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"Paradigma baru dalam pengelolaan dan perkembangan industri pertimahan di Provinsi Bangka Belitung telah memunculkan perusahaan-perusahaan yang melaksanakan pemurnian bijih timah. Dalam proses pemurnian bijih timah hingga menjadi logam timah juga menghasilkan s/ag timah yang mengandung unsur radioaktif. Slag yang dihasilkan dikategorikan sebagai TENORM. Data pengukuran radioaktivitas yang dilakukan dalam penelitian sebelumnya menunjukkan bahwa slag yang dihasilkan mengandung unsur radioaktif melebihi batas yang telah ditentukan. Berdasarkan rekomendasi dari Basic Safety Standard yang dikeluarkan oleh international Atomic Energy Agency (IAEA), batas tindakan penanganan TENORM apabila konsentrasinya = 1000 - 10.000 Bq/kg atau mempunyai paparan radiasi gamma = 50 pR/jam. Jika konsentrasi unsur radioaktif dalam TENORM telah memenuhi batasan tersebut maka TENORM harus dikendalikan sebagaimana halnya limbah radioaktif. Dengan kondisi tersebut berdasarkan ketentuan peraturan perundangan, pengeloljaan terhadap slag yang dihasilkan wajib memiliki izin pemanfaatan tenaga nuklir. Penelitian ini mengidentifikasi faktor-faktor yang mempengaruhi perusahaan smelter timah sehingga belum mengelola limbah yang mengandung unsur radioaktif dan membandingkan kinerja sme/er timah dalam pengelolaan limbah yang mengandung unsur radioaktif. Secara umum penelitian ini dimaksudkan untuk menganalisis faktor-faktor yang. mempengaruhi dan membandingkan kinerja syneiter dalam rangka pengelolaan limbah yang mengandung unsur radioaktif ramah lingkungan.

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The new paradigm in the management and development on tin industry in Bangka Belitung Province has made the emergence of companies whose business is in the menagement and purification of tin ore. On the other hand, the process of the processing and purification of tin ore into tin metal also produce byproduct such as among others monasite, ilmenite, and slag which contain radioactive elements. Category of produced s/ag is TENORM. Radioactivity measurement data from the previous research indicates that the slag produced contains radioactive elements exceeding the established limit. Based on the recommendations from basic Safety Standard issued by IAEA, the limit for management of TENORM is if the concentration is = 1000 - 10.000 Ba/kg or it has gamma-radiation exposure = 50 pR/hour. if concentration of radioactive elements exceeding the established limit of TENORM, It must be controlled in the same manner as in controlling radioactive wastes. Given the condition, pursuant to laws and regulations the management of produced slag requires a licence for utilization of nuclear energy. This research identifies factors influencing the activities of tin smelter which makes the management of waste and compare the performance of tin smelter in managing the waste containing radioactive elements are not yet properly conducted. This research has the objective to analyze factors influencing and compare the performance of tin smelter, environmentally-friendly in managing the waste containing radioactive elements from tin smelters. "

"Pengembangan kapas transgenik dilakukan untuk memenuhi kebutuhan serat kapas yang mencapai 464.400 ton per tahun, untuk industri tekstil di Indonesia. Produksi kapas Indonesia hanya dapat memenuhi 2% kebutuhan dalam negeri sehingga sisa kebutuhan kapas harus dipenuhi melalui impor.Rendahnya produktivitas kapas di Indonesia dipengaruhi oleh beberapa faktor, diantaranya iklim, teknologi budidaya, ketersediaan bibit unggul serta gangguan hama dan penyakit. Faktor-faktor tersebut mengakibatkan pertumbuhan dan perkembangan tanaman terganggu sehingga potensi produksi tanaman kapas menjadi tidak optimal.Kapas transgenik Bollgard adalah salah satu produk rekayasa genetik yang dikembangkan melalui teknik rekombinan ADN. Gen Bt yang ditransfer ke tanaman kapas memiliki efektivitas pengendalian yang tinggi terhadap hama utama tanaman kapas H. armigera sehingga melalui pengembangan kapas transgenik diharapkan produktivitas tanaman kapas dapat ditingkatkan.Di samping meningkatkan produktivitas, dalam pengembangan kapas transgenik Bollgard harus dilakukan pengkajian terutama pada saat dilepas ke lingkungan, mengingat protein crylAc yang dihasilkan oleh Bt di dalam kapas Bollgard kemungkinan dapat tertransfer ke tanaman lain, berpengaruh pada serangga non-target maupun jumlah mikroba tanah yang dapat mempengaruhi kesuburan tanah.Penelitian ini bertujuan untuk membangun suatu model dinamik yang dapat menggambarkan secara holistik pengaruh pengembangan kapas Bollgard pada lingkungan, baik lingkungan alami yang dicerminkan melalui dinamika populasi serangga hama dan mikroba tanah, lingkungan sosial dalam hal ini adalah dinamika penduduk dan kehidupan sosial ekonomi penduduk khususnya petani, melalui tingkat kesejahteraan masyarakat yang memperoleh manfaat dari budidaya tanaman kapas, maupun lingkungan buatan berupa ekosistem perkebunan kapas. Penelitian ini juga bertujuan untuk membuat prediksi pengaruh pengembangan tanaman transgenik pada lingkungan melalui simulasi model dinamik.Penelitian dilakukan dengan pendekatan gabungan kualitatif dan kuantitatif. Metode yang digunakan adalah metode system dynamics. Pelaksanaan penelitian dilakukan melalui tahap: (1) desk study, untuk mengkaji hasil-hasil penelitian sebelumnya, (2) tahap deskriptif analitik dengan metode survei, dan (3) pembuatan model.Berdasarkan hasil penelitian diketahui bahwa diagram simpal kausal yang menyusun model pengaruh pengembangan kapas transgenik pada lingkungan membentuk empat simpal positif (reinforcing loop) dan empat simpal negatif (balancing loop). Pada subsistem penduduk bekerja satu simpal positif dan satu simpal negatif. Pada subsistem produksi kapas terbentuk duo simpal positif dan dua simpal negatif sedangkan pada subsistem serangga hama terbentuk satu simpal positif dan satu simpal negatif.Simulasi yang dilakukan pada model dinamik pengaruh pengembangan kapas transgenik pada lingkungan menyimpulkan bahwa pengembangan kapas transgenik Bollgard menunjukkan adanya dampak pada penurunan populasi serangga hama. Berdasarkan prediksi, populasi serangga hama akan meningkat kembali sejalan dengan timbulnya resistensi serangga hama terhadap protein crylAc yang dihasilkan tanaman kapas Bollgard. Jumlah total mikroba tanah berkurang akibat protein crylAc, dan diprediksi berkurangnya mikroba tanah dapat mengurangi tingkat kesuburan tanah. Penelitian ini juga menyimpulkan bahwa pengembangan kapas transgenik menunjukkan adanya pengaruh pada tingkat kesejahteraan petani.Berdasarkan hasil penelitian tersebut, beberapa upaya yang disarankan antara lain: menerapkan teknik budidaya yang tepat dengan mengurangi penggunaan herbisida dan pupuk kimia untuk mengatasi berkurangnya mikroba tanah yang dapat mempengaruhi kesuburan tanah. Pengendalian serangga hama yang dapat mengganggu keseimbangan ekosistem dan stabilitas produksi dengan pengelolaan resistensi hama melalui penerapan strategi refugia. Selain itu, perlu dilakukan pengkajian lebih lanjut mengenai dampak tanaman transgenik pada komponen tanah lain yang ikut menentukan kesuburan lahan, seperti komponen fisik tanah, kimia tanah, serta bahan organik tanah.

