首页> 外文会议>International in situ and on-site bioremediation symposium >PETROLEUM HYDROCARBON REMEDIATION IN BIOPILES: OPTIMIZING AERATION AND HEATING
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PETROLEUM HYDROCARBON REMEDIATION IN BIOPILES: OPTIMIZING AERATION AND HEATING

机译:生物岩中的石油碳氢化合物修复:优化曝气和加热

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A full-scale ex-situ bioremediation field study was carried out at the Soil Recycling Center (GRC) operated by Deme Environmental Contractors (DEC NV) in Kallo (Belgium), to evaluate the efficiency of aeration and heating for bioremediation in biopiles. An existing cell, 57 m long and 20 m wide, was filled up to a height of 1.8 m with contaminated soil. Both the aeration system and heating system consisted of pipes placed in the concrete floor of the cell. On top of the pipes a layer of gravel was placed to protect this construction. The soil was characterized as a clayey sand (texture: 70.8% sand, 17.7 % silt, 11.5% clay), the mean soil bulk density was 1.55 ± 0.09 g cm-3 at the start and 1.57 ± 0.07 at the end of the treatment period. Initial total hydrocarbon concentration was 1898 mg kg-1dry soil. The process was monitored during time by measuring the temperature and oxygen concentration weekly at different depths in the biopile. Two types of respirometry testing were done: the transient respirometry test proposed by Hinchee et al. (1992) and a static respirometry test as described by Patterson et al. (1999). The total petroleum hydrocarbon (TPH) concentration was measured at different times and the treatment was stopped when an average concentration of 500 mg TPH kg-1 was reached. The biopile operation began late September 2001 and concluded beginning of December 2001. TPH, oxygen concentrations and temperature values showed that very heterogeneous conditions existed in the biopile. The oxygen concentrations during aeration were at atmospheric level at every depth in the biopile, suggesting that aeration was more than sufficient. Assuming that optimal bacterial activity does not need atmospheric oxygen levels, a discontinuous aeration system would be more economical. Although respiration tests showed a decrease of biological activity over time, the estimated degradation rate was low, when compared to the decrease in hydrocarbon concentration. Further research will be needed to optimize the design of a discontinuous aeration system by oxygen concentration measurements and respiration tests.
机译:在Kallo(比利时)的Deme环境承包商(DEC NV)运营的土壤回收中心(GRC)进行了全面的前型生物修复现场研究,以评估生物填充中生物修复的通气和加热效率。现有的细胞,57米长和20米宽,含有污染的土壤的高度为1.8米。曝气系统和加热系统都包括放置在电池的混凝土地板中的管子。在管道上,放置一层砾石以保护这种结构。土壤的特征为粘土砂(质地:70.8%砂,17.7%淤泥,11.5%粘土),在开始时,平均土壤堆积密度为1.55±0.09g cm-3,结束时为1.57±0.07时期。初始总烃浓度为1898mg Kg-1dry土壤。通过在Biopile中的不同深度测量温度和氧气浓度期间在时间期间监测该方法。完成了两种类型的呼吸测定试验:Hinchee等人提出的瞬态呼吸测定法试验。 (1992)和帕特森等人所述的静态呼吸测定试验。 (1999)。在不同时间测量总石油烃(TPH)浓度,并且当达到500mg TPH-1的平均浓度时停止处理。 BIopile操作开始于2001年9月下旬并结束于2001年12月开始。TPH,氧浓度和温度值表明,生物素中存在非常异质的条件。在Biopile的每一个深度时,通气期间的氧浓度在大气压下,表明曝气量大于足够。假设最佳的细菌活性不需要大气氧水平,不连续的曝气系统将更经济。尽管随着时间的推移,呼吸试验显示生物活性的降低,但与烃浓度的降低相比,估计的降解速率低。需要进一步的研究来通过氧浓度测量和呼吸试验来优化不连续曝气系统的设计。

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