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Journal : Journal of Tropical Soils

Synergism of Wild Grass and Hydrocarbonoclastic Bacteria in Petroleum Biodegradation Gofar, Nuni
JOURNAL OF TROPICAL SOILS Vol 18, No 2: May 2013
Publisher : UNIVERSITY OF LAMPUNG

Show Abstract | Download Original | Original Source | Check in Google Scholar | DOI: 10.5400/jts.2013.v18i2.161-168

Abstract

The concept of plants and microbes utilization for remediation measure of pollutant contaminated soil is the newest development in term of petroleum waste management technique. The research objective was to obtain wild grass types and hydrocarbonoclastic bacteria which are capable to synergize in decreasing petroleum concentration within petroleum contaminated soil. This research was conducted by using randomized completely block design. This research was conducted by using randomized completely block design. The first factor treatments were consisted of without plant, Tridax procumbens grass and Lepironia mucronata grass. The second factor treatments were consisted of without bacterium, single bacterium of Alcaligenes faecalis, single bacterium of Pseudomonas alcaligenes, and mixed bacteria of Alcaligenes faecalis with P. alcaligenes. The results showed that mixed bacteria (A.  faecalis and P. alcaligenes) were capable to increase the crown and roots dry weights of these two grasses, bacteria population, percentage of TPH (total petroleum hydrocarbon) decrease as well as TPH decrease and better pH value than that of single bacterium. The highest TPH decrease with magnitude of 70.1% was obtained on treatment of L. mucronata grass in combination with mixed bacteria.[How to Cite: Gofar N. 2013.Synergism of Wild Grass and Hydrocarbonoclastic Bacteria in Petroleum Biodegradation. J Trop Soils 18 (2): 161-168. Doi: 10.5400/jts.2013.18.2.161][Permalink/DOI: www.dx.doi.org/10.5400/jts.2013.18.2.161]REFERENCESBello YM. 2007. Biodegradation of Lagoma crude oil using pig dung.  Afr J Biotechnol 6: 2821-2825.Gerhardt KE, XD Huang, BR Glick and BM Greenberg. 2009. Phytoremediation and rhizoremediation of organic soil contaminants: Potential and challenges. Plant Sci 176: 20-30.Glick BR. 2010. Using soil bacteria to facilitate phytoremediation.  Biotechnol Adv 28: 367-374. Gofar N. 2011.  Characterization of petroleum hydrocarbon decomposing fungi isolated from mangrove rhizosphere.  J Trop Soils 16(1): 39-45. doi: 10.5400/jts.2011.16.1.39Gofar N. 2012. Aplikasi isolat bakteri hidrokarbonoklastik asal rhizosfer mangrove pada tanah tercemar minyak bumi. J Lahan Suboptimal 1: 123-129 (in Indonesian). Hong WF, IJ Farmayan, CY Dortch, SK Chiang and JL Schnoor. 2001. Environ Sci Technol 35: 1231.Khashayar T and T Mahsa. 2010.  Biodegradation potential of petroleum hydrocarbons by bacterial diversity in soil. Morld App Sci J 8: 750-755.Lal B and S Khanna. 1996. Degradation of Crude Oil by Acinetobacter calcoaceticus and Alcaligenes odorans, J Appl Bacteriol 81: 355- 362.Mackova M, D Dowling and T Macek. 2006. Phytoremediation and rhizoremediation: Theoretical background. Springer, Dordrecht, Netherlands. 300 p. Malik ZA and S Ahmed.  2012. Degradation of petroleum hydrocarbons by oil field isolated bacterial consortium. Afr J Biotechnol 11: 650-658.Mendez MO and RM Maier. 2008. Phytostabilization of mine tailings in arid and semiarid environment an emerging remediation technology. Environ Health Prospect 116: 278-283.Milic JS, VP Beskoski, MV Ilic, SM Ali, GDJ Cvijovic and MM Vrvic.  2009.  Bioremediation of soil heavily contaminated with crude oil and its products: composition of the microbial consortium. J Serb Chem Soc  74: 455-460.Mukre AM, AA Hamid, A Hamzah and WM Yusoff.  