An Analysis of Water Security Issues in Jakarta City, Indonesia Destinee Penney & Mandie Yantha
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Algal Blooms Observation Using Stellite Imageries and Massive Fish
Monitoring of Algal Blooms and Massive Fish Kill in the Jakarta Bay, Indonesia using Satellite Imageries Sam Wouthuyzen 1), C.K. Tan 2), J. Ishizaka 3)) Tong Phuoe Hoang Son 4) and Varis Ransi5), Salam Tarigan 1), and Agus Sediadi 6), 1) Research Center for Oceanography, Jakarta, Indonesia. E-mail: [email protected] 2) United Nations University, Japan. E-mail: [email protected] 3) Faculty of Fisheries, Nagasaki University, Nagasaki, Japan. E-mail: ishizaka@net,nagasaki-u.ac.jp 4) Institute of Oceanography, Nha Trang, Vietnam. E-mail: [email protected] 5) National Ocean Service, NOAA, USA. E-mail : [email protected] 6) Agency for the Assessment and Aplication of Technology, Jakarta, Indonesia. E-mail: [email protected] ABSTRACT main threads to the water quality of the bay. Any material discharged into the sea causes some changes. The water environment in the Jakarta Bay gets more Such changes may be great or small, long-lasting or and more stress due to heavy eutrophication and transient, wide spread or extremely localized. If the pollution. In this study, we monitored the change can be detected and is regarded as damaging, concentration of chlorophyll-a as an indicator of it is constitutes pollution (Perez, at al., 2003). eutrophication using Terra and Aqua MODIS Literature review on water quality of the Jakarta Bay (Moderate-resolution Imaging Spectro-radiometer) from 1970’s to present indicated that the Jakarta Bay satellites data from 2004 to 2007. During those get continuous pressures due to eutrophication and periods, there were seven occurrences of massive fish heavy pollutions (Arifin et al., 2003). -
(Pb) Pollution in the River Estuaries of Jakarta Bay
The Sustainable City IX, Vol. 2 1555 Analysis of lead (Pb) pollution in the river estuaries of Jakarta Bay M. Rumanta Universitas Terbuka, Indonesia Abstract The purpose of this study is to obtain information about the level of Pb in the sediment of the estuaries surrounding Jakarta Bay and to compare them. Samples were taken from 9 estuaries by using a grab sampler at three different location points – the left, right and the middle sides of the river. Then, samples were collected in one bottle sample and received drops of concentrated HNO3. The taking of samples was repeated three times. In addition, an in situ measurement of pH and temperature of samples was taken as proponent data. The Pb concentration of the river sediment was measured using an AAS flame in the laboratory of Balai Penelitian Tanah Bogor. Data was analyzed statistically (one way ANOVA and t-test student) by using SPSS-11.5 software. The results show that Pb concentration in the sediment of the estuaries surrounding Jakarta was quite high (20–336 µg/g). The sediment of Ciliwung River in the rainy season was the highest (336 µg/g). Pb concentration of sediment in the dry season was higher than that in the rainy season, except in Ciliwung River. It was concluded that all rivers flowing into Jakarta Bay make a significant contribution to the Pb pollution in Jakarta Bay, and the one with the largest contribution was Ciliwung River. Keywords: Pb, sediment, estuaries, dry season, rainy season, AAS flame. 1 Introduction Jakarta Bay (89 km of length) is formed as a result of the extension of Karawang Cape in the eastern region and Kait Cape in the western region into the Java Sea (Rositasari [1]). -