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The development of transgenic cotton is performed to fulfill cotton demand by Indonesian textile industries at the amount of 464.000 ton per year. Indonesia's production supply only 2% of local demand, while the rest is imported.

The low cotton productivity in Indonesia is influenced by climate condition, cultivation technology, the availability of high quality seed stock, and pest attack. The effect from those factors will inhibit plant's growth, which resulted on the low cotton productivity.

The transgenic Bollgard cotton is produced by genetic engineering using DNA recombinant techniques. Bt gene transferred to cotton plant cell can effectively control H. Amigera cotton's main. Development of this transgenic cotton is expected increase cotton plant productivity.

Research on the impact of transgenic Bollgard cotton cultivation to the environment should be done due to the possibility that crylAc protein produced by Bt which is inserted to Bollgard cotton can possibly transferred to other plant and then influence either the non-target insect or the number of soil microorganism and has the effect to soil fertility.

The objective of this research is to build a dynamic model that can describe holistically the impact of developing Bollgard cotton to the environment, either natural environment indicate by the dynamics of pest population and soil microorganism, social environment indicate by the dynamics of population and socio-economic aspect mainly farmer with the prosperity level who get the benefit of cotton cultivated, or man-made environment indicate by cotton field eco-system. The other objective research is to predict the impact of developing transgenic plant to the environment by means of system dynamics model simulation.

The research is used the combination of qualitative and quantitative approaches and System Dynamics method. The research is divided into 3 phases: (1) desk study to review and study the previous research (2) descriptive analyses, done by survey method, and (3) build a dynamics model.

The research finds that the causal loop diagram created to study the impact of transgenic cotton to the environment forms 4 positive loops (reinforcing loops) and 4 negative loops (balancing loops). In population subsystem, there are 1 reinforcing loop and 1 balancing loop. In cotton production subsystem, there are 2 reinforcing loops and 2 balancing loops, and pest insect subsystem formed 1 reinforcing loop and 1 balancing loop.

Based on the simulation of the dynamics model on the impact of development, of transgenic cotton to the environment, it is concluded that there is an impact to the decrease of pest insect population. It is predicted that, insect pest population will increase along with the increasing resistance of the pest to crylAc protein produced by Boligard cotton plant. The number of total soil microorganism will decrease due to the presence of crylAc protein and is predicted to decrease the soil fertility index. This research finds that there is an impact to the farmer's income from the cultivation of transgenic cotton.

It is suggested to implement the suitable cultivation technique to resolve the decreasing number of soil microorganism that affect to soil fertility, the effects of applying refugee strategy to control pest insect population. Further researches concerning the impact of transgenic plant to another soil component which would be influenced soil fertility and plant productivity should be done."

"Pemerintah telah melaksanakan kegiatan pembangunan Sarana air Bersih dan Sanitasi Lingkungan sejak Pelita I sampai sekarang. Menurut laporan dari Bank Dunia dengan mengunakan data SUSENAS 2004, baru 48% penduduk terlayani air bersih, di mana untuk daerah perkotaan 42% dari jumlah penduduk perkotaan dan daerah perdesaan 51% dari jumlah penduduk perdesaan. Dalam laporan tersebut disebutkan selama 8 tahun dari tahun 1994 sampai tahun 2002, peningkatan cakupan air bersih hanya 10% di pedesaan dan 9% di daerah perkotaan. Selain itu sebanyak 40% penduduk perdesaan buang air besar tidak pada tempatnya yaitu di kebon, kolam, danau, sungai dan laut. Hal menyebabkan angka penyakit diare yang masih cukup tinggi yaitu 280/1000 penduduk dan menempati urutan ke 3 penyebab kematian pada bayi, urutan ke 2 pada balita dan nomor 5 pada semua umur, dan sering timbul dalam bentuk kejadian luar biasa (KLB) dengan kematian cukup tinggi. Rendahnya cakupan sarana air bersih dan sanitasi lingkungan disebabkan karena prioritas pemerintah dalam pembangunan sarana air bersih dan sanitasi lingkungan bukan prioritas utama. Oleh sebab itu, Bank Dunia telah memberikan pinjaman untuk pembangunan sarana air bersih dan sanitasi lingkungan melalui proyek WSLIC-2.Penelitian ini bertujuan untuk mengetahuan keberhasilan proyek WSLIC-2 khususnya dalam peningkatan derajat kesehatan masyarakat melalui penurunan kejadian diare pada balita dan mengetahui faktor-faktor yang mempengaruhi kejadian diare serta menentukan faktor-faktor yang paling dominan. Penelitian ini merupakan penelitian survei (non experimental). Teknik penelitian mengunakan kuesioner dengan responden ibu rumah tangga yang mempunyai anak balita. Desa yang disurvei adalah desa yang telah dibangun Sarana air bersih dan sanitasi lingkungan dan desa yang belum dibangun sebagai desa kontrol. Untuk menententukan desa kontrol dengan dicari desa yang hampir sama kondisinya yaitu dari segi geografinya, tingkat sosial ekonomi dan perilakunya masyarakat dengan desa yang telah dibangun. Penggunaan desa kontrol adalah untuk mengetahui kondisi awal sebelum desa dibangun. Analisis yang digunakan menggunakan analisa Statistik dengan mengunakan Program SPSS.Hasil penelitian adalah: terdapat penurunan angka kejadian diare pada balita setelah pembangunan sarana air bersih dan sanitasi lingkungan di desa penelitian, hal ini ditunjukan dengan membandingkan antara desa kontrol (Desa Klampok) yang belum terbangun sarana sebanyak 28 kejadian kejadian diare dengan desa yang telah dibangun sarana yaitu Desa Jambearjo sebanyak 13 kejadian. Apabila dihidung secara rata-rata pada semua umur penduduk didaerah penelitian dapat menurunkan kejadian diare pada setiap 1000 penduduk dari 154 kejadian menurun menjadi 90 kejadian diare.Penurunan kejadian diare pada balita diduga oleh ketersediaan air bersih, sarana untuk membuang air besar, perilaku mencuci tangan setelah buang air besar, mencuci tangan setelah membersihkan balita buang air besar, buang tinja bayi, membuang sampah dan pengetahuan kesehatan lingkungan. Sedangkan varibel yang paling dominan yang berhubungan dengan kejadiaan diare yaitu sarana membuang air besar dan mencuci tangan setelah membersihkan balita dari buang air besar. Secara bersama-sama kedua varibel tersebut sating berinteraksi dengan nilai p = 0,028 dan OR = 7,11. Persamaan regresi logistik Y (kejadian diare pada balita) = -0,241 + 1,962 kondisi jamban x cuci tangan setelah membersihkan balita buang air besar.Dalam penelitian penulis menyarankan agar pemerintah daerah untuk mengurangi kejadian diare pada desa lain yang tidak masuk dalam daftar yang akan dibangun dad proyek WSLIC-2 dapat mereplikasi pendekatan proyek WSL1C-2 dengan lebih memperhatikan pembangunan sarana membuang air besar berupa pembangunan jamban dan mendorong perubahan perilaku hidup bersih terutama dalam cuci tangan dengan membuang sampah dengan cara lebih mengentensifkan pelatihan dan penyuluhan dibidang kesehatan lingkungan.

