Spatial and Temporal Distribution of Water Plant Based on Satellite Imagery and the Effect in Jatiluhur Reservoir

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Vol 21 No 2 (2024): Jurnal Kesehatan Lingkungan Volume 21 No. 2, Juli 2024
Diterbitkan: Jul 1, 2024

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Arip Rahman
Pusat Riset Konservasi Sumber Daya Laut dan Perairan Darat, BRIN
Masayu Rahmia Anwar Putri
Pusat Riset Konservasi Sumber Daya Laut dan Perairan Darat, BRIN
Sri Endah Purnamaningtyas
Pusat Riset Konservasi Sumber Daya Laut dan Perairan Darat, BRIN
Lismining Pujiyani Astuti
Pusat Riset Konservasi Sumber Daya Laut dan Perairan Darat, BRIN
Andri Warsa
Pusat Riset Konservasi Sumber Daya Laut dan Perairan Darat, BRIN

Abstrak

Water vegetation in lakes or reservoirs can change the water's ecology. Water vegetation in Jatiluhur Reservoirs is dominated by water hyacinth (Eichhornia crassipes). Water hyacinth in lakes or reservoirs becomes an invasive weed that can cause ecological degradation. Jatiluhur Reservoir is one of the water bodies affected by the uncontrolled growth of water vegetation. The study was conducted to determine the spatial and temporal distribution patterns of water vegetation and its effect on Jatiluhur Reservoir. Water vegetation's spatial and temporal distribution was analyzed using Sentinel-2A satellite image data. The Normalized Difference Vegetation Index (NDVI) algorithm was used to see the distribution of water vegetation in the reservoir waters. The observations show that the movement of water vegetation starts from the inlet area and then moves along with the flow of water to the center of the reservoir. Finally, it accumulates in the outlet area. The correlation between vegetation cover area and month of observation obtained the equation y=662.5x + 128.1. Based on the equation, the increasing vegetation cover area in the Jatiluhur Reservoir is predicted to reach 128.1 ha per month. The physical method used for controlling the growth and distribution of vegetation (water hyacinth) in Jatiluhur Reservoir by taking in the waters. Efforts to control vegetation physically must notice the increasing rate of water hyacinth distribution.

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Referensi

Astuti LP, Indriatmoko I. Kemampuan Beberapa Tumbuhan Air dalam Menurunkan Pencemaran Bahan Organik dan Fosfat untuk Memperbaiki Kualitas Air. J Teknol Lingkung. 2018;19(2):183.

Dersseh MG, Kibret AA, Tilahun SA, Worqlul AW, Moges MA, Dagnew DC, et al. Potential of water hyacinth infestation on Lake Tana, Ethiopia: A prediction using a GIS-based multi-criteria technique. Water (Switzerland). 2019;11(9).

Makhanu KS. Impact of water hyacinth on Lake Victoria. Water Sanit All - Partnerships Innov Proc 23rd WEDC Conf. 1997;165–6.

Malik A. Environmental challenge vis a vis opportunity: The case of water hyacinth. Environ Int. 2007;33(1):122–38.

Parolin P, Rudolph B, Bartel S, Bresch C, Poncet C. Worldwide invasion pathways of the South American Eichhornia crassipes. Acta Hortic. 2012;937:1133–40.

Dechassa N. Origin, Distribution, Impact and Management of Water Hyacinth (Eichhornia crassipes (Martius) Solm): A Review. J Environ Earth Sci. 2020;10(10):13–8.

Ismail SN, Subehi L, Mansor A, Mashhor M. Invasive Aquatic Plant Species of Chenderoh Reservoir, Malaysia and Jatiluhur Reservoir, Indonesia. IOP Conf Ser Earth Environ Sci. 2019;380(1).

Rosyidy MK, Ashilah QP, Ash Siddiq IP. Pemanfaatan Citra Sentinel-2 Untuk Monitoring Sebaran dan Luasan Eceng Gondok Secara Spasio-Temporal Sebagai Upaya Menjaga Kondisi Air dan Sanitasi di Inlet Waduk Saguling , Jawa Barat Application of Sentinel-2 Imagery for Monitoring Area and Distribution. Semin Nas Penginderaan Jauh ke-6. 2019;31–40.

