某污染场地地下水中溶解性有机质组成特征及其自然衰减指示作用

Characterizing the composition of dissolved organic matter in groundwater at a polluted site and its indicating significance for natural attenuation

  • 摘要: 溶解性有机质(DOM)影响着地下水中污染物的降解转化行为,其结构组成的变化可以反映外来污染物的迁移转化过程。以山东某污染场地地下水为研究对象,利用三维荧光光谱(EEM)、同步荧光光谱(SFS)和荧光区域体积积分法(FRI)分析研究区地下水DOM的组成及结构变化规律,并结合自然衰减能力评估方法——水文地球化学指标分析方法和微生物学分析方法探讨DOM光谱信息对地下水有机污染自然衰减效果的指示作用。结果表明:在地下水有机污染持续存在和长期的微生物作用下,地下水DOM中类腐殖质和类蛋白物质组分含量均增加,随着生物降解作用越来越强烈,DOM中类蛋白物质占比逐渐升高。基于FRI分区理论,提出可用特定荧光分区相对含量比〔P(Ⅰ+Ⅱ)/P〕,即类蛋白物质与类腐殖质物质的相对含量比,作为快速判断地下水有机污染自然衰减生物作用效果的代替表征指标,P(Ⅰ+Ⅱ)/P越大,表明自然衰减中的生物降解作用越强。

     

    Abstract: Dissolved organic matter (DOM) affects the degradation and transformation of pollutants in groundwater, and the changes of DOM structural composition can reflect the migration and transformation process of external pollutants. Taking groundwater from a polluted site in Shandong Province as the research object, three-dimensional fluorescence spectroscopy (EEM), synchronous fluorescence spectroscopy (SFS) and fluorescence region volume integral method (FRI) were used to analyze the composition and structure of the groundwater DOM. The role of DOM spectral information in indicating the natural attenuation effect of groundwater organic pollution was investigated in combination with the natural attenuation capacity assessment methods, i.e. hydrogeochemical index analysis method and microbiological analysis method. The results showed that the content of both humus-like and protein-like substances in groundwater increased under the persistence of organic pollution in groundwater and long-term microbial action, and the proportion of protein-like substances gradually increased with the increasingly strong biodegradation. Based on FRI region theory, a substitute characterization index was proposed to quickly assess the effect of the biodegradation in the natural attenuation of organic pollution in groundwater: the ratio of relative contents of specific fluorescence regions P(Ⅰ +Ⅱ) /P, that was, the ratio of the relative content of protein-like substances to humus-like substances. The larger the value of P(Ⅰ+Ⅱ) /P was, the stronger the biodegradation in natural attenuation was.

     

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