2008.  Development of three bacteria consortium for the bioremediation of crude petroleum-oil in contaminated water. J Biol Sci 8: 73-79.Ndimele PE. 2010. A review on the phytioremediation of petroleum hydrocarbon. Pakistan J Biol Sci 12:  715-722.Newman LA and CM Reynolds.  2004.  Phytoremediation of organic compounds. Curr Opin Biotechnol  15: 225-230.Onwuka F, N Nwachoko, and E Anosike. 2012. Determination of total petroleum hydrocarbon (TPH) and some cations (Na+, Ca2+ and Mg2+) in a crude oil polluted soil and possible phytoremediation by Cynodon dactylon L (Bermuda grass). J Environ Earth Sci 2: 12-17.Pezeshki SR, MW Hester, Q Lin and JA Nyman.  2000.  The effect of oil spill and clean-up on dominant US Gulf Coast Marsh Macrophytes: a review.  Environ Pollution 108: 129-139.Pikoli MR, P Aditiawati and DI Astuti. 2000. Isolasi bertahap dan identifikasi isolat bakteri termofilik pendegradasi minyak bumi dari sumur bangko. Laporan Penelitian pada Jurusan Biologi, ITB, Bandung (unpublished, in Indonesian).Pilon-Smits E and JL Freeman. 2006. Environmental cleanup using plants: biotechnological advances and ecological considerations. Front Ecol Environ 4: 203-10. Rahman KSM, JT Rahman, P Lakshmanaperumalsamy, and IM Banat. 2002. Towards efficient crude oil degradation by a mixed bacterial consortium. Bioresource Technol 85: 257-261.Rossiana N.  2004. Oily Sludge Bioremediation with Zeolite and Microorganism and It’s Test with Albizia Plant (Paraserianthes falcataria) L (Nielsen). Laboratory of Environmental Microbiology, Department of Biology Padjadjaran University, Bandung (unpublished).Rossiana, N.  2005.  Penurunan Kandungan Logam Berat dan Pertumbuhan Tanaman Sengon (Paraserianthes falcataria L (Nielsen) Bermikoriza dalam Media Limbah Lumpur Minyak Hasil Ekstraksi. Laboratorium Mikrobiologi dan Biologi Lingkungan Jurusan Biologi Fakultas Matematika dan Ilmu Pengetahuan Alam Universitas Padjajaran, Bandung  (in Indonesian).Sathishkumar M, B Arthur Raj, B Sang-Ho, and Y Sei-Eok. 2008. Biodegradation of crude oil by individual bacterial strains and a mixed bacterial consortium isolated from hydrocarbon contaminated areas clean. Ind J Biotechnol 36: 92-96.Shirdam R, AD Zand, GN Bidhendi and N Mehrdadi.  2008. Phytoremediation of hydrocarbon-contaminated soils with emphasis on effect of petroleum hydrocarbons on the growth of plant species. Phytoprotection 89: 21-29.Singer AC, DE Crowley and IP Thompson.  2003.  Secondary plant metabolites in phytoremediation and biotransformation. Trends Biotechnol 21: 123-130.Singh A and OP Ward. 2004.  Applied Bioremediation and Phytoremediation. Springler, Berlin, 281p.Surtikanti H and W Surakusumah.  2004.  Peranan Tanaman dalam Proses Bioremediasi Oli Bekas dalam Tanah Tercemar.  Ekol Biodivers Trop  2: 48-52 (in Indonesian).Wenzel WW.  2009.  Rhizosphere processes and management in plant-assisted bioremediation (phytoremediation) of soil.  Plant Soil 321: 385-408.Widjajanti H, I Anas, N Gofar and MR Ridho.  2010.  Screening of petroleum hydrocarbons degrading bacteria as a bioremediating agents from mangrove areas. Proceeding of International Seminar, workshop on integrated lowland development and management, pp. C7 1-9.Widjajanti H.  2012. Bioremediasi Minyak Bumi Menggunakan Bakteri dan Kapang Hidrokarbonoklastik dari Kawasan Mangrove Tercemar Minyak Bumi. [Disertasi]. Universitas Sriwijaya (in Indonesian).
Improvement of Sand Tailing Fertility Derived from Post Tin Mining Using Leguminous Crop Applied by Compost and Mineral Soil Dedik Budianta; Nuni Gofar; Gusti Aditya Andika
JOURNAL OF TROPICAL SOILS Vol 18, No 3: September 2013
Publisher : UNIVERSITY OF LAMPUNG