Reconnaissance Study Of
(a) Large Reservoir and Small Pump Capacity In most drainage areas, a pumping station is characterized by storage of flood in a large reservoir placed at the pumping station so as to minimize pump capacity, thus initial cost and operation cost. Table 3.18 includes data of pump capacity and area of reservoir attached. However, as explained in the 1973 Master Plan Study Report, if pumps are small, the reservoir may not yet empty before the next rainstorm. (b) Complicated Network of Drainage System The pump drainage areas in the DKI Jakarta have complicated network of drains with a lot of gates. Flood water is so controlled by gates to distribute optimum discharge to downstream in consideration of flow capacity of main drain, pump capacity as well as down stream water level including Sea Level. (c) Planning without Consideration of Secondary and Tertiary Drains The other characteristics of drainage system in the DKI Jakarta is that existing pump capacity and starting water level of a reservoir of a pump drainage area are so determined that highest water level or the Design Flood Level along the main drain is lower than the existing bank elevation for one day flood with 25-year return period, assuming that most of rainfall can be drained to the main drain. However, there are a lot of flood prone areas in pump drainage areas. One cause of inundation in flood prone areas may be improper installation/maintenance of secondary/tertiary drains, though gravity drain can be attained. Also high Design Flood Level of main drain may be other causes why rainwater is difficult to be drained. -
Kementerian Keuangan Republik Indonesia Sekretariat Jenderal Pusat Pembinaan Profesi Keuangan
KEMENTERIAN KEUANGAN REPUBLIK INDONESIA SEKRETARIAT JENDERAL PUSAT PEMBINAAN PROFESI KEUANGAN DAFTAR KANTOR AKUNTAN PUBLIK (KAP) YANG TELAH MEMPEROLEH IZIN DARI MENTERI KEUANGAN PER 26 JULI 2021 NO NAMA NO INDUK NO KMK TANGGAL KMK PEMIMPIN KAP ALAMAT NO TELP EMAIL 1 A. Kadir Rahman, Drs., Ak., M.M. 02.2.0498 KEP-109/KM.6/2002 08/05/2002 Abdul Kadir Rahman Jalan Gading Elok Timur V BN 2 No. 1, Kelapa Gading Permai, Jakarta Utara 14240 (021) 4532248 [email protected] 2 A. Salam Rauf, Drs., & Rekan 98.2.0167 KEP-932/KM.17/1998 22/10/1998 Iman Budiman Jl. Pancoran Barat X No. 7 RT. 010/004, Pancoran, Jakarta Selatan 12780 (021) 7948333 [email protected] Jalan Flamboyan Raya H 1 No. 9, Bumi Malaka Asri 3, Malakasari, Duren Sawit, Jakarta 3 Abdul Aziz Fiby Ariza 12.2.0921 856/KM.1/2012 10/08/2012 Abdul Aziz M.N. (021) 86602049, 8632184 [email protected] Timur 13460 Komplek Perumahan Keuangan Jl. Ambulombo III Nomor 11 Karang Tengah Ciledug RT (021) 22271950, (021) 4 Abdul Fattah Guliling 16.2.1074 832/KM.1/2016 25/08/2016 Abdul Fattah Guliling [email protected] 05/RW 06 15157 7304963 5 Abdul Ghonie & Rekan 16.2.1058 129/KM.1/2016 07/03/2016 Abdul Ghonie Abubakar Graha Satria I Lt. 3 Suite 304, Jalan R. S. Fatmawati No. 5, Jakarta Selatan 12430 (021) 7511744 [email protected] Jl. Ir. H. Juanda No. 50 6 Abdul Hamid dan Rekan 16.2.1094 1485/KM.1/2016 28/12/2016 Wilda Farah 021 7417874 [email protected] Perkantoran Ciputat Indah Permai Blok C30 7 Abdul Muntalib Dan Yunus 16.2.1059 124/KM.1/2016 07/03/2016 Yunus Pakpahan Jl. -
Updating the Seabird Fauna of Jakarta Bay, Indonesia