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The implementation of Water Supply and Environment Sanitation (WSES) from Pelita I to day is currently only 48 percent of the population has access to water That includes 42 percent of the urban and 51 percent of the rural population. In the 8 years from 1994 to 2002, this figure increase by only 10 percent in rural areas and 9 percent in the urban. However, more than 40 percent of rural households use unsanitary open pits or defecate in fields/beaches/water bodies. These caused the incident diarrhea is still height 280/1000 of population. Diarrhea has rank 3 to be caused baby die, and rank 2 of children under five finally rank 5 in all of age.

National development initiative prioritize infrastructure of WSES were lower in priority and remain limited, WSES service coverage therefore remained limited and WSES development was unable with population increase. Therefore, World Bank proposed loan to develop water supply and sanitation facilities in rural areas through WSLIC-2 project.

Research will explore the factors correlate with incident diarrhea for children under five and how the WSLIC-2 project can reduce number of incident diarrhea. The research method used questioner to housewife, They have children under five. The research was two villages, one village developed water supply and sanitation facilities under WSLIC-2 project and other village undeveloped as village control, The characteristic of geography, social-economic and health behavior of two villages are almost same with the other. The village control will be used to kwon characteristic condition without project WSLIC-2.

The conclusion of the research is decrease of number of incident diarrhea in the village with project WSLIC-2 from 28 to 13 incident diarrhea or if we use average of 1000 people, number of incident diarrhea decrease from I54 to 90 incident diarrhea. This figures come from number incident diarrhea in village (Jambearjo) under WSLIC-2 project and village (Klampok) without project WSLIC-2 project. There are multiple factors are suspected with incident diarrhea. These factors are lack of water supply, latrine facility, solid waste facility, hand washing (after defecate and after defecate children under five years, throw away excreta of children under five and knowledge of environmental sanitation and the main factors are latrine facility and hand washing after defecate children under five years. Two variables are interaction, with p value is 0,028 and odd ratio = 7,11. Logistic Regression is Y (incident diarrhea of children under five years) - -0,241 + 1,962 latrine facility x hand washing after defecate children under five years.

Some recommendation to address this issue are: (a) local government can replicate WSLIC-2 project with local budged (b) encourage to communities build latrine by they self (c) Improving health behavior by improving hygiene sanitation training."

