Penggunaan Biokompos dalam Bioremediasi Lahan Tercemar Limbah Minyak Bumi

Abstract

AbstrakPenelitian ini dilakukan untuk mengetahui efektifitas biokompos, rumput gajah dan kelompok mikroba yang efektif dalam bioremediasi lahan tercemar minyak bumi yang dilakukan dalam skala laboratorium, dan bahan tambahan yang digunakan urea sebagai sumber nitrogen. Pada penelitian ini dilakukan berdasarkan rasio C/N yaitu 15, 10, dan 5. Parameter uji yang dilakukan untuk mengetahui kondisi optimal yang dicapai pada remediasi terdiri atas pH, kadar air, kadar abu, dan kemampuan ikat air/water holding capacity (WHC). Hasilnya menunjukan degradasi TPH (Total Petroleum Hidrokarbon) sebesar 91,15% dengan komposisi medium (100 g berat kering lumpur minyak bumi, 100 g berat kering biokompos, 9 g urea, rasio C/N = 5) menggunakan perlakuan dari kombinasi rumput gajah, mikroorganisme, urea dan biokompos selama 35 hari. Faktor lingkungan yang menghasilkan kondisi optimal ini dicapai pada remediasi diperoleh melalui kondisi awal pH 8,25; kadar air 49,97%; WHC 101,64%; dan kadar abu 63,76% dan kondisi akhir pH 6,25; kadar air 55,04%; kadar abu 73,39%; dan WHC 124,11%. Penambahan kompos dan urea dapat meningkatkan efisiensi degradasi TPH dan diperoleh hubungan positif antara jumlah penambahan kompos dan urea terhadap tingkat degradasi TPH. AbstractThis research was conducted to determine the effectiveness of biocompost and elephant grass of rehabilitating oil polluted land using landfarming methods, in combination with the addition of urea as sources of nitrogen. This research was conducted based on the 15, 10, and 5 of C/N ratios, respectively. Test parameters needed to knowing the optimal condition in remediation were pH, water content, ash content, and water holding capacity (WHC). Results show the Total Petroleum Hydrocarbon (TPH) was degraded until 91,15% for 35 days. Under treatment of elephant grass, urea, biocompost combination within composition medium of (100 g dry mass soil polluted hydrocarbon, 100 g dry mass biocompost, 9 g fertilizer, and C/N ratio : 5) using combined treatment of elephant grass, microorganisme, fertilizer, and biocompost after 35 days. The environmental factor yielding this optimal remediation reached was obtained through initial condition of pH 8,25; water content 49,97%; WHC 101,64%; ash content 63,76% and final condition of pH 6,25; water content 55,04%; ash content 73,39%; and WHC 124,11%, respectively. The addition of compost and urea has increased the efficiency of TPH degradation and obtained positive relationship between addition amounts of compost and urea to the level of TPH degradation.

THE POTENTIAL BIODEGRADATION HYDROCARBONS OF PETROLEUM SLUDGE WASTE BY CELL BIOMASS SPONGE Callysppongia sp.

“…Measurements parameters degradation (formation of gas, the smell of fermentation, pH, and absorbent media degradation) is performed every 5 days by taking 1 piece vial each treatment, suspension of media degradation and residual PSW not degraded separated by a separating funnel, suspension media degradation accommodated in the vial another absorbance measurement at λ = 600 nm, while the rest of the PSW dissolved in 10 mL of dichloromethane GR, shaken until all dissolved, allowed to stand ± 3 minutes to ensure all PSW soluble. Analysis of hydrocarbon components making up the waste petroleum sludge done by taking 50 mL of solution, waste petroleum sludge, diluted with 10 mL dichloromethane and samples must free of water before it analyzed by GC-MS [2,27,28,29].…”

“…Measurement parameter degradation (formation of gas, the smell of fermentation, pH, and the determination of the level of biodegradation is done by PSW diluted with dikloromethana, evaporated until all the solvent evaporates, and then weighed using the analytical balance Mettler AE-100. Note: All treatments carried out at a temperature 32 0 C, shaker with a speed of 100 rpm [2,28,29].…”

“…toxic, mutagenic and carcinogenic, categorized as hazardous materials, toxic. Waste petroleum hydrocarbon contamination can occur in nearly all lines of petroleum activities ranging from exploration through refining process, the process upstream to downstream stages and could potentially result in the form of sludge waste petroleum (oil sludge) [1,2].…”

Uji Efektivitas Kotoran Sapi Dalam Remediasi Tanah Top Soil Yang Tercemar Oli

“…Salah satu kandungan yang sulit diurai pada limbah oli merupakan senyawa hidrokarbon. Senyawa hidrokarbon akan menjadi zat pencemar apabila masuk ke dalam tanah dan dapat mengganggu pertumbuhan mikroorganisme yang terdapat di dalam tanah (Aliyanta, 2011).…”

Industri Pengolahan Minyak Bumi Di Indonesia

“…3. Pencemaran Air [147][148] Pencemaran perairan biasanya terjadi akibat tumpahan minyak bumi yang sering terjadi laut, hal ini di sebabkan adanya kebocoran kapal tengker yang mengangkut minyak bumi selain itu penyebab lainya adalah meledaknya anjungan minyak lepas pantai, operasi kapal dan bangunan lepas pantai. Bocornya sistem penampungan atau adanya kapal yang tenggelam menyebabkan tumpahan minyak dilaut sampai ke lepas pantai.…”