首页> 外文期刊>International Biodeterioration & Biodegradation >Effects of local microbial bioaugmentation and biostimulation on the bioremediation of total petroleum hydrocarbons (TPH) in crude oil contaminated soil based on laboratory. and field observations
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Effects of local microbial bioaugmentation and biostimulation on the bioremediation of total petroleum hydrocarbons (TPH) in crude oil contaminated soil based on laboratory. and field observations

机译:根据实验室,局部微生物的生物强化和生物刺激对原油污染土壤中总石油烃(TPH)生物修复的影响。和实地观察

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This study investigated factors enhancing the performance of the bioremediation of Total Petroleum Hydrocarbons (TPHs) in crude oil-contaminated soil in laboratory and field observations. The bio-augmentation process used local microbial consortia (MCI, MC2 and MC3) combined with the bio-stimulation processes of nutrient addition (mineral salt medium, MSM and NPK) and enhanced air stimulation (air supply and Oxygen Releasing Compound (ORC1m)). The microcosm tests were conducted in tank and soil column setups, whereas the field test was performed in test plots inside an oil and gas facility in Malaysia. In the microcosm tank experiment, the combination of bioaugmentation (10% inoculum size of MC3) and MSM biostimulation yielded the highest TPH degradation of 79% of the total. In the column experiments, the degradation of TPHs in the top soil was highest in columns combining bioaugmentation and nutrient addition, whereas in the bottom soil, the degradation of TPHs was highest in columns combining bioaugmentation with the addition of both nutrients and ORCs. In the field demonstration, 97% of the TPHs were degraded in the top soil (0-1 m) when bioaugmented with MC2. The kinetic analysis study of the microcosm tank showed that a combination of both biostimulation and bioaugmentation in the soil column achieved the fastest rate constant of 0.0390 day(-1). The field test also demonstrated a comparable rate constant of 0.0339 day(-1). The kinetic rate constants in both the laboratory and field indicated that the best treatment method for the contaminated site is a combination of MC3 bioaugmentation and nutrient biostimulation
机译:这项研究在实验室和现场观察中研究了增强原油污染土壤中总石油烃(TPHs)生物修复性能的因素。生物增强过程使用了局部微生物联盟(MCI,MC2和MC3),并结合了添加营养(矿物盐培养基,MSM和NPK)和增强空气刺激(空气供应和氧气释放化合物(ORC1m))的生物刺激过程。 。微观测试是在储罐和土壤柱设置中进行的,而现场测试是在马来西亚的石油和天然气设施内的测试区中进行的。在缩影缸实验中,生物强化(接种量为MC3的10%)和MSM生物刺激相结合产生了最高的TPH降解,占总降解量的79%。在柱实验中,结合生物强化和添加养分的柱顶土中TPHs的降解最高,而在底部土壤结合生物增强和添加养分和ORCs柱中TPHs的降解最高。在现场演示中,当使用MC2生物增强时,表层土壤(0-1 m)中有97%的TPHs降解。对微观世界坦克进行的动力学分析研究表明,在土壤柱中生物刺激与生物强化相结合的最快速率常数为0.0390天(-1)。现场测试还表明可比较的速率常数为0.0339天(-1)。在实验室和现场的动力学速率常数均表明,针对污染部位的最佳处理方法是将MC3生物强化和营养物生物刺激相结合

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