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BIOREMEDIATION FEASIBILITY STUDY FOR THE AVENUE COKING WORKS, CHESTERFIELD, UK

机译:英国切斯特菲尔德的道路焦化厂生物修复可行性研究

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Three locations of the former Avenue Coking Works have been sampled for bioremediation feasibility testing. In a first stage, slurry biodegradation tests were performed to assess the potential for biodegradation and optimal treatment conditions. Treatment conditions included dead and live controls, addition of inorganic fertiliser, a commercial nutrient mixture and inorganic fertilisers with adapted bacteria. Bioremediation was monitored by respiration measurents and by chemical analyses of pollutants after 8 and 17 weeks. For all soil samples but the Tar Pit, BTEX, phenol, cresols, C2-alkylphenols, NSO-heterocyclic compounds and naphtalene were removed to a significant extent. 3-ring PAH and mineral oil was also degraded in some, not all, samples. Higher ring PAH, C3-alkylphenols and mineral oil in some samples did not degrade. Slightly better microbial activity and pollutant removal appeared to result from the addition of inorganic fertilisers, albeit in combination with a bacterial inoculum. In a second stage, biodegradation kinetics were determined in two solid phase bioreactors for two soils, each receiving a commercial nutrient supplement. An 80-day monitoring of respiration activity and pollutants in soil and off-gas samples enabled mass balancing. For the soil highly polluted with tar, similar biodegradation was observed for BTEX, naphtalene and mineral oil as for the batch tests, without biodegradation of higher ring PAH. Phenolic compounds were not degraded. Significant volatilisation of VOC as well as cyanide was observed, most of the decrease in VOC concentrations in the soil was however due to biodegradation. For moderately polluted soil, similar results were observed as in the batch tests, I.e. a good removal of naphtalene and a decrease of approximately 50% of mineral oil and total PAH. PCR-analysis demonstrated the presence of Sphingomonas sp. Which could grow on pyrene as a unique source of carbon. Finally a full scale biopile was set up at the site to determine the achievable end points in real environment. After bioremediation of the plant area and waste tip material a soil is produced with only the heavier PAH’s remaining. The leachability for PAH’s, phenols and cyanides was largely reduced after treatment. C3-alkylphenols showed to be resistant for bioremediation.
机译:已对前大道焦化厂的三个位置进行了采样,以进行生物修复可行性测试。在第一阶段,进行了浆料生物降解测试,以评估生物降解潜力和最佳处理条件。处理条件包括死亡和活体控制,添加无机肥料,市售营养混合物以及带有适应性细菌的无机肥料。在8周和17周后,通过呼吸测量仪和污染物的化学分析监测生物修复。对于除沥青坑,BTEX,苯酚,甲酚,C2-烷基酚,NSO-杂环化合物和萘以外的所有土壤样品,都已大量去除。在某些(并非全部)样品中,三环PAH和矿物油也被降解。在某些样品中,较高环的PAH,C3-烷基酚和矿物油不会降解。尽管添加了无机肥料,但与细菌接种物结合使用后,微生物活性和污染物去除效果似乎略有提高。在第二阶段中,在两个土壤中的两个固相生物反应器中确定了生物降解动力学,每种土壤均接受了商业化的营养补充剂。对土壤和废气样品中的呼吸活动和污染物进行80天的监测可以实现质量平衡。对于焦油高度污染的土壤,BTEX,萘和矿物油的生物降解与分批测试相似,而高环PAH则没有生物降解。酚类化合物未降解。观察到VOC以及氰化物的大量挥发,但是土壤中VOC浓度的大部分下降是由于生物降解引起的。对于中度污染的土壤,观察到的结果与分批测试(即分批测试)相似。萘的去除效果很好,矿物油和总PAH减少了约50%。 PCR分析表明鞘氨醇单胞菌属的存在。可以在pyr上生长,作为唯一的碳源。最后,在现场设置了一个完整的生物堆,以确定实际环境中可实现的终点。在对植物区域和废料尖端材料进行生物修复之后,仅残留了较重的PAH,便产生了土壤。处理后,PAH,酚和氰化物的浸出能力大大降低。 C3-烷基酚显示出对生物修复的抗性。

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