Tirtaningtyas & Yordan: Seabirds of Jakarta Bay, Indonesia, update 11 UPDATING THE SEABIRD FAUNA OF JAKARTA BAY, INDONESIA FRANSISCA N. TIRTANINGTYAS¹ & KHALEB YORDAN² ¹ Burung Laut Indonesia, Depok, East Java 16421, Indonesia ([email protected]) ² Jakarta Birder, Jl. Betung 1/161, Pondok Bambu, East Jakarta 13430, Indonesia Received 17 August 2016, accepted 20 October 2016 ABSTRACT TIRTANINGTYAS, F.N. & YORDAN, K. 2017. Updating the seabird fauna of Jakarta Bay, Indonesia. Marine Ornithology 45: 11–16. Jakarta Bay, with an area of about 490 km2, is located at the edge of the Sunda Straits between Java and Sumatra, positioned on the Java coast between the capes of Tanjung Pasir in the west and Tanjung Karawang in the east. Its marine avifauna has been little studied. The ecology of the area is under threat owing to 1) Jakarta’s Governor Regulation No. 121/2012 zoning the northern coastal area of Jakarta for development through the creation of new islands or reclamation; 2) the condition of Jakarta’s rivers, which are becoming more heavily polluted from increasing domestic and industrial waste flowing into the bay; and 3) other factors such as incidental take. Because of these factors, it is useful to update knowledge of the seabird fauna of Jakarta Bay, part of the East Asian–Australasian Flyway. In 2011–2014 we conducted surveys to quantify seabird occurrence in the area. We identified 18 seabird species, 13 of which were new records for Jakarta Bay; more detailed information is presented for Christmas Island Frigatebird Fregata andrewsi. To better protect Jakarta Bay and its wildlife, regular monitoring is strongly recommended, and such monitoring is best conducted in cooperation with the staff of local government, local people, local non-governmental organization personnel and birdwatchers. -
DKI JAKARTA.Pdf
DAFTAR JEMAAH BERHAK LUNAS TAHAP I TAHUN 1441H/2020M PROVINSI DKI JAKARTA BERHAK LUNAS TAHAP 1 KODE NO NO. PORSI NAMA ALAMAT KECAMATAN EMBARKASI 1 0900024005 NY HAERIYAH JL KIRAI NO.43B RT.06/01 KEBAYORAN BARU JKG 2 0900088988 HENI AMALIA LORONG 101 TIMUR NO. 66 RT 05/02 KOJA JKG 3 0900095483 LUSIA ISTHIATI SUPENI JL.MARUNDA BARU RT.003/03 CILINCING JKG 4 0900101689 EVA FARAH DIBA JL.CIP.JAYA AA/33A RT.009/008 JATINEGARA JKG 5 0900102137 AMINA KP.BARU RT.001/009 CAKUNG JKG 6 0900102532 HJ BARKAH PONDOK KELAPA RT.009/012 DUREN SAWIT JKG 7 0900102637 MARYATI JL.PEJUANG IV NO.36 RT.04/04 KELAPA GADING JKG 8 0900103256 SHOBAH NAWALIAH MENTENG DALAM RT.002/010 TEBET JKG 9 0900103666 SITI SAIDAH MENTENG DALAM RT.002/010 TEBET JKG 10 0900104448 PURWANTO JL.PERSAHABATAN RT.011/004 JAGAKARSA JKG 11 0900106046 AYU NURCAHYANI SETIA BUDI TIMUR RT.02 RW.01 SETIABUDI JKG 12 0900106750 KHUZAIBIYAH JL. LODAN RAYA VI RT.001/001 NO.14 PADEMANGAN JKG 13 0900107703 SUKINI KOMP KOSTRAD RT 11 RW 07 KEBAYORAN LAMA JKG 14 0900108788 CHUSNUL CHOTIMAH JL. JATI BARU III RT 005/004 TANAH ABANG JKG 15 0900108990 ROMELAH JL.BATU I GG.ARAB RT.014/005 PASAR MINGGU JKG 16 0900111076 SITI ROHANI JL.WULUH III NO.11 RT/RW.004/007 PALMERAH JKG 17 0900111109 RETNO KUSTIAH JL.KAYU MANIS V BARU RT.006/004 MATRAMAN JKG 18 0900111812 LILI NURWANTI JL. CIPINANG KEBEMBEM RT.010/010 PULOGADUNG JKG 19 0900111833 GATOT SUGITO JL.PINANG EMASX/UD.10 RT.010/003 KEBAYORAN LAMA JKG 20 0900113012 KASTOLANI KOMP. -
Kode Dan Data Wilayah Administrasi Pemerintahan Provinsi Dki Jakarta