"Pulau kecil merupakan pulau yang memiliki keanekaragaman yang spesifik, sumberdaya aiam yang terbatas dangan masyarakat yang memiliki karakteristik sosial budaya yang beradaptasi dengan kehidupan pulau. Ekosistem kapulauan memiliki karakteristik adanya keterbataaan daya dukung Iingkungan baik lahan maupun air sebagai kebutuhan dasar.Pulau Panggang merupakan pulau dengan Iuas 9 Ha, pada tahun 2001 dihuni oleh 3.275 jiwa dengan kepadatan 364 jiwa/ha adalah melebihi kepadatan kota Jakarta (144 jiwa/ha). Kepadatan penduduk, di pulau kecil akan mengakibatkan terjadinya tekanan tarhadap Iingkungan dan berdampak pada penurunan sumberdaya pulau. Air bersih akan semakin langka dan mahal yang pada akhimya akan membebani perekonomian masyarakat pulau. Untuk mengatasi masalah tekanan penduduk terhadap sumberdaya air maka di pulau kecil harus dilakukan pengelolaan air bersih dengan tujuan untuk mempertahankan ketersadiaan air bersih yang dapat dimanfaatkan oleh penduduk pulau.Pangelolaan air bersih di Pulau Panggang menjadi masalah penting karena keterbatasan sumber air bersih dan kemampuan masyarakat untuk membayar. Hingga saat ini penduduk Pulau Panggang memanfaatkan air bersih dari air hujan yang ditampung daiam tangki/bak penampungan. Penurunan kualitas Iingkungan dapat teridentifikasi dan penurunan kuantitas dan kualitas air sumur dangkal yang telah tercemar oleh Iimbah rumah tangga dan air laut.Tujuan penelitian adalah untuk mengidentifikasi faktor-faktor yang menyebabkan belum dilakukan pengelolaan air bersih secara Iestari, membuat model pengelolaan air bersih secara Iestari dan mengidentifikasi faktor-faktor yang akan berpengaruh terhadap keberhasilan pengelolaan air bersih secara lestari. Hipotesis yang diajukan dalam penelitian adalah: Bila curah hujan total Iebih besar atau sama dengan jumlah kebutuhan air bersih penduduk puiau kecil, dengan melakukan pengelolaan air bersih secara Iestari maka kebutuhan air bersih penduduk dapat terpenuhi dan air hujan (air hujan dan air tanah dangkal).Peneiitian ini bersifat deskriptif dengan pendekatan kualitatif dan kuantitatif. Metode penelitian yang digunakan adalah ex post facto dan survei. Pengambilan sampel untuk kuesioner dilakukan dengan metode simple random sampling, dan kualitas air ditentukan berdasarkan uji fisik, kimia, dan bakteri coli.Berdasarkan hasil penelitian diketahui kebutuhan air bersih penduduk Pulau Panggang sebanyak 70 Iiter/orang/hari atau sebanyak 6.877,5 m3/bulan. Jumlah curah hujan rata-rata yang jatuh di wilayah Kepulauan Seribu sebanyak 127,5 mm/bulan atau 11.473,5 m3/bulan. Air Iarian sebanyak 3.442,05 m3/buIan. Neraca air di Pulau Panggang dengan laju pertambahan penduduk 1,8%/tahun maka hingga tahun 2026 akan terjadi surplus air bersih, dan pada tahun 2027 akan terjadi defisit air bersih.Penerapan teknologi RO di Pulau Panggang di nilai tidak Iestari karena, tujuan pembangunan RO hanya untuk memenuhi kebutuhan air minum sebesar 8 Iiter/jiwa/hari. Kebiasaan masyarakat adalah mengkonsumsi air hujan sehingga pada musim hujan penduduk Pulau Panggang tidak memanfaatkan air RO sehingga akan menjadi beban pemerintah dalam mengoperasikan unit pengolahan air bersih tersebut.Berdasarkan hasil penelitian disimpulkan di Pulau Panggang belum dilakukan pengelolaan air bersih secara Iestari, disebabkan:1). Pengelolaan air bersih masih bersifat sektoral oleh antar instansi.2). Belum adanya konsep -pengelolaan air bersih dengan biaya murah sehingga tidak membebani anggaran pemerintah atau sesuai dengan tingkat ekonomi penduduk pulau Panggang.3). Keterbatasan sumberdaya manusia dan sumber ekonomi masyarakat Pulau Panggang.Untuk mengatasi masalah kebutuhan air bersih di Pulau Panggang harus melakukan pengelolaan air bersih secara Iestari, meliputi:1). Teknologi tepat guna Teknologi pengelolaan air bersih yang diterapkan dengan berdasarkan pada sifat dan fungsi Iingkungan alami pulau, dapat diterapkan dan sesuai dengan Iingkungan binaan dan lingkungan sosiai. Teknologi yang digunakan dapat dilaksanakan oleh masyarakat dan memberikan manfaat sesuai tujuan pengelolaan air bersih.2). Pengelolaan kuantitas air bersih, yaitu untuk meningkatkan jumlah relatif air bersih terhadap jumlah penduduk. Meliputi:a). Pemanenan air hujan, yaitu melakukan penangkapan air hujan dari atap dan ditampung dalam tangki/bak penampungan. Tempat penampungan air hujan harus dimiliki oleh setiap rumah dan di dalamnya dapat diberikan treatment sehingga air yang masuk ke dalam tangki tidak tercemar oleh pencemar yang ada pada Iingkungan dan dapat menambah mineral yang dibutuhkan oleh manusia.b). Penataan ruang dan mengatasi masalah kepadatan jumlah penduduk, melakukan penghijauan pada daratan pantai yang sesuai dengan Iingkungan pulau.c). Hemat dalam memanfaatkan air bersih.3). Pengelolaan kualitas air bersih.Bertujuan untuk mencegah bahan pencemar masuk ke dalam air bersih, baik yang ada dalam penampungan atau yang tersimpan sebagai air tanah dangkal. Pengeloaan kualitas air bersih dapat dilakukan dengan: perbaikan sanitasi dan pengendalian pengambilan air tanah.Hal berpengaruh terhadap keberhasilan pengelolaan air bersih secara lestari adalah:1). Adanya konsep pengelolaan air bersih secara Iestari dengan menyesuaikan dengan sifat Iingkungan alam, Iingkungan binaan dan Iingkungan sosial.2). Adanya koordinasi antara dinas terkait dalam melakukan kegiatan pengelolaan air bersih.3). Melibatkan masyarakat dalam pengelolaan air bersih secara lestari.4). Sosialisasi pengelolaan air bersih secara menerus sehingga pengelolaan air bersih secara lestari dapat menjadi salah satu bagian dari aktivitas kehidupan penduduk pulau.