Show Abstract | Download Original | Original Source | Check in Google Scholar | DOI: 10.5400/jts.2013.v18i3.217-223

Abstract

The research was aimed to study the potency of two leguminous cover crops in enhancing tailing fertility of post tin mining with and without addition of mineral soil  and compost. This pot experiment was carried out in Greenhouse of Soil Science Department, Faculty of Agriculture, Sriwijaya University from November 2011 until March 2012. Design experiment used was a Completly Randomized Design (CRD) factorial with two factors. The first factor was type of cover corps which were Centrosema pubescens and Pueraria javanica. The second factor was plant media composition which were 100% sand tailing, 60% sand tailing + 40%  mineral soil, and  95% sand tailing + 5% compost. The result showed that N content on sand tailing after harvesting applied by compost and mineral soil was not significant by difference. Meanwhile, P content on sand tailing applied by compost was higher than mineral soil application and/or control (100% sand tailing).Keywords: Compost, legominous crop, N and P nutrients, sand tailing [How to Cite: Budianta D, N Gofar and GA Andika. 2013. Improvement of Sand Tailing Fertility Derived from Post Tin Mining Using Leguminous Crop Applied by Compost and Mineral Soil. JTrop Soils 18 (3): 217-223. Doi: 10.5400/jts.2013.18.3.217][Permalink/DOI: www.dx.doi.org/10.5400/jts.2013.18.3.93]REFERENCESAng LH. 2002. Problems and Prospecs of Afforestration on Sandy Tin Tailings in Peninsular Malaysia. J Trop Forest Sci 1: 87-105Budianta D, U Harun and R Santi. 2010. Perbaikan Sandy Tailing Asal Lahan Pasca Penambangan Timah dengan Kompos untuk Pertumbuhan Nilam. Prosiding Seminar Nasional, Masyarakat Konservasi Tanah dan Air Indonesia: 235-255, Jambi (in Indonesian).Djunaedi EK and F Djabar. 2003. Pemantauan dan Evaluasi Konservasi Sumber Daya Mineral di Daerah Bukit Sunur, Kabupaten Bengkulu Utara Provinsi Bengkulu. Kolokium Hasil Kegiatan Inventarisasi Sumber Daya Mineral – DIM, TA. 2003 (in Indonesian).Hakim N, MY Nyakpa, AM Lubis, SG Nugroho, MR. Saul, M A  Diha, G B  Hong and H H  Bailey. 1986. Dasar–Dasar Ilmu Tanah. Penerbit Universitas Lampung, Lampung (in Indonesian).Juhaeti N, N Hidayati, F Syarif and S Hidayat. 2009. Uji potensi tumbuhan akumulator merkuri untuk fitoremediasi lingkungan tercemar akibat kegiatan penambangan emas tanpa izin (PETI) di Kampung Leuwi Bolang, Desa Bantar Karet, Kecamatan Nanggung, Bogor. Berita Biologi 9: 529-538 (in Indonesian).Kasno A. 2009. Peranan Bahan Organik terhadap Kesuburan Tanah. Informasi Ringkas Bank Pengetahuan Padi Indonesia. Balai Penelitian Tanah, Bogor (in Indonesian).Mokhtaruddin A M and M Norhayati. 1995. Modification of Soil Structure of Sand Tailings: I. Preliminary Study on the Effect of Organic Amandment and Iron on Soil Aggregation. Pertanka J Trop Agric Sci 18: 85-88.Mustikarini E D, T Lestari, U Widyastuti and Suharsono. 2010. Konsentrasi Pb, Cu, dan Sn pada buah aksesi nenas lokal Bangka yang dibudidayakan di lahan pasca penambangan timah Bangka. Prosiding Seminar Naional, Masyarakat Konservasi Tanah dan Air Indonesia: pp. 293-301, Jambi (in Indonesian).Purwantari ND. 2007. Reklamasi area tailing di pertambangan dengan tanaman pakan ternak, mungkinkah?. Wartazoa  17: 101-108 (in Indonesian).Pusat Penelitian Tanah.  1983. Term of Refernce Type-A Proyek Penelitian Pertanian menunjang Transmigrasi (P3MT). Departemen Pertanian. Badan Penelitian dan Pengembangan Pertanian. Bogor (in Indonesian). Rahyunah W. 2011. Pengaruh pemberian kompos untuk tanaman caisim (Brassica juncea L.) sebagai rotasi tanaman setelah padi pada sistem pertanian terapung di lahan rawa lebak. Skripsi pada Jurusan Tanah. Fakultas Pertanian. Universitas Sriwijaya, Indralaya (unpublihed, in Indonesian).Risza R. 1995. Budidaya Kelapa Sawit. AAK. Kanisius. Yogyakarta (in Indonesian).Saptiningsih E. 2007. Peningkatan produktivitas tanah pasir untuk pertumbuhan tanaman kedelai dengan inokulasi mikorhiza dan rhizobium. BIOMA 9: 58–61 (in Indonesian).Setyorini D and RW Ladiyani. 2005. Cara Cepat Menguji Status Hara dan Kemasaman Tanah. Balai Penelitian Tanah. Bogor (in Indonesian).Sinar Tani. 2008. Teknologi Pencetakan Sawah Dan Pengelolaan Sawah Pada Lahan Tambang Timah. Available at http://www.sinartani.com/iptek/teknologi-pencetakan-sawah-dan-pengelolaan-sawah-pada-lahan-tambang-timah-1274070248.htm (diakses tanggal 25-4-2011) (in Indonesian).Sitorus SRP and LN Badri. 2008. Karakteristik tanah dan vegetasi lahan terdegradasi pasca penambangan timah serta teknik rehabilitasi untuk keperluan revegetasi. Prosiding Semiloka Nasional Strategi Penanggulangan Krisis Sumber Daya Lahan Untuk Ketahanan Pangan dan Energi, pp. 140-150 (in Indonesian).Sitorus SRP, E Kusumastuti and  N Badri. 2005. Karakteristik dan teknik rehabilitasi lahan pasca penambangan timah di pulau Bangka dan Singkep. J Tanah dan Iklim 27: 57-73 (in Indonesian)Sopian  A. 2009. Respon tanaman karet pada lahan pasca tambang batubara terhadap bahan amelioran berupa pupuk NPK dan kapur dolomit. J Agrifor 7(1): 1-7 (in Indonesian).Sudaryono. 2009. Tingkat kesuburan tanah ultisol pada lahan pertambangan batubara Sangatta, Kalimantan Timur. J Teknik Lingkungan 10: 337- 346 (in Indonesian).Suwandi. 2009. Menakar kebutuhan hara tanaman dalam pengembangan inovasi budidaya sayuran berkelanjutan. Pengembang Inovasi Pert 2: 131-147 (in Indonesian).Syarif F, N Hidayati and T Juhaeti. 2009. Tumbuhan Berdaun Lebar Berpotensi Akumulator. Tumbuhan Akumulator untuk Fitoremediasi Lingkungan Tercemar Merkuri dan Sianida Penambangan Emas. LIPI press, Jakarta (in Indonesian).Yani M. 2005. Reklamasi lahan bekas pertambangan dengan penanaman jarak pagar (Jatropha  curcas Linn). Pusat Penelitian Surfaktan dan Bioenergi. LPPM – IPB, Bogor (in Indonesian).Ye ZH, WS Shu, ZQ Zhang, CY Lan and MH Wong. 2002. Evaluation of Major Constraint to Revegatation of Lead/Zinc Mine Tailings Using Bioassay Techniques. Chemosphere 47: 1103-1111. 
Increasing of Rice Yield by Using Growth Promoting Endophytic Bacteria from Swamp Land Siti Nurul Aidil Fitri; Nuni Gofar
JOURNAL OF TROPICAL SOILS Vol 15, No 3: September 2010
Publisher : UNIVERSITY OF LAMPUNG

