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The Effect of Natural Organic Matter on UV/Hydrogen Peroxide Treatment and the Effect of UV/Hydrogen Peroxide Treatment on Natural Organic Matter.

机译:天然有机物对UV /过氧化氢的影响以及UV /过氧化氢对天然有机物的影响。

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摘要

Ultraviolet light with hydrogen peroxide (UV/H2O2) produces hydroxyl radicals that degrade organic micro-pollutants. However, radicals react non-selectively with natural organic matter (NOM). This research effort quantified the effect of NOM variation on the efficiency of UV/H 2O2 contaminant destruction, explored the kinetics of hydroxyl radical/NOM reactions, determined the effect of UV/H2O2 on biofilm formation potential, measured UV/H2O2 impact on trihalomethane (TTHM) and haloacetic acid (HAA5) formation potential, and evaluated UV/H2O2 effects on TTHM speciation after chlorination. Granular activated carbon (GAC) adsorption was investigated to improve process efficiency and reduce by-product formation potential without creating brominated THM problems.;A year-long UV/H2O2 pilot study was conducted to study seasonal variations in NOM and multiple GAC breakthrough conditions. Pilot-scale reactors consistently achieved 80% atrazine degradation, allowing comparison of low pressure (LP) and medium pressure (MP) lamps for contaminant destruction efficiency and unintended by-product formation.;The effect of NOM on UV/H2O2 destruction of atrazine, metolachlor, methyl tert-butyl ether (MTBE), methylisoborneol, ibuprofen, gemfibrozil, and 17a-ethynylestradiol was evaluated. UV absorbance scans demonstrated changes in NOM from UV/H2O2 that increased under certain NOM conditions. As NOM increased, electrical energy per order (EEO) requirements for contaminant destruction increased; requirements increased similarly for all contaminants. UV/H2O2 followed by GAC eliminated the contaminants, throughout the year. LP lamps had lower E EO requirements than MP lamps. UV/H2O2 destruction of MTBE was evaluated with bench-scale experiments using waters with varying NOM. Destruction and EEO values correlated well with specific-ultraviolet absorption for pilot-scale and bench-scale experiments. Changes in the kinetics of NOM/hydroxyl radical reactions were observed with different types of NOM. Total assimilable organic carbon (AOC) concentration increased through UV/H 2O2 by 14 to 33%, more with conventionally treated (CONV) reactor influent than with Post-GAC influent. The AOC concentration increases generated by MP and LP processes were similar. The Spirillum strain AOC increased through UV/H2O2 50 to 65% due to formation of smaller more soluble compounds, e.g., organic acids. Pseudomonas fluorescens strain AOC concentration increased when CONV water served as pilot influent, but not when Post-GAC water was used. GAC effluent streams receiving UV/H 2O2 pretreatment produced biofilms with greater heterotrophic plate counts than controls. The GAC effluent stream following the MP reactor produced the most viable biofilm.;Three-day simulated distribution system (SDS) TTHM concentration increased through the UV/H2O2 reactors (20 to 118%). Post-GAC reactor influent produced lower 3-day SDS TTHM concentration than CONV influent after UV/H2O2. Three-day SDS HAA5 concentration increased for CONV UV/H2O2 pilot influent, but not for Post-GAC influent. No difference in 3-day SDS DBP concentrations was observed between LP and MP processes. Brominated THMs are more toxic than chloroform, thus minimizing them is desirable. UV/H2O2 did not shift 3-day SDS THMs towards the brominated species. UV/H2O2 increased the TTHM contribution of 3-day SDS chloroform by 7 to 13%, while 3-day SDS bromoform TTHM contribution decreased by 0.5 to 7%. GAC adsorption after UV/H2O2 insignificantly increased 3-day SDS bromoform concentration from 0.01 to 0.02 mumole/L.;UV/H2O2 can be used with GAC for excellent contaminant removal and minimal adverse effects.
机译:含有过氧化氢(UV / H2O2)的紫外线会产生羟基自由基,降解有机微污染物。但是,自由基与天然有机物(NOM)发生非选择性反应。这项研究工作量化了NOM变化对UV / H 2O2污染物破坏效率的影响,探索了羟基自由基/ NOM反应的动力学,确定了UV / H2O2对生物膜形成潜力的影响,测量了UV / H2O2对三卤甲烷的影响( TTHM)和卤乙酸(HAA5)的形成潜力,并评估了氯化后UV / H2O2对TTHM形态的影响。对颗粒活性炭(GAC)吸附进行了研究,以提高工艺效率并减少副产物形成的可能性,而不会产生溴化THM问题。;进行了为期一年的UV / H2O2初步研究,以研究NOM的季节性变化和多种GAC突破条件。中试规模的反应堆始终实现80%的at去津降解,可以比较低压(LP)和中压(MP)灯的污染物破坏效率和意外副产物的形成。NOM对UV / H2O2破坏at去津的影响,评估了异丙甲草胺,甲基叔丁基醚(MTBE),甲基异冰片醇,布洛芬,吉非贝齐和17a-乙炔基雌二醇的含量。紫外线吸收扫描显示,在某些NOM条件下,UV / H2O2中NOM的变化增加。随着NOM的增加,销毁污染物的每订单电能(EEO)要求也增加了;所有污染物的需求量均以类似方式增加。全年使用UV / H2O2和GAC消除了污染物。 LP灯的E EO要求低于MP灯。使用具有不同NOM的水,通过实验室规模的实验评估了MTBE的UV / H2O2破坏。在中试规模和实验规模的实验中,破坏度和EEO值与特定紫外线吸收密切相关。观察到不同类型的NOM的NOM /羟基自由基反应动力学的变化。通过UV / H 2O2吸收的总有机碳(AOC)浓度增加了14%至33%,传统处理(CONV)反应器进水比GAC后进水高。 MP和LP工艺产生的AOC浓度增加相似。螺旋藻菌株的AOC通过UV / H2O2的含量增加了50%至65%,这是由于形成了较小的更易溶的化合物(例如有机酸)。当使用CONV水作为先导进水时,荧光假单胞菌菌株AOC浓度增加,但使用Post-GAC水时则不增加。接受UV / H 2O2预处理的GAC废水流产生的生物膜的异养菌板数比对照多。 MP反应器之后的GAC流出物流产生了最可行的生物膜。三天模拟分配系统(SDS)TTHM浓度通过UV / H2O2反应器而增加(20%至118%)。 GAC后反应器进水比UV / H2O2处理后CONV进水产生的三天SDS TTHM浓度低。 CONV UV / H2O2先导进水的三天SDS HAA5浓度增加,但GAC后进水则没有。在LP和MP过程之间,未观察到3天SDS DBP浓度的差异。溴化THM比氯仿有更高的毒性,因此希望将其降至最低。 UV / H2O2不会使3天的SDS THM移向溴化物种。 UV / H2O2将3天SDS氯仿的TTHM贡献提高了7%至13%,而3天SDS溴仿TTHM的贡献降低了0.5至7%。 UV / H2O2处理后的GAC吸附将3天SDS溴仿浓度从0.01毫摩尔/升微升至0.02 mol /L。UV/ H2O2可与GAC一起使用,以实现优异的污染物去除和最小的不利影响。

著录项

  • 作者

    Metz, Deborah H.;

  • 作者单位

    University of Cincinnati.;

  • 授予单位 University of Cincinnati.;
  • 学科 Engineering Environmental.
  • 学位 Ph.D.
  • 年度 2012
  • 页码 278 p.
  • 总页数 278
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

  • 入库时间 2022-08-17 11:43:21

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