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Plant activity and organic contaminant processing by aquatic plants.

机译:植物活动和水生植物对有机污染物的处理。

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This research explored fate of organic contaminants in aquatic plant systems through (i) experimental development of relationships to describe sorption, uptake and enzymatic processing of contaminants by plants and inhibition of aquatic plants by contaminants and (ii) incorporation of experimental relationships into a conceptual model which describes contaminant fate in aquatic plant systems. This study focused on interactions of aquatic plants L. minor and M. aquaticum with halogenated phenols. 2,4,5-trichlorophenol (2,4,5-TCP) and 2,4-dichlorophenol (2,4-DCP) are precursors for the highly toxic and heavily applied herbicides 2,4,5-T and 2,4-D and were examined in detail. Chlorophenols are generally resistant to microbial degradation, a property which may limit microbial remediation options as effective alternatives for clean up of contaminated sites.; Relationships for fundamental interactions between plants and contaminants that dictate uptake, enzymatic processing and sequestration of contaminants by aquatic plants were established. An assay which quantified production of oxygen by plants was developed to quantify plant metabolic activity and inhibition. Uptake of chlorinated phenols depended on plant activity and aqueous phase concentration of contaminant in the protonated form. Therefore, plant activity, contaminant pKa and media pH were established as critical parameters controlling rate of contaminant uptake. A conceptual model was developed which incorporated plant activity and inhibition into a mathematical description of uptake of organic contaminants by aquatic plants. The conceptual model was parameterized using experimental data delineating effect of plant activity, inhibition and speciation on contaminant uptake and the model was verified using independently gathered data. Experimentation with radio-labeled chlorinated phenols established that contaminants were sequestered internal to plants by plant enzymatic processing. 19F NMR was established as a technique to quantify transformation and conjugation products internal to plants and contaminant assimilation by plants and demonstrated that multiple metabolites containing the parent compound were present and quantifiable internal to plants. Finally, fate of plant-sequestered contaminants in an anaerobic bioassay was examined using Desulfitobacterium sp. strain Viet1.; The results of this study address the role of aquatic plants in sequestration of contaminants in surface waters that indicate the potential and limitations of use of aquatic plants in natural and engineered treatment systems.
机译:这项研究探索了水生植物系统中有机污染物的结局,方法是:(i)通过实验建立关系来描述植物对污染物的吸收,吸收和酶促处理,以及污染物对水生植物的抑制作用;(ii)将实验关系纳入概念模型描述了水生植物系统中污染物的归宿。这项研究的重点是水生植物小L. and M. aquaticum与卤代酚的相互作用。 2,4,5-三氯苯酚(2,4,5-TCP)和2,4-二氯苯酚(2,4-DCP)是高毒性和重施除草剂2,4,5-T和2,4的前体-D和详细检查。氯酚通常对微生物降解具有抵抗力,该特性可能会限制微生物修复方法作为清除污染部位的有效替代方法。建立了植物与污染物之间基本相互作用的关系,这些相互作用决定了水生植物对污染物的吸收,酶促处理和螯合。开发了一种量化植物产生的氧气的测定法,以量化植物的代谢活性和抑制作用。氯代酚的吸收取决于植物活性和质子化形式的污染物的水相浓度。因此,植物活性,污染物pKa和培养基pH被确定为控制污染物吸收速率的关键参数。建立了概念模型,将植物活性和抑制作用纳入了水生植物对有机污染物吸收的数学描述中。使用描述植物活性,抑制和物种形成对污染物吸收的影响的实验数据对概念模型进行参数化,并使用独立收集的数据对模型进行验证。用放射性标记的氯化酚进行的实验确定,通过植物酶促处理将污染物隔离在植物内部。建立19F NMR作为量化植物内部转化和缀合产物以及植物对污染物同化的技术,并证明了含有母体化合物的多种代谢物存在且可量化于植物内部。最后,使用脱硫杆菌属(Desulfitobacterium sp。)检测了厌氧生物测定中植物所含污染物的命运。 Viet1。这项研究的结果解决了水生植物在螯合地表水中污染物中的作用,这表明了在自然和工程处理系统中使用水生植物的潜力和局限性。

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