Show Abstract | Download Original | Original Source | Check in Google Scholar | DOI: 10.5400/jts.2010.v15i3.271-276

Abstract

Increasing of Rice Yield by Using Growth Promoting Endophytic Bacteria from Swamp Land (SNA Fitri and N Gofar):  Swamp land has can be used as a paddy field that will be potential as a rice source However, this land has some limiting factors such as low fertility. On the other hand, continous used of inorganic fertilizer to improve soil fertility will also have some disadvantages. Therefore,  an alternative method as  fertilizers complement is needed.  Biofertilizer  is potential to be developed.  Previous research had succeeded to explore and selected some bacteria from rice tissues grown on swamp land.  That research had found two bacteria Consortium were named as Growth Promoting Endophytic Bacterial Consortium (GPEBC).  The aims of this research were (1) to evaluate the effect of a GPEBC population density and a level of N fertilizer on plant N absorption, and rice yield in the swamp soil, and (2) to find out the optimal population density of GPEBC and optimal dosage of N fertilizer on plant N absorption and rice yields in the swamp soil.  The research used a factorial completely randomized design with 3 factors and 3 replicates.  The first factor was a kind of GPEBC which consisted of Consortium A and consortium B.  The second factors was population density of GPEBC which consisted of 0 CFU mL-1, 107 cfu mL-1, 109 cfu mL-1, and 1011 cfu mL-1.  The third factor was N-fertilizer dosages which consisted of 50% of plant nitrogen necessity (equivalent to 57.50 kg N ha-1), 75% of plant nitrogen necessity (equivalent to 86.25 kg N ha-1), and 100 % of plant N necessity (equivalent to 115 kg N ha-1).  The research showed that GPEBC of the Consortium B had a better effect on rice yiels than Consortium A.  The population density of 107 cfu mL-1 of GPEBC increased the growth and the yield of rice grown on swamp soil. Treatment combination of 75% of plant N necessity, and 107 cfu mL-1 of population density produced the best production of Consortium B  (GPEBC) for rice grown on swamp soil.
The Potential of Swampland Microalgae as Nitrogen Provider Primastya Ayu Lestari; Nuni Gofar; Dedik Budianta
JOURNAL OF TROPICAL SOILS Vol 23, No 3: September 2018
Publisher : UNIVERSITY OF LAMPUNG

Show Abstract | Download Original | Original Source | Check in Google Scholar | DOI: 10.5400/jts.2018.v23i3.125-131

