Raditya; Putra, Agik Dwika

doi:10.13057/biodiv/d230324

Cited by 9 publications

(5 citation statements)

References 29 publications

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“…The preference for using R. mucronata to plant mangroves also makes this species more dominant in Muarareja Village (Tegal City). The findings of Purwanto et al (2022) suggest that R. mucronata might be a good choice. Since 1997 to enhance the likelihood of success in mangrove rehabilitation programs, mangroves have been planted in Brebes as a measure intended to prevent further abrasion (Susantoro et al 2020).…”

Section: Species Compositionmentioning

confidence: 98%

Carbon stock at several types of mangrove ecosystems in Bregasmalang, Central Java, Indonesia

SUGIATMO

POEDJIRAHAJOE²,

Pudyatmoko³

et al. 2023

Biodiversitas

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Abstract. Sugiatmo, Poedjirahajoe E, Pudyatmoko S, Purwanto RH. 2023. Carbon stock at several types of mangrove ecosystems in Bregasmalang, Central Java, Indonesia. Biodiversitas 24: 182-191. Mangrove ecosystems have an important role but are also faced with the conversion of use and impacts from climate change. Therefore, this research aims to determine the carbon stock above-ground, below-ground, and the soil at several types of mangrove ecosystems in Bregasmalang, Central Java. A total of 8 transect lines, each having a length of 125 m and consisting of six plots, were placed in four types of mangrove ecosystems to obtain data on the diameter of the vegetation and soil at five different depths. Allometric equations were used to analyze diameter data, while the soil compositions were analyzed in the laboratory. The results showed that the total carbon stock in Bregasmalang was 713.13 Mg ha-1 with the details as follows; above-ground 30.27 Mg ha-1 (4%), below-ground 10.99 Mg ha-1 (2%), and soil carbon 671.87 Mg ha-1 (94%). Meanwhile, the total carbon stock in conservation mangrove forests was 763.75 Mg ha-1, rehabilitation mangrove 719.25 Mg ha-1, silvofishery 680.71 Mg ha-1, and ponds 688.81 Mg ha-1. Based on the results, the high soil and total carbon stock in conservation mangroves showed the importance of protecting the ecosystems to mitigate climate change.

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Section: Species Compositionmentioning

confidence: 98%

Carbon stock at several types of mangrove ecosystems in Bregasmalang, Central Java, Indonesia

SUGIATMO

POEDJIRAHAJOE²,

Pudyatmoko³

et al. 2023

Biodiversitas

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“…Another research was conducted on Indonesian mangroves in Gorontalo (Kasim et al 2019), North Maluku (Serosero et al 2020), East Kalimantan (Edwin et al 2021), and West Lombok (Sukuryadi et al 2021) recorded 9, 10, 15 and 12 species, respectively. However, species composition in Benoa Bay's Rhizophora zone had a higher species number than Mare Island (Akbar et al 2016), Jakarta Bay , Situbondo, East Java (Hariyanto et al 2019), Mantehage-Paniki Islands, North Sulawesi (Opa et al 2019) and Cirebon (Purwanto et al 2022) were only found five true mangrove species. Several mangrove species were co-dominantly identified with Rhizophora, such as A. alba, B. hainesii, B. parviflora, E. agallocha, H. littoralis, L. littorea, S. hydrophyllacea, S. ovata and X. moluccensis, as found in Riau (Prianto et al 2006), and A. officinalis, B. cylindrica, B. sexangula, S. caseolaris in North Sumatra, Indonesia (Harefa et al 2022).…”

Section: Mangrove Community Structurementioning

confidence: 99%

Spatial distribution of mangrove health index on three genera dominated zones in Benoa Bay, Bali, Indonesia

SUGIANA¹,

ANDIANI²,

DEWI³

et al. 2022

Biodiversitas

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Abstract. Sugiana IP, Andiani AAE, Dewi IGAIP, Karang IWGA, As-Syakur AR, Fharmawan IWE. 2022. Spatial distribution of mangrove health index on three genera dominated zones in Benoa Bay, Bali, Indonesia. Biodiversitas 23: 3407-3418. A study of mangrove forest stratification was conducted in Benoa Bay which experienced high coastal development pressures during the last decade. The study aimed to determine mangrove health index distribution (MHI) and forest community structures along three genera-dominated zones which were Sonneratia, Rhizophora and Bruguiera. Random forest method was applied to classify the areas of distributed genera along the bay. Forest structure was assessed with 54 plots. The forest was mainly composed of Rhizophora and Sonneratia-dominated zones in a respective forest area proportion at approximately 51% and 45%. Those zones were dominated by R. mucronata and S. alba with an importance value index (IVI) at 266.35% and 145.57%, respectively. A narrow Bruguiera zone composed of B. gymnorrhiza domination was found in the most landward area, only covering 4% of the mangrove area. Overall accuracy and a kappa coefficient indicated high accuracy of forest classification at 97% and 0.94 respectively. We found that 47.44% of mangrove areas could be classified into the highest healthiness category indicating that the mangrove forest in Benoa Bay is in excellent condition. The Rhizophora zone made a significant contribution to the entire forest state since the excellent category coverage in this zone was approximately 73.80%.

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“…The occurrence may arise due to the distinctive attributes of this ecosystem, which serve as inhibitory factors for species. In addition to their high salinity, mangrove forests are also affected by tidal cycles (Froilan et al, 2020;Matatula et al, 2019;Purwanto et al, 2022).…”

Section: Discussionmentioning

confidence: 99%

Features of mangrove ecosystems after ten years of restoration on Flores Island, Indonesia

Wirabuana,

Baskorowati,

Pamungkas

et al. 2024

Preprint

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Indonesia has extensively reforested mangroves to stabilize coastal ecosystems and mitigate climate change. Reforestation's long-term effects on recovering mangroves are not extensively established because most projects are only observed for two years. It raises the question of whether mangrove replanting aids biodiversity conservation and ecological recovery. This project will characterize Flores Island mangrove ecosystems after ten years of regeneration. The ecological survey took place at Bangkoor, Kolisia, and Talibura reforestation areas. Floristic composition, wildlife diversity, carbon sequestration, and energy storage were measured at each location. Field observations revealed 10 plant and 11 animal species, with flora and fauna species varying by site. Flora diversity was highest in Kolisia and fauna diversity was highest in Talibura. Talibura and Kolisia have similar vegetation and wildlife than Bangkoor. Restored mangrove stands sequestered 28.69 − 70.02 Mg CO2 ha− 1 and stored 30.54×104 − 54.07×104 MJ ha− 1 of energy. Rhizophora apiculata (47.37 ± 5.68 kg CO2) had the most carbon sequestration, while Bruguiera gymnorhiza (645.22 ± 21.65 MJ) had the highest energy storage. Reforestation-induced mangrove ecosystems have biodiversity, carbon storage, and energy stock features.

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Spatial distribution of mangrove vegetation species, salinity, and mud thickness in mangrove forest in Pangarengan, Cirebon, Indonesia

Cited by 9 publications

References 29 publications

Carbon stock at several types of mangrove ecosystems in Bregasmalang, Central Java, Indonesia

Carbon stock at several types of mangrove ecosystems in Bregasmalang, Central Java, Indonesia

Spatial distribution of mangrove health index on three genera dominated zones in Benoa Bay, Bali, Indonesia

Features of mangrove ecosystems after ten years of restoration on Flores Island, Indonesia

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