Prasetyo S, Anggoro S, Soeprobowati TR. The Growth Rate of Water Hyacinth (Eichhornia Crassipes (Mart.) Solms) in Rawapening Lake, Central Java. J Ecol Eng. 2021;22(6):222–31.

Dewantara EF, Purwanto YJ, Setiawan Y. Strategi Pengendalian Eceng Gondok (Eichornia crassipes) di Perairan Waduk Jatiluhur, Jawa Barat. 2021;18(1):63–74.

Moningkey GS, Andaki JA, Dien CR, Jusuf N, Rarung LK, Moningkey RD. Evaluasi Pengendalian Eceng Gondok (Eichorniacrassipes) Di Danau Tondano Kabupaten Minahasa Dalam Masa Pandemi Covid-19. AKULTURASI J Ilm agrobisnis Perikan. 2021;9(1):65–77.

Hasan MR, Chakrabarti R. Floating aquatic macrophytes – Water hyacinths. Use algae Aquat macrophytes as Feed small-scale Aquac – A Rev. 2009;53–66.

Taabu-Munyaho A, Marshall BE, Tomasson T, Marteinsdottir G. Nile perch and the transformation of Lake Victoria. African J Aquat Sci. 2016;41(2):127–42.

Villamagna AM, Murphy BR. Ecological and socio-economic impacts of invasive water hyacinth (Eichhornia crassipes): A review. Freshw Biol. 2010;55(2):282–98.

Ntiba MJ, Kudoja MW, Mukasa CT. Management Issues in the Lake Victoria Watershed. 2001.

Ongore CO, Aura CM, Ogari Z, Njiru JM, Nyamweya CS. Spatial-temporal dynamics of water hyacinth, Eichhornia crassipes (Mart.) and other macrophytes and their impact on fisheries in Lake Victoria, Kenya. J Great Lakes Res. 2018;44(6):1273–80.

Moningkey AT, Lihiang A, Rampengan MMF. Sebaran Spasial Eceng Gondok (Echornia Crassipes) di Danau Tondano. J Episentrum. 2020;1(3):32–7.

Astuti, Lismining Pujiyantiurfiarini A, Sugianti Y, Warsa A, Rahman A, Hendrawan ALS. Tata Kelola Perikanan Berkelanjutan di Waduk Jatiluhur. Haryadi J, Kartamihardja E., Krismono, Tjahjo DW., Amri K, editors. Penerbit Deepublish. Yogyakarta: PENERBIT DEEPUBLISH; 2016. 260 p.

McFeeters SK. The use of the Normalized Difference Water Index (NDWI) in the delineation of open water features. Remote Sens Environ. 1996;25(3):687–711.

Huete AR, Liu HQ. An Error and Sensitivity Analysis of the Atmospheric and Soil-Correcting Variants of the NDVI for the MODISEOS. IEEE Trans Geosci Remote Sens. 1994;32(4):897–905.

Leprieur C, Kerr YH, Mastorchio S, Meunier JC. Monitoring vegetation cover across semi-arid regions: Comparison of remote observations from various scales. Int J Remote Sens. 2000;21(2):281–300.

Dewantara EF. Strategi Pengendalian Eceng Gondok ( Eichornia crassipes ) di Perairan Waduk Jatiluhur. Institut Pertanian Bogor; 2020.

Greco MKB, Freitas JR de. On two methods to estimate production of Eichhornia crassipes in the eutrophic Pampulha reservoir (MG, Brazil). Brazilian J Biol. 2002;62(3):463–71.

Nusantari E. Kerusakan Danau Limboto Dan Upaya Konservasi Melalui Pemberdayaan Masyarakat Dan Peran Perguruan Tinggi. J Pendidik Biol. 2010;1(2):1–22.

O’Sullivan PE, Reynolds CS. The Lakes Handbook. Vol. 2, The Lakes Handbook. 2007. 1–560 p.