KODE DAN DATA WILAYAH ADMINISTRASI PEMERINTAHAN PROVINSI DKI JAKARTA JUMLAH N A M A / J U M L A H LUAS JUMLAH NAMA PROVINSI / K O D E WILAYAH PENDUDUK K E T E R A N G A N (Jiwa) **) KABUPATEN / KOTA KAB KOTA KECAMATAN KELURAHAN D E S A (Km2) 31 DKI JAKARTA 31.01 1 KAB. ADM. KEP. SERIBU 2 6 - 10,18 21.018 31.01.01 1 Kepulauan Seribu 3 - Utara 31.01.01.1001 1 Pulau Panggang 31.01.01.1002 2 Pulau Kelapa 31.01.01.1003 3 Pulau Harapan 31.01.02 2 Kepulauan Seribu 3 - Selatan. 31.01.02.1001 1 Pulau Tidung 31.01.02.1002 2 Pulau Pari 31.01.02.1003 3 Pulau Untung Jawa 31.71 2 KODYA JAKARTA PUSAT 8 44 - 52,38 792.407 31.71.01 1 Gambir 6 - 31.71.01.1001 1 Gambir 31.71.01.1002 2 Cideng 31.71.01.1003 3 Petojo Utara 31.71.01.1004 4 Petojo Selatan 31.71.01.1005 5 Kebon Pala 31.71.01.1006 6 Duri Pulo 31.71.02 2 Sawah Besar 5 - 31.71.02.1001 1 Pasar Baru 31.71.02.1002 2 Karang Anyar 31.71.02.1003 3 Kartini 31.71.02.1004 4 Gunung Sahari Utara 31.71.02.1005 5 Mangga Dua Selatan 31.71.03 3 Kemayoran 8 - 31.71.03.1001 1 Kemayoran 31.71.03.1002 2 Kebon Kosong 31.71.03.1003 3 Harapan Mulia 31.71.03.1004 4 Serdang 1 N A M A / J U M L A H LUAS JUMLAH NAMA PROVINSI / JUMLAH WILAYAH PENDUDUK K E T E R A N G A N K O D E KABUPATEN / KOTA KAB KOTA KECAMATAN KELURAHAN D E S A (Km2) (Jiwa) **) 31.71.03.1005 5 Gunung Sahari Selatan 31.71.03.1006 6 Cempaka Baru 31.71.03.1007 7 Sumur Batu 31.71.03.1008 8 Utan Panjang 31.71.04 4 Senen 6 - 31.71.04.1001 1 Senen 31.71.04.1002 2 Kenari 31.71.04.1003 3 Paseban 31.71.04.1004 4 Kramat 31.71.04.1005 5 Kwitang 31.71.04.1006 6 Bungur -
No Name Address Distance* Min. Rate*
No Name Address Distance* Min. Rate* Jl. Pejompongan Raya ZenRooms Benhil 0.83 km from Start with: 1 No.2, Jakarta Pusat, Tondano JCC Rp. 338,842 Indonesia RedDoorz @ Jl. Pejompongan Baru No.5, 0.95 km from Start with: 2 Pejompongan Baru Jakarta, Indonesia JCC Rp. 227,272 Jl. Danau Jempang No.77, RedDoorz @ 1.19 km from Start with: 3 Bendungan Hilir, Jakarta Jempangan Benhil JCC Rp. 185,950 Pusat, Jakarta, Indonesia Jl. Anggrek Neli Murni Raya RedDoorz @ 1.27 km from Start with: 4 No.10, Kemanggisan, Kemanggisan JCC Rp. 227,273 Jakarta, Indonesia JL. Blora No. 20, Thamrin, 0.19 km from Start with: 5 Clay Hotel Jakarta Jakarta Sudirman Rp. 288,429 RedDoorz @ Jl. Juana No. 21, Menteng, 0.2 km from Start with: 6 Sudirman Jakarta Pusat, Indonesia Sudirman Rp. 205,785 RedDoorz @ Jl. Juana No. 15, Sudirman, 0.23 km from Start with: 7 Sudirman Station Jakarta Pusat, Indonesia Sudirman Rp. 227,273 Jl. Kota Bumi No. 31 Thamrin, 0.41 km from Start with: 8 Residence 100 Jakarta Pusat, Indonesia Sudirman Rp. 247,107 ZensRoom near Jl. Kotabumi No.31, Thamrin, 0.42 km from Start with: 9 Bundaran HI Jakarta, Indonesia Sudirman Rp. 238,842 Jln. Setiabudi 8 No. 20. RedDoorz 0.61 km from Start with: 10 Setiabudi, Jakarta Selatan, @Setiabudi Sudirman Rp. 205,785 Jakarta 12920, Indonesia Jl. Setia Budi Tengah No.15, Alivio Suites 0.79 km from Start with: 11 RT.5/RW.1, Kuningan, Kuningan Sudirman Rp. 400,826 Jakarta, Indonesia Le Green Suites Jl. Setiabudi Tengah No. -
Asian Green Mussels Perna Viridis (Linnaeus, 1758) Detected in Eastern Indonesia
BioInvasions Records (2015) Volume 4, Issue 1: 23–29 Open Access doi: http://dx.doi.org/10.3391/bir.2015.4.1.04 © 2015 The Author(s). Journal compilation © 2015 REABIC Rapid Communication A ferry line facilitates dispersal: Asian green mussels Perna viridis (Linnaeus, 1758) detected in eastern Indonesia Mareike Huhn1,2*, Neviaty P. Zamani1 and Mark Lenz2 1Marine Centre, Department of Marine Science and Technology, Bogor Agricultural University, Jalan Lingkar Akademi, Kampus IPB Dramaga, Bogor 16680, West Java, Indonesia 2GEOMAR Helmholtz Centre for Ocean Research Kiel, Düsternbrooker Weg 20, 24105 