Abstract

This study aimed to identify and explore the potential of microalgae from swampland of South Sumatra as nitrogen contributor for rice plants grown on swampland. Determination of sampling points was done by looking at the presence and abundance of microalgae in the sampling locations.  The method used in the sampling is purposive sampling method. The samples were grouped into 3, i.e. culture 1 (B1) derived from rice cultivation area, culture 2 (B2) derived from land that was not cultivated with rice, and culture 3 (B3) derived from swamp water samples. The medium used to culture the microlagae was Johnson's medium. The variables measured were the number of microalgae cells and ammonium concentrations on day 1, 4, 8 and 16 of culturing. Three species of Cyanophyceae class from the swampland were identified, i.e. thread algae, Synedra sp. and Melosira sp. Those microalgae may contribute the maximum amount of available nitrogen of 21.41 ìg mL-1 in the form of ammonium to the rice plants on days 10-12. Microalgae in culture 1 can contribute nitrogen for rice plants in the form of ammonium about 16.23% - 48.71% with the cell density of 7.48 cells mL-1.
Characterization of Petroleum Hydrocarbon Decomposing Fungi Isolated from Mangrove Rhizosphere Nuni Gofar
JOURNAL OF TROPICAL SOILS Vol 16, No 1: January 2011
Publisher : UNIVERSITY OF LAMPUNG

Show Abstract | Download Original | Original Source | Check in Google Scholar | DOI: 10.5400/jts.2011.v16i1.39-45

Abstract

The research was done to obtain the isolates of soil borne fungi isolated from mangrove rhizosphere which were capable of degrading petroleum hydrocarbon compounds. The soil samples were collected from South Sumatra mangrove forest which was contaminated by petroleum. The isolates obtained were selected based on their ability to survive, to grow and to degrade polycyclic aromatic hydrocarbons in medium containing petroleum residue. There were 3 isolates of soil borne hydrocarbonoclastic fungi which were able to degrade petroleum in vitro. The 3 isolates were identified as Aspergillus fumigates, A. parasiticus, and Chrysonilia sitophila. C. sitophila was the best isolate to decrease total petroleum hydrocarbon (TPH) from medium containing 5-20% petroleum residue.Keywords: Hydrocarbonoclastic fungi, hydrocarbon compounds, mangrove rhizosphere
Increasing of Rice Yield by Using Growth Promoting Endophytic Bacteria from Swamp Land Fitri, Siti Nurul Aidil; Gofar, Nuni
JOURNAL OF TROPICAL SOILS Vol. 15 No. 3: September 2010
Publisher : UNIVERSITY OF LAMPUNG

Show Abstract | Download Original | Original Source | Check in Google Scholar | DOI: 10.5400/jts.2010.v15i3.271-276

Abstract

Increasing of Rice Yield by Using Growth Promoting Endophytic Bacteria from Swamp Land (SNA Fitri and N Gofar):  Swamp land has can be used as a paddy field that will be potential as a rice source However, this land has some limiting factors such as low fertility. On the other hand, continous used of inorganic fertilizer to improve soil fertility will also have some disadvantages. Therefore,  an alternative method as  fertilizers complement is needed.  Biofertilizer  is potential to be developed.  Previous research had succeeded to explore and selected some bacteria from rice tissues grown on swamp land.  That research had found two bacteria Consortium were named as Growth Promoting Endophytic Bacterial Consortium (GPEBC).  The aims of this research were (1) to evaluate the effect of a GPEBC population density and a level of N fertilizer on plant N absorption, and rice yield in the swamp soil, and (2) to find out the optimal population density of GPEBC and optimal dosage of N fertilizer on plant N absorption and rice yields in the swamp soil.  The research used a factorial completely randomized design with 3 factors and 3 replicates.  The first factor was a kind of GPEBC which consisted of Consortium A and consortium B.  The second factors was population density of GPEBC which consisted of 0 CFU mL-1, 107 cfu mL-1, 109 cfu mL-1, and 1011 cfu mL-1.  The third factor was N-fertilizer dosages which consisted of 50% of plant nitrogen necessity (equivalent to 57.50 kg N ha-1), 75% of plant nitrogen necessity (equivalent to 86.25 kg N ha-1), and 100 % of plant N necessity (equivalent to 115 kg N ha-1).  The research showed that GPEBC of the Consortium B had a better effect on rice yiels than Consortium A.  The population density of 107 cfu mL-1 of GPEBC increased the growth and the yield of rice grown on swamp soil. Treatment combination of 75% of plant N necessity, and 107 cfu mL-1 of population density produced the best production of Consortium B  (GPEBC) for rice grown on swamp soil.
Characterization of Petroleum Hydrocarbon Decomposing Fungi Isolated from Mangrove Rhizosphere Gofar, Nuni
JOURNAL OF TROPICAL SOILS Vol. 16 No. 1: January 2011
Publisher : UNIVERSITY OF LAMPUNG