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Small islands are islands that possess spesific diversity, limited natural resources with its people having social and cultural characteristics that adapts to the archipelago life. The island ecosystem has the characteristic of the limited environment condition to support their basic needs, both land and water.Panggang is an island with an area of 9 Ha. ln 2001, 3.275 people live here and its density population of 364 people/Ha outnumbered the density population of Jakarta (144 people/Ha). Such a high population in a small island can cause pressures on the environment and contribute to the deterioration of the island?s natural resources. Clean water will become rare and unaffordable and therefore burden the economic of the local community. To overcome the problem of the people?s pressures toward water resources, a management of clean water has to be conducted in the purpose of preserving the clean water supply that is useful for the local community.Clean water management has become an important issue on Panggang lsland because of the limited resources of clean water and the people?s lacking ability to pay for it. The people on Panggang Island have been using clean water that comes from rain, which is restored in reservoir. The environment quality deterioration can be identified from the decreasing quantity and quality of the land water, which has been contaminated by house waste pollution and seawater.The objectives of this research are for identification some factors which causes there is no sustainability of clean water management; for create a sustainability of clean water management model; and for identitication. which factors that, can causes this sustainability of clean water management to be succeed.The proposed hypothesis in this research is: When total rainfall is bigger than or is the same as total of clean water that people need on small island, with a sustainability of clean water management, the need of clean water of those people can be fulfilled by using water from rainwater (rain and shallow groundwater).This research is descriptive with a qualitative and quantitative approach. The research method used is ex-post facto and survey. The sampling for the questionnaire is completed by using the simple random sampling, and the water quality is determined from its physical and chemical test and also we do on colli bacteria test.Based on the result of this research, it is known that the need of clean water of the people on Panggang Island is 70 Iiter/people/day or approximately 6.877,5 m3/month. The amount of the rainfalls in Kepulauan Seribu area is approximately 127,5 mm/month or 11.473, 5 m3/month. The water flow is 3.442,06 m3/month. Based on the clean water scales in Panggang island and 1,8%/year the people rapid population growth, it is assumed that there will be a surplus of clean water in 2026, and will be a deficit in 2027.The use of the reverse osmosis technology on Panggang island is considered because the purpose ofthe reverse osmosis enstabilishment is merely to fulfill the need of clean water for 8 liter/people/day. The people usually consume rainwater, therefore in the rainy seasons the Panggang lsland?s local communities do not use the osmosis-reversed water, and this becomes a burden for local govemment in operating the clean water management.Based on the result of this research, it can be concluded that in Panggang Island, the clean water management has not been yet conducted in a sustainable way. This is caused by :1). The clean water management on small islands is still sectional and conducted merely by certain institutions.2). There has not been a concept of clean water management with a small budget that does not burden the local govemmenfs fiscal year, nor that suites the economy level of the Panggang Island community.3). The limit of human resources and financial sources for Panggang lsland's community.To overcome problem of clean water necessity in Panggang island, a sustainable management of clean water must be conducted. this includes :1). Efficacious technology.The technology of clean water management, which is used based on the characters and functions of the natural environment, shall be accepted and also be suited in the developed and social environment. So it can be conducted by the community and thus give advantages adjusted to the purpose of the clean water management2). The clean water quantity management, is to increase the relative amount of clean water toward the people which includes :a). Rain water harvesting, is to seize rainwater from roofs and restore them in the reservoir. Every house has to have a reservoir for rain water. They can give treatment inside of the tank to prevent water that fall into the reservoir from being contaminated by environmental contamination and to add minerals needed by human.b). Reforestation the whole island and solving the population problem, planting on the coastline that is suitable with the island's environmentc). Economizing the clean water.3). Clean water quality managementThe purpose of the clean water quality management is to prevent clean water, which is restored in the reservoir and in around shallow water, from being contaminated by environmental contamination. The clean water quality management could e conducted with repairing the sanitary equipments and controlling the the ground extraction.Things that give contributions to the successfulness of a sustainable clean water management of clean water are :1). The concept of clean water management by adjusting to the natural environment characters as well as to the developed and social environment.2). An obligation to have a good social coordination between the relative institutions in conducting the activities of the clean water management.3). Including the people in managing the clean water in sustainable way.4). A continous socialization of the clean water management in order to make it as one of the activities that becomes a habit ofthe people in doing their activities."

"Perubaban laban berdampak pada perubaban (peningkatan/penurunan) suhu udara permukaan. Tujuan mengetahui kondisi Iahan, pola kecenderungan suhu udara. Menganalisis kekuatan korelasi perubaban laban dengan perubaban suhu udara permukaan dan besar dampaknya di Kecamatan Cisarua. Metodenya deskriptif, persentase, grafik trendline dengan If tertinggi, analisis statistik r, dan koefisien determinasi If. Kondisi lahan Kecamatan Cisarua: bukan hutan 5398 Ha dan hutan seluas 974 Ha. Suhu rata-rata pukul 07.00 wib turu."l, suhu rata-rata pukul 13.00 wib naik, suhu rata-rata pukul 18.00 wib naik. Kuat korelasi laban hutan dengan suhu rata-rata pukul 13.00 adalah -0,535, laban bukan hutan dengan suhu rata-rata pukul13.00 adalah 0,537, laban hutan dengan suhu rata pukull8.00 wib adalah -0,793, dan lahan bukan hutan dengan suhu rata-rata pukul 18.00 wib adalah 0,785. Besar dampak perubahan lahan pada suhu rata-rata pukul 13.00 adalah 44% dan pada suhu rata-rata pukull8.00 wib adalah 81%. Kondisi lahan Kecamatan Cisarua tahun 2009: bukan hutan 5398 Ha dan hutan 974 Ha. Suhu rata-rata pukul 07.00 wib turun, suhu rata-rata pukul 13.00 wib naik, dan suhu rata-rata pukul 18.00 naik. Kekuatan korelasi lahan hutan dengan suhu rata-rata pukul 13.00 wib adalah -0,535, laban bukan hutan dengan suhu rata-rata pukul 13.00 wib adalah 0,537, laban hutan dengan suhu rata-rata pukul 18.00 wib adalah -0,793, laban bukan hutan dengan suhu rata:rata pukul 18.00 wib adalah 0,785. Besar dampak perubaban lahan pada suhu rata-rata pukul13.00 wib adalah 44% dan pada suhu rata-rata pukul18.00 wib sebesar 81%. Perlu dicermati setiap penurunan lahan hutan, penghijauan, dipertahankan dan diciptakan hutan kota, pelaksanaan permen tentang penataan ruang, perda tentang penata ruang yang ketat, dan ketat dalam pemberian IMB

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The aim of this research is to learn about land condition and the trend of temperature change. It is carried out by analyzing the correlation strength between the conversion in land use and temperature change as well as its impact. The applied method is descriptive in nature using percentage, trend line graphs, statistical analysis and determination coefficient or k. The subject of this research is the area in the sub-district of Cisarua consisting of 5398 hectares of non-forest vegetation and 974 hectares of forest vegetation. The research shows that the average temperature at 07:00 am is decreasing and whilst the average temperature at 0l:00 pm is increasing and the average temperature at 06:00 pm is increasing. The correlation strength of forest vegetation with the average temperature at 01:00pm is -0.535 while the same measurement taken for non-forest vegetation shows correlation strength of 0.537. At 06:00 pm the correlation strength between forest vegetation and the average temperature is 0.793 meanwhile the correlation strength between for non-forest vegetation is 0.785. The impact of land conversion at the average temperature at 01:00pm is 44% and atthe average temperature at 01:00pm is 81%. Bearing in mind the impact caused by the decreasing forest vegetation it is advisable that the regional government of Bogor as well as the government apparatus of the sub-district of Cisarua and the entire community to be more alert on the ever decreasing area of forest vegetation and to implement a reforestation policy, to encourage the creation and maintenance of city-forest and implementing of the Minister's Decree on Spatial Planning, to push for a regional regulation on spatial management and to be stricter in releasing building permit."

