首页> 外文学位 >Insights into the mechanisms of iron reductive dissolution in vadose zone soils and implications for landfill activities: Predicting the potential for groundwater pollution.
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Insights into the mechanisms of iron reductive dissolution in vadose zone soils and implications for landfill activities: Predicting the potential for groundwater pollution.

机译:深入研究渗流带区土壤中铁还原溶解的机理及其对垃圾填埋场活动的影响:预测地下水污染的潜力。

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摘要

Anomalously high iron (Fe) concentrations have been measured in groundwater samples collected from monitoring wells downstream of several landfill units in Florida. Based on monitoring data, vadose zone soils and aquifer sediments impacted by landfills could be sources of Fe that pollutes the groundwater, and not landfilled wastes. Therefore, the objectives of this study were to investigate the reductive dissolution of soil-Fe as a function of biotic and abiotic processes; and to lay the groundwork for the development of a geochemical solubility model for Fe.;Soil samples were collected from different locations in North Florida, using a sampling strategy that included samples with a gradient in the degree of Fe-mineral crystallization. After characterization, soil samples were used in biotic (using bacteria from an anaerobic digester) and abiotic (using sulfide as electron donor) Fe-reductive dissolution batch studies. Fe(II) was released from all soils in concentrations that exceeded the secondary drinking water limit of 0.3 mg/L, when treated with bacteria and organic carbon (OC) or with sulfide but under abiotic conditions. Microbial respiration of OC in soils appears to be a major pathway and could lead to Fe-reductive dissolution in Fe-rich soils that interact with OC-rich waters or leachates. The rates of Fe-reductive dissolution were positively correlated with soil Fe content when glucose was used as the OC source, while no relationship was obvious when landfill leachate was used as OC. Sulfide driven Fe-reductive dissolution was positively correlated with soil-Fe content. However, despite the initial high release of Fe(II) into the aqueous phase in soil spiked with sulfide, temporal trends of Fe-reductive dissolution rates suggest that this pathway may not be as significant as the biotic process due likely to the precipitation of solid FeS species.;Finally, batch studies were conducted using hematite, an Fe-oxide mineral, to investigate the effects of pH, OC and ionic strength on Fe-reductive dissolution rates. Obtained data were used to develop a geochemical solubility model for soil-Fe; which was then validated using soil samples. However, an efficient fine tuning and validation of the model was not fully accomplished as more experimental and field data are still needed.
机译:在佛罗里达州几个垃圾填埋场下游的监测井中收集的地下水样品中,异常高的铁(Fe)浓度被测量。根据监测数据,受垃圾填埋影响的渗流带土壤和含水层沉积物可能是污染地下水的铁源,而不是垃圾填埋场。因此,本研究的目的是研究土壤铁的还原溶解与生物过程和非生物过程的关系。铁的地球化学溶解度模型的开发奠定了基础。土壤样品是从北佛罗里达州的不同地点收集的,采用的采样策略包括铁矿物结晶度梯度的样品。表征后,将土壤样品用于生物(使用厌氧消化池中的细菌)和非生物(使用硫化物作为电子供体)的铁还原溶出批次研究。当用细菌和有机碳(OC)或用硫化物处理但在非生物条件下处理时,Fe(II)从所有土壤中释放的浓度均超过二次饮用水限值0.3 mg / L。土壤中OC的微生物呼吸似乎是一个主要途径,并且可能导致与高OC的水或渗滤液相互作用的富Fe土壤中的Fe还原溶解。以葡萄糖为OC源时,Fe还原溶解速率与土壤Fe含量呈正相关,而以垃圾渗滤液为OC源则无明显关系。硫化物驱动的铁还原溶解与土壤铁含量呈正相关。然而,尽管最初掺入硫化物的土壤中的Fe(II)最初大量释放到水相中,但Fe降低溶出速率的时间趋势表明,该途径可能不如生物过程重要,这可能是由于固体沉淀所致。最后,使用赤铁矿(一种Fe-氧化物矿物)进行了批量研究,以研究pH,OC和离子强度对Fe还原溶出速率的影响。获得的数据用于建立土壤铁的地球化学溶解度模型。然后使用土壤样本进行验证。但是,由于仍然需要更多的实验数据和现场数据,因此尚未完全完成模型的有效微调和验证。

著录项

  • 作者

    Oppong-Anane, Akua Bonsu.;

  • 作者单位

    University of Florida.;

  • 授予单位 University of Florida.;
  • 学科 Environmental science.
  • 学位 Ph.D.
  • 年度 2014
  • 页码 154 p.
  • 总页数 154
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

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