This study aims to determine the types of mangrove vegetation and the factors where mangroves grow in the land of Eti, Teluk Piru, West Seram Regency. The methods used in the measurement and observation in this study were descriptive and field surveys. Based on the results of mangrove research in the country of Eti, Teluk Piru, West Seram Regency, the types of vegetation that make up the mangrove ecosystem at the research site are: Sonneratia alba, Rhizophora apiculata, Rhizophora stylosa, Bruguiera gymnorrhyza, Bruguiera cylindrica, Avicennia officinalis, Xylocarpus granatum, Nypa fruticaria. agallocha and Scyphiphora hydrophyllacea and the measurement results of environmental parameters that affect mangroves, namely. Temperature: the lowest temperature range is 27oC to the highest temperature is 33oC. Salinity: the lowest salinity level is 21 ppt to the highest salinity is 33 ppt. The degree of acidity (pH) of water: the range of the lowest water pH is 5.5 to the highest temperature 8. The degree of acidity (Ph) of the soil: the range of the lowest water pH is 5 to the highest temperature 8. Subsrak: the condition of the soil at the study site has a type of substrate mud up to sandy mud. DO: the average DO front is 2.9 mg/1 and the average DO back is 2.8 mg/1 in the results obtained the average DO value is 5.3 mg/l. mud thickness: the average thickness of the front mud is 43 cm, the average thickness of the middle mud is 31 cm and the average thickness of the rear mud is 29 cm.
This study aims to analyze the air quality of mangrove forests on the coast of Amahai, Central Maluku Regency, including DO, salinity, temperature, pH, TDS, BOD and NH4. Data were analyzed directly in the field and in the laboratory. Measurement of air quality is divided into 3 (three) research locations. Each location represents the condition and character of the environment, namely near the estuary, middle and far from the estuary. The water quality of each location was analyzed descriptively. The results showed that the condition of the coastal waters of Amahai State at high tide had a range (DO between 101.8 – 109.2 mg/l, TDS between 101.8 – 109.2 mm/l, temperature between 29.5 – 30.0 OC, salinity between 3.9 – 4.5, pH between 6.3 – 6.7, NH4 between 0.005 – 0.008 mg/l and BOD between 3 – 3.9 mg/l) compared to low tide conditions with DO quality range between 5.7 – 6.3 mg/l, temperature between 29.0 -29.5 OC, salinity between 3.2 - 4 , pH between 6.3 - 6.9, NH4 between 0.006 - 0.008 mg /l and BOD between 3.2 – 3.7 mg/l). Overall the measurement results are still within the permitted quality standard limits. The air quality index calculation shows DO and TDS parameters in good category, pH and BOD in fairly good category, while DO and salinity parameters are in poor condition. The calculation of the Pollution Index for each parameter is based on the Decree of the Minister of the Environment No. 51 of 2004 at three sampling points, Mangrove Tourism Places, Estuary/River and Amahai Settlement. for each parameter Good Status for parameters DO, salinity, temperature, pH, TDS, BOD and NH4.
