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991.
采用涡流空化(SC)/Fenton协同降解溶液中活性艳红K-2BP,探讨了H2O2、Fe2+、pH、涡流压力以及活性艳红K-2BP初始浓度对SC/Fenton降解效果的影响。结果表明,H2O2和Fe2+的浓度过高或过低都会降低活性艳红K-2BP的降解率,低pH环境有助于活性艳红K-2BP的降解,活性艳红K-2BP的降解率随涡流压力的增大而升高,随其初始浓度的增加而降低。当活性艳红K-2BP初始质量浓度为10mg/L,H2O2质量浓度为165mg/L,Fe2+摩尔浓度为1.5×10-4mol/L,pH为4.0,涡流压力为0.8MPa时,活性艳红K-2BP降解率可达91.81%。 相似文献
992.
针对TiO2光催化反应中易出现电子-空穴对(e--h+)的复合、而Fenton技术又面临铁污泥的问题,向TiO2光催化反应中加入零价铁(Fe0)。通过调节溶液pH,使Fe0缓释Fe2+,且反应之后的pH仍能满足TiO2光催化反应所需。溶液中的Fe2+,一方面能减弱TiO2光催化产生的e--h+的复合,提高TiO2光催化反应的效率;另一方面,在紫外灯照射下也可以起到光Fenton降解作用。研究结果表明,Fe0共存下TiO2光催化对废水的降解率高于单独使用TiO2光催化或光Fenton对废水的降解率。对Fe0共存下TiO2光催化降解废水的褪色率的动力学研究表明,该反应属于三级动力学反应,且其对有机物的降解具有TiO2光催化和光Fenton加合增效的效果。 相似文献
993.
微波-Fenton氧化-PAFSi絮凝法处理含油废水 总被引:2,自引:0,他引:2
采用微波-Fenton氧化-PAFSi絮凝法处理含油废水,结果表明,200mL水样先经微波辐射6rnin,在pH=2,H2O2(30%)3.5g/L,Fe2+ 1.3g/L的条件下氧化4h后,采用聚硅酸铝铁(Al:Fe:Si=10:2:1)和聚丙烯酰胺在pH:8时进行絮凝实验,处理后废水浊度、SS、COD、含油量和色度分别降低了99.46%、96.66%、91.94%、97.97%和95.00%,且经处理后废水的BOD5/COD由原水的0.04提高到0.53。实验还分析了含油废水的降解机理。 相似文献
994.
采用Fenton氧化开展了对高浓度造纸废水深度处理的中试实验,对Fenton氧化的COD的去除效果,各药剂加药量及成本,排泥量和装置运行的稳定性等进行探讨和分析,结果表明,一级Fenton氧化的COD去除率可达到90%以上,出水COD在100 mg/L左右,总加药成本在6元左右,排泥量约为1~1.2 kg/t废水;二级Fenton氧化的COD去除率在96%左右,出水COD小于60 mg/L,总加药成本在8元左右,排泥量约为1.15~1.4 kg/t废水,验证了Fenton氧化用于高浓度造纸废水深度处理达到新的排放标准的可行性。 相似文献
995.
微波-Fenton 氧化-PAFSi 絮凝法处理含油废水简 总被引:1,自引:0,他引:1
采用微波-Fenton氧化-PAFSi絮凝法处理含油废水,结果表明,200 mL水样先经微波辐射6 min,在pH=2,H2O2(30%)3.5 g/L,Fe2+ 1.3 g/L的条件下氧化4 h后,采用聚硅酸铝铁(Al:Fe:Si=10:2:1)和聚丙烯酰胺在pH=8时进行絮凝实验,处理后废水浊度、SS、COD、含油量和色度分别降低了99.46%、96.66%、91.94%、97.97%和95.00%,且经处理后废水的BOD5/COD由原水的0.04提高到0.53。实验还分析了含油废水的降解机理。 相似文献
996.
Fenton氧化法在处理难降解有机污染物时具有独特的优势,是一种很有应用前景的废水处理技术。在阐述传统Fenton氧化、光Fenton氧化、电Fenton氧化技术的基础上,介绍了三种氧化技术在难降解有机废水处理中的应用现状,并对其在废水处理中的优势、存在问题和研究方向作出了系统评述。 相似文献
997.