"ABSTRAKWilayah pesisir Jakarta Utara terancam bencana akibat fenomena kenaikan muka air laut dan penurunan permukaan tanah. Dampak kerusakan yang ditimbulkan dari kedua fenomena ini sangat merugikan bagi masyarakat di wilayah tersebut. Tujuan penelitian adalah menganalisis kerentanan wilayah pesisir dan memprediksi kerusakan lingkungan akibat kenaikan muka air laut di Jakarta Utara. Informasi kerentanan adalah hasil integrasi kondisi fisik (informasi pasang surut, gelombang, penggunaan lahan, ketinggian pantai, skenario B2 SRES IPCC, penurunan permukaan tanah) dengan sosial ekonomi (usia balita, usia lanjut, penduduk wanita, kepadatan penduduk, dan penduduk miskin) dengan menggunakan Sistem Informasi Geografi (SIG). Penelitian menggunakan data QuickBird dan DEM SRTM X-C band tahun 2000 untuk menghasilkan informasi penggunaan lahan dan ketinggian pantai. Hasil integrasi menunjukkan willayah pesisir yang sangat rentan pada kenaikan muka air laut adalah Penjaringan, Warakas, Kalibaru, Kebon Bawang, dan Rawabadak Utara. Prediksi total kenaikan muka air laut hingga tahun 2030 mencapai 6,45 m sehingga diprediksikan 1054 ha pemukiman, 551 ha industri, 181 ha tambak, dan 66 ha lahan sawah akan tergenang dan menyebabkan kerugian ekonomi mencapai Rp 277.270.766.595,00. Diketahuinya tingkat kerentanan serta prediksi kerugian akibat kenaikan muka air laut, diharapkan perencanaan pembangunan di wilayah pesisir akan lebih memperhatikan hal tersebut.

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ABSTRACTThe coastal areas in North Jakarta threatened disaster due to sea level rise and land subsidance phenomenon. The aims of this study is to analyze the coastal vulnerability due to sea level rise as part as adaptation to reduce the inundation impact in North Jakarta. Vulnerability information obtained from the integration between the physical conditions (tidal, wave, land use, coastal elevation, IPCC SRES B2 scenario, land subsidence) and socioeconomic (age of the children, elderly, female population, population density, and the poor) using Geographic Information System (GIS). This study using remote sensing information from DEM SRTM X-C band in year 2000 with spasial resolution 30 m to generate coastal elevation and QuickBird satellite data for generate land use information. The result show that the coastal areas with very high vulnerability to sea level rise is Penjaringan, Warakas, Kalibaru, Kebon Bawang, and Rawabadak Utara. Besides vulnerability analysis, the study also predicted total sea level rise in 2030 which reached 6.45 m, causing a lot of damage, especially in the settlement and industrial areas. The prediction of settlement areas that stagnant is 1054 ha, industrial 551 ha, fishpond 181 ha, and field 66 ha. According to economic analyze, the extent damage will cause losses of Rp 277,270,766,595.00. Therefore, the knowledge level of vulnerability as well as losses due to sea level rise, expected development planning in coastal areas will pay more attention to it."

"ABSTRAKTesis ini membahas pemanfaatan tanaman eceng gondok (Eichhornia crassipes (Mart.) Solms.) dalam pengolahan limbah cair sekolah. Penelitian ini bertujuan untuk menganalisis karakteristik limbah cair yang dihasilkan sekolah dan efektivitas pengolahannya dengan bantuan tanaman. Parameter yang digunakan untuk menentukan efektivitas pengolahan limbah adalah BOD, TSS, pH, serta minyak dan lemak berdasarkan KepMen LH No. 112 tahun 2003. Hasil penelitian menunjukkan bahwa belum dilakukan pengolahan limbah cair oleh sekolah. Limbah cair yang dihasilkan oleh sekolah sebelum pengolahan melebihi baku mutu untuk parameter BOD5 dan TSS. Limbah cair yang dihasilkan oleh sekolah setelah pengolahan secara biologi menggunakan tanaman eceng gondok kualitasnya mengalami penurunan dan tidak melebihi baku mutu. Fitoremediasi efektif meningkatkan kualitas limbah cair sekolah hingga berada di bawah baku mutu dengan penurunan TSS hingga 96%, kenaikan pH hingga 14 %, dan penurunan BOD5 hingga 91%. Perlakuan paling efektif dalam pengolahan limbah cair dengan eceng gondok adalah dengan 6 daun selama 12 hari.

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ABSTRACTThe focus of this thesis is to discusses the use of water hyacinth plants (Eichhornia crassipes(Mart.) Solms.) in wastewater treatment produced by a school. The aim of the study is to analyze the characteristics of the wastewater produced by the school and the effectiveness of phytoremediation process. The parameters used to determine the effectiveness of wastewater treatment is BOD, TSS, pH, and oil and grease based KepMen No. LH. 112 of 2003. The results showed that the treatment has not been done by school. Liquid waste generated by the school prior to processing exceeds the quality standards for parameters BOD5 and TSS. Liquid waste generated by the school after the biological treatment using water hyacinth plant quality declined and did not exceed the standard. Phytoremediation effectively improve the quality of wastewater from school below the standards by up to 96% removal of TSS, pH increase up to 14%, and 91% removal of BOD5. The most effective treatment in this research is the tratment of water hyacinth with 6 leaves for 12 days."

"[Ekosistem perairan tawar, seperti sungai sebagai penyangga dari aktivitas antropogenik. Manusia sebagai elemen utama memiliki kewajiban untuk menjaga kualitas sungai, baik sebagai masyarakat ataupun pemerintah. Limbah domestik dari aktivitas manusia, seperti limbah deterjen dan fecal coliform telah melebihi daya tampung dan daya dukung perairan. Sehingga berdampak pada degradasi lingkungan. Kebijakan hukum lingkungan hidup dapat menjadi batasan untuk aktivitas manusia yang menggunakan bantaran sungai, tetapi dalam penerapannya masih terdapat kesenjangan antara masyarakat, pemerintah, dan produk hukum. Atas dasar deskripsi tersebut, tujuan dari penelitian ini adalah untuk menganalisis status mutu air yang ditetapkan dalam Keputusan Menteri Lingkungan Hidup No. 115 tahun 2003 dan meramalkan kebijakan lingkungan hidup dengan rencana skenario kebijakan yang akan datang. Studi kasus dilakukan di bantaran Sungai Cipinang dengan metode bola salju. Nilai mutu air Sungai Cipinang adalah -134 dengan status tercemar berat. Rencana skenario kebijakan lingkungan hidup menghasilkan empat macam narasi. Narasi satu adalah kondisi ideal, narasi dua adalah keterkaitan antara nilai masyarakat terhadap lingkungan, narasi tiga adalah kerusakan sumber daya alam bersama, dan narasi empat adalah tidak terlaksananya peraturan., River is one of the freshwater aquatic ecosystem. The function of river as a buffer for human activity. Humans as a major element have an obligation to maintain the water quality of river, either as a society or government. Domestic waste from human activities, such as detergent and fecal coliform have been exceeded of carrying capacity. It can impact to environmental degradation and river become damage. Policy of environmental’s law, may be limit to human activities, but in practice, there is still gap between society, government, and legal products. Based on the description, the purposes of this study are, to analyze the status of water quality based on the decree of the Minister Environment No. 115 in 2003, community participation, and predict the environmental policy with scenario. Case studies conducted in Cipinang’s river with the snowball method. The value of water quality is -134, and the status are heavily polluted. Scenario planning for environmental’s policy have four scenarios. First scenario is an ideal condition, second is relationship between the communities values and environmental, third is tragedy of the commons, and fourth is not implemented of regulations.]"