Show Abstract | Download Original | Original Source | Check in Google Scholar | DOI: 10.5400/jts.2011.v16i1.39-45

Abstract

The research was done to obtain the isolates of soil borne fungi isolated from mangrove rhizosphere which were capable of degrading petroleum hydrocarbon compounds. The soil samples were collected from South Sumatra mangrove forest which was contaminated by petroleum. The isolates obtained were selected based on their ability to survive, to grow and to degrade polycyclic aromatic hydrocarbons in medium containing petroleum residue. There were 3 isolates of soil borne hydrocarbonoclastic fungi which were able to degrade petroleum in vitro. The 3 isolates were identified as Aspergillus fumigates, A. parasiticus, and Chrysonilia sitophila. C. sitophila was the best isolate to decrease total petroleum hydrocarbon (TPH) from medium containing 5-20% petroleum residue.Keywords: Hydrocarbonoclastic fungi, hydrocarbon compounds, mangrove rhizosphere
Synergism of Wild Grass and Hydrocarbonoclastic Bacteria in Petroleum Biodegradation Gofar, Nuni
JOURNAL OF TROPICAL SOILS Vol. 18 No. 2: May 2013
Publisher : UNIVERSITY OF LAMPUNG

Show Abstract | Download Original | Original Source | Check in Google Scholar | DOI: 10.5400/jts.2013.v18i2.161-168

Abstract

The concept of plants and microbes utilization for remediation measure of pollutant contaminated soil is the newest development in term of petroleum waste management technique. The research objective was to obtain wild grass types and hydrocarbonoclastic bacteria which are capable to synergize in decreasing petroleum concentration within petroleum contaminated soil. This research was conducted by using randomized completely block design. This research was conducted by using randomized completely block design. The first factor treatments were consisted of without plant, Tridax procumbens grass and Lepironia mucronata grass. The second factor treatments were consisted of without bacterium, single bacterium of Alcaligenes faecalis, single bacterium of Pseudomonas alcaligenes, and mixed bacteria of Alcaligenes faecalis with P. alcaligenes. The results showed that mixed bacteria (A.  faecalis and P. alcaligenes) were capable to increase the crown and roots dry weights of these two grasses, bacteria population, percentage of TPH (total petroleum hydrocarbon) decrease as well as TPH decrease and better pH value than that of single bacterium. The highest TPH decrease with magnitude of 70.1% was obtained on treatment of L. mucronata grass in combination with mixed bacteria.[How to Cite: Gofar N. 2013.Synergism of Wild Grass and Hydrocarbonoclastic Bacteria in Petroleum Biodegradation. J Trop Soils 18 (2): 161-168. Doi: 10.5400/jts.2013.18.2.161][Permalink/DOI: www.dx.doi.org/10.5400/jts.2013.18.2.161]REFERENCESBello YM. 2007. Biodegradation of Lagoma crude oil using pig dung.  Afr J Biotechnol 6: 2821-2825.Gerhardt KE, XD Huang, BR Glick and BM Greenberg. 2009. Phytoremediation and rhizoremediation of organic soil contaminants: Potential and challenges. Plant Sci 176: 20-30.Glick BR. 2010. Using soil bacteria to facilitate phytoremediation.  Biotechnol Adv 28: 367-374. Gofar N. 2011.  Characterization of petroleum hydrocarbon decomposing fungi isolated from mangrove rhizosphere.  J Trop Soils 16(1): 39-45. doi: 10.5400/jts.2011.16.1.39Gofar N. 2012. Aplikasi isolat bakteri hidrokarbonoklastik asal rhizosfer mangrove pada tanah tercemar minyak bumi. J Lahan Suboptimal 1: 123-129 (in Indonesian). Hong WF, IJ Farmayan, CY Dortch, SK Chiang and JL Schnoor. 2001. Environ Sci Technol 35: 1231.Khashayar T and T Mahsa. 2010.  Biodegradation potential of petroleum hydrocarbons by bacterial diversity in soil. Morld App Sci J 8: 750-755.Lal B and S Khanna. 1996. Degradation of Crude Oil by Acinetobacter calcoaceticus and Alcaligenes odorans, J Appl Bacteriol 81: 355- 362.Mackova M, D Dowling and T Macek. 2006. Phytoremediation and rhizoremediation: Theoretical background. Springer, Dordrecht, Netherlands. 300 p. Malik ZA and S Ahmed.  2012. Degradation of petroleum hydrocarbons by oil field isolated bacterial consortium. Afr J Biotechnol 11: 650-658.Mendez MO and RM Maier. 2008. Phytostabilization of mine tailings in arid and semiarid environment an emerging remediation technology. Environ Health Prospect 116: 278-283.Milic JS, VP Beskoski, MV Ilic, SM Ali, GDJ Cvijovic and MM Vrvic.  2009.  Bioremediation of soil heavily contaminated with crude oil and its products: composition of the microbial consortium. J Serb Chem Soc  74: 455-460.Mukre AM, AA Hamid, A Hamzah and WM Yusoff.  2008.  Development of three bacteria consortium for the bioremediation of crude petroleum-oil in contaminated water. J Biol Sci 8: 73-79.Ndimele PE. 2010. A review on the phytioremediation of petroleum hydrocarbon. Pakistan J Biol Sci 12:  715-722.Newman LA and CM Reynolds.  2004.  Phytoremediation of organic compounds. Curr Opin Biotechnol  15: 225-230.Onwuka F, N Nwachoko, and E Anosike. 2012. Determination of total petroleum hydrocarbon (TPH) and some cations (Na+, Ca2+ and Mg2+) in a crude oil polluted soil and possible phytoremediation by Cynodon dactylon L (Bermuda grass). J Environ Earth Sci 2: 12-17.Pezeshki SR, MW Hester, Q Lin and JA Nyman.  2000.  The effect of oil spill and clean-up on dominant US Gulf Coast Marsh Macrophytes: a review.  Environ Pollution 108: 129-139.Pikoli MR, P Aditiawati and DI Astuti. 2000. Isolasi bertahap dan identifikasi isolat bakteri termofilik pendegradasi minyak bumi dari sumur bangko. Laporan Penelitian pada Jurusan Biologi, ITB, Bandung (unpublished, in Indonesian).Pilon-Smits E and JL Freeman. 2006. Environmental cleanup using plants: biotechnological advances and ecological considerations. Front Ecol Environ 4: 203-10. Rahman KSM, JT Rahman, P Lakshmanaperumalsamy, and IM Banat. 2002. Towards efficient crude oil degradation by a mixed bacterial consortium. Bioresource Technol 85: 257-261.Rossiana N.  2004. Oily Sludge Bioremediation with Zeolite and Microorganism and It’s Test with Albizia Plant (Paraserianthes falcataria) L (Nielsen). Laboratory of Environmental Microbiology, Department of Biology Padjadjaran University, Bandung (unpublished).Rossiana, N.  2005.  Penurunan Kandungan Logam Berat dan Pertumbuhan Tanaman Sengon (Paraserianthes falcataria L (Nielsen) Bermikoriza dalam Media Limbah Lumpur Minyak Hasil Ekstraksi. Laboratorium Mikrobiologi dan Biologi Lingkungan Jurusan Biologi Fakultas Matematika dan Ilmu Pengetahuan Alam Universitas Padjajaran, Bandung  (in Indonesian).Sathishkumar M, B Arthur Raj, B Sang-Ho, and Y Sei-Eok. 2008. Biodegradation of crude oil by individual bacterial strains and a mixed bacterial consortium isolated from hydrocarbon contaminated areas clean. Ind J Biotechnol 36: 92-96.Shirdam R, AD Zand, GN Bidhendi and N Mehrdadi.  2008. 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Improvement of Sand Tailing Fertility Derived from Post Tin Mining Using Leguminous Crop Applied by Compost and Mineral Soil Budianta, Dedik; Gofar, Nuni; Andika, Gusti Aditya
JOURNAL OF TROPICAL SOILS Vol. 18 No. 3: September 2013
Publisher : UNIVERSITY OF LAMPUNG

