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Bestimmung von Redoxzonen in einem mineral?lbelasteten Grundwasserleiter

机译:测定被矿物油污染的含水层中的氧化还原带

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Goal and Scope The goal of this study is the investigation and the grafic presentation of the characteristic redox zonation in a mineral oil contaminated aquifer which will be formed in the plume downstream of the contamination source. Methanogenic conditions, sulfate-reduction, Fe(III)-reduction, Mn(IV)-reduction, nitrate-reduction, aerobic conditions. By that indications type and degree of microbial degradation which is the most important part in Natural Attenuation (NA) processes can be obtained easily. Methods Changes of the groundwater parameters Eh, O2, NO 3 ? , SO4 2?, Fe2+, Mn2+, HCO3 ?, Ca2+ will be measured upstream, downstream and also in the centre of the plume. The results will be presented in a sequence of special diagrams. Results and Conclusion When microbial degradation of hydrocarbons takes place, a microbial community will always use that electron acceptor from which it will gain a maximum of energy by the corresponding redox-reactions. This means as long as oxygen is available this will be used. After its depletion nitrate serves as electron acceptor leading via nitrite to the formation of nitrogen or ammonia. Manganese (IV) and Iron (III) species which are rather insoluble are mainly available from the soil-phase, can act as electron acceptor as next, leading to soluble Manganese (II) and Iron (II) compounds in groundwater. Finally before methanogenic conditions occur sulphate will become a suitable electron acceptor leading to the formation of hydrogen sulphide. All these processes of mineralization of the hydrocarbons will lead to the production of CO2 and as consequence to an increase of HCO3 ? in groundwater changing the calcareous/carbonic acid-equilibrium. By that more soluble Ca(HCO3)2 is formed from insoluble CaCO3, so the concentration from Ca2+ will also inerease. Thus, by the action of microorganisms, a typical redox-zonation and changes of other parameters will occur. Recommendations and Perspective To follow the changes in time and space of some characteristic groundwater parameters is a simple way to estimate the potential of microbial degradation in a contaminated aquifer considering Natural Attenuation (NA)-processes.
机译:目的和范围这项研究的目的是调查和以石墨形式呈现矿物油污染含水层中的特征性氧化还原带,该含水层将在污染源下游的羽状流中形成。产甲烷条件,硫酸盐还原,Fe(III)还原,Mn(IV)还原,硝酸盐还原,好氧条件。通过这种指示,可以很容易地获得微生物降解的类型和程度,这是自然衰减(NA)过程中最重要的部分。方法改变地下水参数Eh,O2,NO 3? ,SO4 2 +,Fe2 +,Mn2 +,HCO3 +,Ca2 +将在烟羽的上游,下游和中心进行测量。结果将以一系列特殊图表的形式呈现。结果与结论当烃类发生微生物降解时,微生物群落将始终使用该电子受体,通过相应的氧化还原反应,该电子受体将从中获得最大能量。这意味着只要有氧气就可以使用。耗尽后,硝酸盐充当电子受体,通过亚硝酸盐导致形成氮或氨。难溶的锰(IV)和铁(III)物种主要来自土壤相,可作为下一步的电子受体,导致地下水中的可溶性锰(II)和铁(II)化合物。最后,在产甲烷条件发生之前,硫酸盐将成为合适的电子受体,导致形成硫化氢。所有这些碳氢化合物矿化的过程将导致产生CO2,并因此导致HCO3的增加。在地下水中改变钙质/碳酸平衡。由于不溶性CaCO3形成了更易溶的Ca(HCO3)2,因此来自Ca2 +的浓度也将增加。因此,通过微生物的作用,将发生典型的氧化还原区域和其他参数的变化。建议和观点遵循某些自然地下水参数随时间和空间的变化,这是一种考虑自然衰减(NA)过程估算受污染含水层中微生物降解潜力的简单方法。

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