Kiel, Germany E-mail: [email protected] (MH), [email protected] (NZ), [email protected] (ML) *Corresponding author Received: 6 June 2014 / Accepted: 30 October 2014 / Published online: 8 December 2014 Handling editor: Demetrio Boltovskoy Abstract While part of a single country, the Indonesian archipelago covers several biogeographic regions, and the high levels of national shipping likely facilitate transfer of non-native organisms between the different regions. Two vessels of a domestic shipping line appear to have served as a transport vector for the Asian green mussel Perna viridis (Linnaeus, 1758) between regions. This species is indigenous in the western but not in the eastern part of the archipelago, separated historically by the Sunda Shelf. The green mussels collected from the hulls of the ferries when in eastern Indonesia showed a significantly lower body condition index than similar-sized individuals from three different western-Indonesian mussel populations. This was presumably due to reduced food supply during the ships’ voyages. Although this transport- induced food shortage may initially limit the invasive potential (through reduced reproductive rates) of the translocated individuals, the risk that the species will extend its distributional range further into eastern Indonesia is high. -
Multi Purpose Deep Tunnel (MPDT) an Integrated Solution for Flood Control, Water Supply, Waste Wa Ter, Road Tunnel and Public Utilities in the Jakarta Mega City
Multi Purpose Deep Tunnel (MPDT) An Integrated Solution for Flood Control, Water Supply, Waste Wa ter, Road Tunnel and Public Utilities in the Jakarta Mega City Presented to : Singapore International Water Week (SIWW) 2008 June 25, 2008 Suntec Singapore International Convention & Exhibition Centre - Water Leaders Summit and South East Asia Business Forum FIRDAUS ALI, PhD. N A N A I A R Y M A I L N Jakarta Water Supply Regulatory Body E U P M (JWSRB) 1 Environmental Serious Problems being faced by Mega City of Jakarta. 1) Floods, paralyzing the city (Business, Industrial and Municipal damages); a) 2002 Flood damages IDR 9.9 Trillions b) 2007 ditto IDR 8.8 Trillions TOTAL IDR 18.7 Trillions (eq. to USD 2.05 Billions) 2) Raw water scarcity and also badly polluted; 3) Water supply coverage ratio, only around 55 %; 4) Untreated waste water, causing water borne diseases due to e-colli; 5) Excessive abstraction of Ground Water, causing land subsidence and sea water intrusion as well as worsening the flood control management; 6) Traffic congestion is severe, causing national loss IDR 43.3 T/annum (eq. to USD 4.76 B/annum); 7) Climate change worsen the situation. Strategy to Solve Those Problems : STRUCTURAL Urban Integrated Efficient Cost effectiveness MEASURES Infrastructure Development INFRASTRUCTURE SERIOUS PROBLEMS NON STRUCTURAL MEASURES Social Economic Solving Problems Political By Stages Land Acquisition BEST EFFORTS Key Words : 1) Land Acquisition 2) Commitment on Urban Integrated Infrastructure Development by sta ges MULTI PURPOSE DEEP TUNNEL (MPDT) An Integrated Solution for Flood Control, Water Supply, Waste Water, Road Tunnel and Public Utilities in the Jakarta Mega City With the Following Benefits; 1. -
Major Sources and Monthly Variations in the Release of Land-Derived