为了研究车载巡回处理装置对小城镇垃圾渗滤液的处理效果,采用自制的UV-Fenton试验装置研究了pH值、FeSO_4剂量、反应时间等因素对处理效果的影响,结果表明:最佳pH值为4.0,进水中COD为825 mg/L时,FeSO_4和H_2O_2的投加量分别为0.008 mol/L和0.08 mol/L,此时COD去除率72.22%,出水COD为216 mg/L;随着FeSO_4投加量缓慢增加到一定程度后转而下降,FeSO_4最佳投加量为0.008 mol/L;不同H_2O_2和Fe~(2+)配比对COD去除效果具有影响,(10:1)时为最佳配比。经过氨吹脱和混凝沉淀预处理的渗滤液采用UV/Fenton处理工艺,出水中COD可以达到《生活垃圾填埋场污染控制标准》(GB 16889-1997)中二级标准。 相似文献
998.
Influence of pyrene combination state in soils on its treatment efficiency by Fenton oxidation 总被引:1,自引:0,他引:1
Interactions of hydrophobic organic compounds (HOCs) with soil organic matter (SOM) determine their combination state in soils, and therefore strongly influence their mobility, bioavailability, and chemical reactivity. Contact time (aging) of an HOC in soil also strongly influences its combination state and environmental fate. We studied Fenton oxidation of pyrene in three different soils to reveal the influences of SOM, contact time, and combination state on the efficiency of vigorous chemical reactions. Pyrene degradation efficiency depended strongly on the dose of oxidant (H(2)O(2)) and catalyst (Fe(2+)); the greatest degradation was achieved at an oxidant to catalyst molar ratio of 10:1. Pyrene degradation differed among the three soils, ranging from 65.4% to 88.9%. Pyrene degradation efficiency decreased with increasing SOM content, and the aromatic carbon content in SOM was the key parameter. We hypothesize that pyrene molecules that combine with the compact net structure of aromatic SOM are less accessible to Fenton oxidation. Furthermore, pyrene degradation efficiency decreased considerably after aged for 30 days, but further aging to 60 and 180 days did not significantly change degradation efficiency. The Fenton oxidation efficiency of pyrene in both unaged and aged soils was greater than the corresponding desorption rate during the same period, perhaps because Fenton reaction can make pyrene more accessible to the oxidant through the enhancement of HOCs' desorption by generating reductant species or by destroying SOM through oxidation. 相似文献
999.
In this paper, the utilisation of zeolites synthesised from fly ash (FA) and related co-disposal filtrates as low-cost adsorbent material were investigated. When raw FA and co-disposal filtrates were subjected to alkaline hydrothermal zeolite synthesis, the zeolites faujasite, sodalite and zeolite A were formed. The synthesised zeolites were explored to establish its ability to remove lead and mercury ions from aqueous solution in batch experiments, to which various dosages of the synthesised zeolites were added. The test results indicated that when increasing synthesised zeolite dosages of 5-20 g/L were added to the acid mine drainage (AMD) wastewater, the concentrations of lead and mercury in the wastewater were reduced accordingly. The lead concentrations were reduced from 3.23 to 0.38 and 0.17 microg/kg, respectively, at an average pH of 4.5, after the addition of raw FA zeolite and co-disposal filtrate zeolite to the AMD wastewater. On the other hand, the mercury concentration was reduced from 0.47 to 0.17 microg/kg at pH=4.5 when increasing amounts of co-disposal filtrate zeolite were added to the wastewater. The experimental results had shown that the zeolites synthesised from the co-disposal filtrates were effective in reducing the lead and mercury concentrations in the AMD wastewater by 95% and 30%, respectively. 相似文献
1000.
Nanoscale bimetallic Ni/Fe particles were synthesized from the reaction of sodium borohydride (NaBH4) with reduction of Ni^2+ and Fe^2+ in aqueous solution. The obtained Ni/Fe particles were characterized by TEM (transmission electron microscope), XRD (X-ray diffractometer), and N2-BET. The dechlorination activity of the Ni/Fe was investigated using p-chlorophenol (p-CP) as a probe agent. Results demonstrated that the nanoscale Ni/Fe could effectively dechlorinate p-CP at relatively low metal to solution ratio of 0.4 g/L (Ni 5 wt%). The target with initial concentration ofp-CP 0.625 mmol/L was dechlorinted completely in 60 rain under ambient temperature and pressure. Factors affecting dechlorination efficiency, including reaction temperature, pH, Ni loading percentage over Fe, and metal to solution ratio, were investigated. The possible mechanism of dechlorination ofp-CP was proposed and discussed. The pseudo-first- order reaction took place on the surface of the Ni/Fe bimetallic particles, and the activation energy of the dechlorination reaction was determined to be 21.2 kJ/mol at the temperature rang of 287-313 K. 相似文献