Show Abstract | Download Original | Original Source | Check in Google Scholar | DOI: 10.5400/jts.2013.v18i3.217-223

Abstract

The research was aimed to study the potency of two leguminous cover crops in enhancing tailing fertility of post tin mining with and without addition of mineral soil  and compost. This pot experiment was carried out in Greenhouse of Soil Science Department, Faculty of Agriculture, Sriwijaya University from November 2011 until March 2012. Design experiment used was a Completly Randomized Design (CRD) factorial with two factors. The first factor was type of cover corps which were Centrosema pubescens and Pueraria javanica. The second factor was plant media composition which were 100% sand tailing, 60% sand tailing + 40%  mineral soil, and  95% sand tailing + 5% compost. The result showed that N content on sand tailing after harvesting applied by compost and mineral soil was not significant by difference. Meanwhile, P content on sand tailing applied by compost was higher than mineral soil application and/or control (100% sand tailing).Keywords: Compost, legominous crop, N and P nutrients, sand tailing [How to Cite: Budianta D, N Gofar and GA Andika. 2013. Improvement of Sand Tailing Fertility Derived from Post Tin Mining Using Leguminous Crop Applied by Compost and Mineral Soil. JTrop Soils 18 (3): 217-223. Doi: 10.5400/jts.2013.18.3.217][Permalink/DOI: www.dx.doi.org/10.5400/jts.2013.18.3.93]REFERENCESAng LH. 2002. Problems and Prospecs of Afforestration on Sandy Tin Tailings in Peninsular Malaysia. J Trop Forest Sci 1: 87-105Budianta D, U Harun and R Santi. 2010. Perbaikan Sandy Tailing Asal Lahan Pasca Penambangan Timah dengan Kompos untuk Pertumbuhan Nilam. Prosiding Seminar Nasional, Masyarakat Konservasi Tanah dan Air Indonesia: 235-255, Jambi (in Indonesian).Djunaedi EK and F Djabar. 2003. 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The Potential of Swampland Microalgae as Nitrogen Provider Lestari, Primastya Ayu; Gofar, Nuni; Budianta, Dedik
JOURNAL OF TROPICAL SOILS Vol. 23 No. 3: September 2018
Publisher : UNIVERSITY OF LAMPUNG