www.nature.com/scientificreports OPEN Major sources and monthly variations in the release of land- derived marine debris from the Greater Jakarta area, Indonesia Muhammad Reza Cordova * & Intan Suci Nurhati As marine debris becomes increasingly prevalent and induces cascading impacts on marine ecosystems, monitoring of land-derived debris is key for identifying efective mitigation strategies. Indonesia plays a pivotal role in reducing land-derived debris into the oceans considering its extensive coastline, large population and high waste production. We present the frst marine debris monitoring data from Indonesia’s capital, the Greater Jakarta area, by characterizing major sources and monthly variations of debris release at nine river outlets into Jakarta Bay between June 2015-June 2016. Our data show plastics as the most common debris entering Jakarta Bay representing 59% (abundance) or 37% (weight) of the total collected debris. Styrofoam was dominating among plastic debris, highlighting the urgency of reducing plastic and styrofoam uses. Higher debris releases during the rainy season (December-February) highlight the need to intensify river clean-up activities. We estimated an average daily debris release of 97,098 ± 28,932 items or 23 ± 7.10 tons into Jakarta Bay with considerably lower inputs from the capital compared to its neighboring municipalities. Within the plastics category, feld monitoring data yield a daily plastic debris release of 8.32 ± 2.44 tons from the Greater Jakarta area, which is 8–16 times less than global-scale model estimates. Te presence of marine debris − a persistent, solid discarded waste in the marine environment, is pervasive in beaches, coastal waters and open oceans mainly due to land-based human activities. -
Marine Palynological Records in the Southern South China Sea Over the Last 44 Kyr
Marine palynological records in the southern South China Sea over the last 44 kyr Dissertation zur Erlangung des Doktorgrades der Mathematisch-Naturwissenschaftlichen-Fakultät der Christian-Albrechts-Universität zu Kiel vorgelegt von Hiroshi Kawamura Kiel 2002 Referent: Prof. Dr. Wolfgang Kuhnt Koreferent: Dr. habil. Wolfram Brenner Tag der mündlichen Prüfung: 11.12.2002 Zum Druck genehmigt: Kiel, ................................................................... Der Dekan: Prof. Dr. Wulf Depmeier ABSTRACT Dinoflagellate cysts and pollen from the South China Sea (SCS) are investigated to test their applicability as paleoceanographic/paleoclimatic indicators. Modern distribution patterns and species composition of dinoflagellate cysts are determined in 86 surface sediment samples, collected during the R/V Sonne cruises 95, 115 and 140a. A total of 45 dinoflagellate cyst species are identified. The highest concentrations are found in the shallow coastal areas (< 50 m water-depth) off middle Vietnam, where the highest surface water productivity is recorded. Similarly, the lowest surface water productivity recorded near the central SCS basin corresponds to the lowest cyst concentrations. Multivariate statistical analysis of the dinoflagellate cyst assemblage show that the distribution patterns and the species compositions are strongly related to the distance of a surface sample from the coast. This relationship may be the the result of offshore transport from the high productivty shallow coastal areas and/or of surface water productivity gradients in the SCS. The dinoflagellate cyst taxa can therefore be divided into three groups on the basis of surface water productivity, namely: eutrophic & coastal-slope, mesotrophic & shelf to slope, and oligotrophic & oceanic. The eutrophic & coastal-slope group is dominated by protoperidinioids such as Brigantedinium spp.