"[ABSTRAKAnalisis Risiko Kesehatan Lingkungan Akibat Pembuangan Limbah CairPembangkit Listrik Tenaga Panas Bumi (PLTP) Ulumbu ke Sungai (Pada LapanganPanas Bumi Ulumbu, Kabupaten Manggarai, Nusa Tenggara Timur)Pembangkit Listrik Tenaga Panas Bumi (PLTP) merupakan salah satu sumberenergi yang ramah lingkungan karena menghasilkan volume limbah yang rendah,salah satunya adalah limbah cair. Limbah cair panas bumi mengandung unsurkimia, salah satunya adalah Arsen. Limbah cair PLTP akan menimbulkan dampakapabila dibuang secara langsung ke sungai. Tujuan penelitian ini adalah untukmengidentifikasi besarnya konsentrasi Arsen pada limbah PLTP dan air sungai dilokasi penelitian dan dampaknya terhadap konsentrasi Arsen di sungai serta dampakterhadap kesehatan lingkungan. Dari penelitian ini didapatkan hasil konsentrasiArsen pada limbah PLTP sebesar 0,0365 mg/l. Kandungan Arsen dalam limbahyang dibuang masih berada di bawah baku mutu, yaitu sebesar 0,5 mg/l.Pembuangan limbah cair PLTP ini juga tidak meningkatkan konsentrasi Arsen disungai. Konsentrasi Arsen pada air yang dikonsumsi masyarakat adalah 0,008 mg/l.Perhitungan risiko kesehatan masyarakat yang mengkonsumsi air sungaimenunjukkan tidak menimbulkan risiko kesehatan RQ < 1 (RQ = 0,6522).

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ABSTRACTGeothermal power plant is one of the green energy which produces low wastevolume, including wastewater. Geothermal wastewater contains Arsenic, adangerous chemical. It can generate impact when it is discharged to the rivernearby. The purpose of this research is to identify Arsenic concentration in thegeothermal wastewater and in the river on the research location. The result of thisresearch shows that geothermal wastewater Arsenic concentration is still below theregulation, that is 0,0365 mg/l. Its content in the discarded waterwaste is still belowthe quality standar, which is 0,5 mg/l. Geothermal wastewater discharge has noeffect to the Arsenic concentration in the river. Arsenic concentration in the riverthat people consume is 0,008 mg/l. Based on this concentration, health riskassessment ot the comunity who consume the water from the river shows noharmful potential to cause health problem as the RQ less than 1 (RQ = 0,6522).;Geothermal power plant is one of the green energy which produces low wastevolume, including wastewater. Geothermal wastewater contains Arsenic, adangerous chemical. It can generate impact when it is discharged to the rivernearby. The purpose of this research is to identify Arsenic concentration in thegeothermal wastewater and in the river on the research location. The result of thisresearch shows that geothermal wastewater Arsenic concentration is still below theregulation, that is 0,0365 mg/l. Its content in the discarded waterwaste is still belowthe quality standar, which is 0,5 mg/l. Geothermal wastewater discharge has noeffect to the Arsenic concentration in the river. Arsenic concentration in the riverthat people consume is 0,008 mg/l. Based on this concentration, health riskassessment ot the comunity who consume the water from the river shows noharmful potential to cause health problem as the RQ less than 1 (RQ = 0,6522).;Geothermal power plant is one of the green energy which produces low wastevolume, including wastewater. Geothermal wastewater contains Arsenic, adangerous chemical. It can generate impact when it is discharged to the rivernearby. The purpose of this research is to identify Arsenic concentration in thegeothermal wastewater and in the river on the research location. The result of thisresearch shows that geothermal wastewater Arsenic concentration is still below theregulation, that is 0,0365 mg/l. Its content in the discarded waterwaste is still belowthe quality standar, which is 0,5 mg/l. Geothermal wastewater discharge has noeffect to the Arsenic concentration in the river. Arsenic concentration in the riverthat people consume is 0,008 mg/l. Based on this concentration, health riskassessment ot the comunity who consume the water from the river shows noharmful potential to cause health problem as the RQ less than 1 (RQ = 0,6522).;Geothermal power plant is one of the green energy which produces low wastevolume, including wastewater. Geothermal wastewater contains Arsenic, adangerous chemical. It can generate impact when it is discharged to the rivernearby. The purpose of this research is to identify Arsenic concentration in thegeothermal wastewater and in the river on the research location. The result of thisresearch shows that geothermal wastewater Arsenic concentration is still below theregulation, that is 0,0365 mg/l. Its content in the discarded waterwaste is still belowthe quality standar, which is 0,5 mg/l. Geothermal wastewater discharge has noeffect to the Arsenic concentration in the river. Arsenic concentration in the riverthat people consume is 0,008 mg/l. Based on this concentration, health riskassessment ot the comunity who consume the water from the river shows noharmful potential to cause health problem as the RQ less than 1 (RQ = 0,6522).;Geothermal power plant is one of the green energy which produces low wastevolume, including wastewater. Geothermal wastewater contains Arsenic, adangerous chemical. It can generate impact when it is discharged to the rivernearby. The purpose of this research is to identify Arsenic concentration in thegeothermal wastewater and in the river on the research location. The result of thisresearch shows that geothermal wastewater Arsenic concentration is still below theregulation, that is 0,0365 mg/l. Its content in the discarded waterwaste is still belowthe quality standar, which is 0,5 mg/l. Geothermal wastewater discharge has noeffect to the Arsenic concentration in the river. Arsenic concentration in the riverthat people consume is 0,008 mg/l. Based on this concentration, health riskassessment ot the comunity who consume the water from the river shows noharmful potential to cause health problem as the RQ less than 1 (RQ = 0,6522).;Geothermal power plant is one of the green energy which produces low wastevolume, including wastewater. Geothermal wastewater contains Arsenic, adangerous chemical. It can generate impact when it is discharged to the rivernearby. The purpose of this research is to identify Arsenic concentration in thegeothermal wastewater and in the river on the research location. The result of thisresearch shows that geothermal wastewater Arsenic concentration is still below theregulation, that is 0,0365 mg/l. Its content in the discarded waterwaste is still belowthe quality standar, which is 0,5 mg/l. Geothermal wastewater discharge has noeffect to the Arsenic concentration in the river. Arsenic concentration in the riverthat people consume is 0,008 mg/l. Based on this concentration, health riskassessment ot the comunity who consume the water from the river shows noharmful potential to cause health problem as the RQ less than 1 (RQ = 0,6522).;Geothermal power plant is one of the green energy which produces low wastevolume, including wastewater. Geothermal wastewater contains Arsenic, adangerous chemical. It can generate impact when it is discharged to the rivernearby. The purpose of this research is to identify Arsenic concentration in thegeothermal wastewater and in the river on the research location. The result of thisresearch shows that geothermal wastewater Arsenic concentration is still below theregulation, that is 0,0365 mg/l. Its content in the discarded waterwaste is still belowthe quality standar, which is 0,5 mg/l. Geothermal wastewater discharge has noeffect to the Arsenic concentration in the river. Arsenic concentration in the riverthat people consume is 0,008 mg/l. Based on this concentration, health riskassessment ot the comunity who consume the water from the river shows noharmful potential to cause health problem as the RQ less than 1 (RQ = 0,6522)., Geothermal power plant is one of the green energy which produces low wastevolume, including wastewater. Geothermal wastewater contains Arsenic, adangerous chemical. It can generate impact when it is discharged to the rivernearby. The purpose of this research is to identify Arsenic concentration in thegeothermal wastewater and in the river on the research location. The result of thisresearch shows that geothermal wastewater Arsenic concentration is still below theregulation, that is 0,0365 mg/l. Its content in the discarded waterwaste is still belowthe quality standar, which is 0,5 mg/l. Geothermal wastewater discharge has noeffect to the Arsenic concentration in the river. Arsenic concentration in the riverthat people consume is 0,008 mg/l. Based on this concentration, health riskassessment ot the comunity who consume the water from the river shows noharmful potential to cause health problem as the RQ less than 1 (RQ = 0,6522).]"