Show Abstract | Download Original | Original Source | Check in Google Scholar | DOI: 10.5400/jts.2018.v23i3.125-131

Abstract

This study aimed to identify and explore the potential of microalgae from swampland of South Sumatra as nitrogen contributor for rice plants grown on swampland. Determination of sampling points was done by looking at the presence and abundance of microalgae in the sampling locations.  The method used in the sampling is purposive sampling method. The samples were grouped into 3, i.e. culture 1 (B1) derived from rice cultivation area, culture 2 (B2) derived from land that was not cultivated with rice, and culture 3 (B3) derived from swamp water samples. The medium used to culture the microlagae was Johnson's medium. The variables measured were the number of microalgae cells and ammonium concentrations on day 1, 4, 8 and 16 of culturing. Three species of Cyanophyceae class from the swampland were identified, i.e. thread algae, Synedra sp. and Melosira sp. Those microalgae may contribute the maximum amount of available nitrogen of 21.41 ìg mL-1 in the form of ammonium to the rice plants on days 10-12. Microalgae in culture 1 can contribute nitrogen for rice plants in the form of ammonium about 16.23% - 48.71% with the cell density of 7.48 cells mL-1.
Co-Authors Abdul Madjid Abdull Madjid Rohim Abdullah Halim Perdana Kusuma Subakti Ace Baehaki Adi Supriyadi Adipati Napoleon Agus Hermawan Albertus Fajar Irawan Albertus Fajar Irawan Ali Amran Amartiya Sari, Shabilla Andi Diana Andika, Gusti Aditya ANDY MULYANA Angga Prasetya Mulya Anita Desiani Anjastari, Devi Annisa Nabila, Annisa Asmak Asmak Ayuputri, Niken Bambang Suprihatin Budi Untari Buyana, Nova Tri Chairu Nisa Apriyani Dade Jubaedah Dade Jubaedah Dedik Budianta Devi Anjastari Diana Sinurat Diana Utama Diana Utama Diana Utama DWI ANDREAS SANTOSA Dwi Paserena, Karinda Eka Setianingsih Eli Sahara Ermatita - Erra Kartika Erra Kartika, Erra Erwin Saputra Fadjar Sidiq Hidayahtullah fitra yosi, fitra Fitralia Elyza Fitri Siti Nurul Aidil Geovani, Dite Ghea Salsabila, Nadhira Gusti Aditya Andika Hary Widjajanti Irmeilyana Kerenila Agustin Kurnia, M Kahfi Aldi Lestari, Primastya Ayu Lestari, Primastya Ayu M. Umar Harun M. Umar Harun Maria Lusia Marini Wijayanti Marsi Meilasari, Nabilla Meisji Liana Sari Miksusanti Miksusanti Muhammad Wahyu Ilahi Muhammat Rio Halim Munandar Munandar Munawar Munawar Muzayyadah, Fathona Nur Nasrul Harahap Neni Marlina Ni Luh Putu SR Novi Wulandari Mustika Nyayu Nurul Husna Primastya Ayu Lestari Putri Nur, Tri Redina An Fadhila Chaniago Renih Hayati Rodiana Nopianti Rohim, A. Madjid Rosmiah Rosmiah, Rosmiah Satria Jaya Priatna, Satria Jaya Siti Komariah Hildayanti Siti Komariah Hildayanti, Siti Komariah Siti Nurul Aidil Fitri Siti Nurul Aidil Fitri Siti Nurul Aidil, Fitri Sofia Sandi Sriati Sriati Sriati Sriati, Sriati Sugandi Yahdin Susilawati Syarifuddin, Fauzi Yusuf Tanbiyaskur Tanbiyaskur Teguh Randi Pradana Tri Putri Nur Utama, Diana Utama, Diana wahyu tri patria Warsito Warsito Widya Irmawati Wuriesyliane Wuriesyliane Yopie Moelyohadi Yopie Moelyohadi Yuli Andriani Yuli Andriani