Department of Civil Engineering, "National" Chi Nan University Taiwan, China.
J Environ Sci (China). 2010;22(6):864-71. doi: 10.1016/s1001-0742(09)60190-x.
In the first phase of this study, the effectiveness of intrinsic bioremediation on the containment of petroleum hydrocarbons was evaluated at a gasoline spill site. Evidences of the occurrence of intrinsic bioremediation within the BTEX (benzene, toluene, ethylbenzene, and xylenes) plume included (1) decreased BTEX concentrations; (2) depletion of dissolved oxygen (DO), nitrate, and sulfate; (3) production of dissolved ferrous iron, methane, and CO2; (4) deceased pH and redox potential; and (5) increased methanogens, total heterotrophs, and total anaerobes, especially within the highly contaminated areas. In the second phase of this study, enhanced aerobic bioremediation process was applied at site to enhance the BTEX decay rates. Air was injected into the subsurface near the mid-plume area to biostimulate the naturally occurring microorganisms for BTEX biodegradation. Field results showed that enhanced bioremediation process caused the change of BTEX removal mechanisms from anaerobic biodegradation inside the plume to aerobic biodegradation. This variation could be confirmed by the following field observations inside the plume due to the enhanced aerobic bioremediation process: (1) increased in DO, CO2, redox potential, nitrate, and sulfate, (2) decreased in dissolved ferrous iron, sulfide, and methane, (3) increased total heterotrophs and decreased total anaerobes. Field results also showed that the percentage of total BTEX removal increased from 92% to 99%, and the calculated total BTEX first-order natural attenuation rates increased from 0.0092% to 0.0188% per day, respectively, after the application of enhanced bioremediation system from the spill area to the downgradient area (located approximately 300 m from the source area).
在本研究的第一阶段,在一个汽油泄漏现场评估了自然生物修复对石油烃控制的有效性。BTEX(苯、甲苯、乙苯和二甲苯)羽流中自然生物修复发生的证据包括:(1)BTEX 浓度降低;(2)溶解氧(DO)、硝酸盐和硫酸盐耗竭;(3)溶解亚铁、甲烷和 CO2 的产生;(4)pH 值和氧化还原电位降低;(5)产甲烷菌、总异养菌和总厌氧菌增加,尤其是在高污染区。在本研究的第二阶段,在现场应用了强化好氧生物修复过程,以提高 BTEX 的衰减率。空气被注入羽流中部附近的地下,以生物刺激自然存在的微生物进行 BTEX 生物降解。现场结果表明,强化生物修复过程导致 BTEX 去除机制从羽流内部的厌氧生物降解转变为好氧生物降解。由于强化好氧生物修复过程,羽流内部的以下现场观察结果可以证实这种变化:(1)DO、CO2、氧化还原电位、硝酸盐和硫酸盐增加;(2)溶解亚铁、硫化物和甲烷减少;(3)总异养菌增加,总厌氧菌减少。现场结果还表明,总 BTEX 去除率从 92%增加到 99%,计算得出的总 BTEX 自然衰减率从 0.0092%/天增加到 0.0188%/天,分别在强化生物修复系统从泄漏区域应用到下游区域(位于距源区域约 300 m 处)后。