"[Riset Kesehatan Dasar tahun 2013 menyebutkan bahwa DKI Jakarta menempati urutan ke tiga provinsi dengan insiden diare tertinggi Kondisi lingkungan yang berubah perilaku hidup tidak sehat serta pencemaran lingkungan meningkatkan kejadian diare padahal kejadian diare dapat diturunkan dengan integrasi pengelolaan lingkungan berkelanjutan serta perilaku hidup sehat Tujuan penelitian ini menganalisis kondisi lingkungan menganalisis perilaku hidup bersih dan sehat dan menganalisis bentuk pengelolaan lingkungan berbasis masyarakat untuk menurunkan kejadian diare pada balita Penelitian ini menggunakan pendekatan kuantitatif pengumpulan data menggunakan kuesioner dan analisis Kondisi lingkungan Kecamatan Koja terkait sanitasi dan tempat tinggal tidak baik Perilaku hidup bersih dan sehat dari responden 34 baik 40 sedang 26 tidak baik Pengelolaan lingkungan yang dapat dilaksanakan untuk menurunkan kejadian diare pada balita adalah integrasi pelaksanaan sanitasi total berbasis masyarakat serta pengelolaan sampah dengan aman.

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Basic Health Research 2013 shows Jakarta is third highest province with diarrhea cases Environmental changes unhealthy behavior and environment pollution increases the incidence of diarrhea whereas the incidence of diarrhea can be reduced by the integration of healthy behavior and sustainable environmental management This research purposes to know environment condition to analyze the clean and healthy living behaviors and analyze the community based environmental management to reduce incidence of diarrhea in infant This study uses a quantitative approach using the questionnaires and control analysis The environment condition regarding the sanitation is not good Clean and healthy living behaviors of the respondent are 34 good 40 moderate 26 poor Environmental management that can be implemented to reduce the incidence of diarrhea in infant is integration of community led total sanitation and save waste management ;ABSTRACTBasic Health Research 2013 shows Jakarta is third highest province with diarrhea cases Environmental changes unhealthy behavior and environment pollution increases the incidence of diarrhea whereas the incidence of diarrhea can be reduced by the integration of healthy behavior and sustainable environmental management This research purposes to know environment condition to analyze the clean and healthy living behaviors and analyze the community based environmental management to reduce incidence of diarrhea in infant This study uses a quantitative approach using the questionnaires and control analysis The environment condition regarding the sanitation is not good Clean and healthy living behaviors of the respondent are 34 good 40 moderate 26 poor Environmental management that can be implemented to reduce the incidence of diarrhea in infant is integration of community led total sanitation and save waste management.;ABSTRACTBasic Health Research 2013 shows Jakarta is third highest province with diarrhea cases Environmental changes unhealthy behavior and environment pollution increases the incidence of diarrhea whereas the incidence of diarrhea can be reduced by the integration of healthy behavior and sustainable environmental management This research purposes to know environment condition to analyze the clean and healthy living behaviors and analyze the community based environmental management to reduce incidence of diarrhea in infant This study uses a quantitative approach using the questionnaires and control analysis The environment condition regarding the sanitation is not good Clean and healthy living behaviors of the respondent are 34 good 40 moderate 26 poor Environmental management that can be implemented to reduce the incidence of diarrhea in infant is integration of community led total sanitation and save waste management , ABSTRACTBasic Health Research 2013 shows Jakarta is third highest province with diarrhea cases Environmental changes unhealthy behavior and environment pollution increases the incidence of diarrhea whereas the incidence of diarrhea can be reduced by the integration of healthy behavior and sustainable environmental management This research purposes to know environment condition to analyze the clean and healthy living behaviors and analyze the community based environmental management to reduce incidence of diarrhea in infant This study uses a quantitative approach using the questionnaires and control analysis The environment condition regarding the sanitation is not good Clean and healthy living behaviors of the respondent are 34 good 40 moderate 26 poor Environmental management that can be implemented to reduce the incidence of diarrhea in infant is integration of community led total sanitation and save waste management ]"