Guraping mangrove tourism object is located in North Oba District, Tidore Island City. An area that has an important role in supporting physical, chemical, biological, and social functions. However, with the increase in population, it will certainly affect the ecological sustainability of the mangrove itself due to logging actions carried out by the community. Therefore, in supporting the preservation of mangroves in the village of Guraping, the mangrove area is designated as a protected area and a natural tourist attraction. To support the management of natural tourism in the mangrove area, it is necessary to be supported by information on the feasibility of the Guraping mangrove tourism object. The purpose of this study is to analyze the feasibility of the Guraping mangrove tourism object for natural tourism activities. The research was conducted in July 2022. The research method used is descriptive quantitatif method. Determination of sample points using the purposive sample method, sampling was carried out at 3 observation stations, data analysis using quantitative analysis of mangrove feasibility. The results showed that the mangroves of the Guraping tourism area had an IKW value of 72 with the S2 category ("appropriate") to be developed as a tourist attraction. ABSTRAK Objek wisata mangrove Guraping yang berada di Kecamatan Oba Utara kota Tidore kepulauan. Merupakan kawasan yang memiliki peran penting dalam menunjang fungsi fisik, kimia, biologi, dan sosial. Oleh sebab itu dalam menunjang kelestarian mangrove di desa Guraping kawasan mangrove ditetapkan sebagai kawasan lindung dan objek wisata alam. Untuk menunjang pengelolaan wisata alam dalam kawasan mangrove, perlu didukung dengan informasi kelayakan kawasan objek wisata mangrove Guraping. Adapun tujuan dari penelitian ini adalah menganalisis kelayakan objek wisata mangrove Guraping untuk aktifitas wisata alam. Penelitian di lakukan pada bulan Juli 2022. Metode penelitian yang digunakan yaitu metode deskriptif kuantitatif. Penentuan titik sampel menggunakan metode purposive sample, pengambilan sampel dilakukan di 3 stasiun pengamatan, analisis data menggunakan analisis kelayakan mangrove untuk wisata. Hasil penelitian menunjukkan bahwa mangrove kawasan wisata Guraping memiliki nilai IKW 72 dengan kategori S1 (“sangat sesuai”) untuk dikembangkan sebagai objek daya tarik wisata. Kata kunci : Ekowisata, mangrove, hutan Guraping, objek wisata, Maluku Utara
The availability of potential natural tourist attractions in a place must also be supported by the readiness of human resources through increasing community understanding and skills. The purpose of doing service is to improve the understanding and skills of the community in preparing quality natural tourist attraction objects and to train how to assess the potential of tourism objects based on weighting and scoring according to ADO guidelines. The method used is socialization, observation, and evaluation. The results of the service showed that there was an increase in knowledge and interest in learning from all participants who attended, this was evidenced by the post-test results which showed that there was an increase in the value of understanding the concept of tourist attraction objects, community-based tourism concepts, forms of quality participation and the ability to assess objects based on scoring. This socialization activity is also able to motivate the people of Abubu to develop the potential of existing objects with the readiness of facilities for visitors, as well as foster self-confidence to later be involved in managing natural and cultural resources as quality tourism products.
Desa Taar terletak di kecamatan Dullah Selatan Kota Tual, yang memiliki daya tarik akan kawasan mangrove yang cukup luas sehingga merupakan habitat yang baik bagi beberapa jenis burung. Desa Taar memiliki beberapa jenis burung yang ditemukan antara lain: Cikukua seram (Philemon moluccensis), Gajahan Timur (Numenius madagascariensis), Kowak Malam Merah (Nycticorax caledonicus), Nuri Maluku (Eos bornea), Pergam Tarut (Ducula concina) dan beberapa jenis lainnya. Penelitian ini bertujuan untuk mengetahui keragaman jenis satwa burung pada vegetasi mangrove dan untuk mengetahui pengaruh kerapatan vegetasi mangrove terhadap keragaman jenis satwa burung di desa Taar. Metode pengamatan satwa burung yang digunakan adalah metode Line Transek dan pengamatan vegetasi dilakukan berdasarkan metode Analisis Garis Berpetak pada jalur – jalur pengamatan yang sudah ditentukan. Keragaman satwa burung yang ditemukan di desa Taar pada jalur 1 sampai dengan jalur 10 sebanyak 14 jenis. Pada jalur 1 nilai H’ = 2,02 dengan jumlah jenis 9 satwa burung; jalur 2 H’ = 2,31 jumlah jenis 11 satwa burung; jalur 3 H’ = 2,07 jumlah jenis 10 satwa burung; jalur 4 H’ = 1,83 jumlah jenis 8 satwa burung; jalur 5 H’ = 2,13 jumlah jenis 10 satwa burung; jalur 6 H’ = 2,14 jumlah jenis 11 satwa burung; jalur 7 H’ = 2,20 jumlah jenis 12 satwa burung; jalur 8 H’ = 2,27 jumlah jenis 11 satwa burung; jalur 9 H’ = 2,36 jumlah jenis 12 satwa burung; jalur 10 H’ = 2,25 jumlah jenis 10 satwa burung. hasil analisa regresi menunjukkan tidak ada pengaruh nyata antara variabel kerapatan terhadap keragaman jenis satwa burung.
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