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191.
对纳氏试剂的两种配制方法在配制难易和含汞量、空白吸光度、校准曲线、检出限、精密度和加标回收率等方面作了比较,得出KI、HgCl2和KOH配制的纳氏试剂与KI、HgI2和NaOH配制的纳氏试剂相比,配制虽麻烦,但含汞量、空白吸光度和检出限均较低,而灵敏度、精密度和加标回收率却较高,可作为配制纳氏试剂的首选方法。而KI、HgI2和NaOH配制的纳氏试剂可用于应急监测中。 相似文献
192.
研究不同磁化时间、不同磁场强度以及催化氧化体系中各种影响因素对表面活性剂污水CODcr的去除率的影响。结果表明:在pH值3,H2O2加入量为0.5%(体积比),FeSO4.7H2O浓度为3 000 mg/L,反应10min,去除率达69.8%。在相同实验条件下,外加磁场强度分别为235.6 mT、357.3 mT、427.8 mT,CODcr的去除率可提高3.5%、8.4%、10.5%。 相似文献
193.
The low biodegradability of polyphenolic compounds typically found in olive processing indicated that biological treatment is not always successful in the treatment of olive oil mill wastewater in term of COD removal. In this study the results of investigations on the applicability of Fenton‘s reagent in the treatment of this effluent were discussed. The efficiency of this method was determined. 86% of removal COD was obtained using 5 mol H2O2 and 0.4 mol Fe^2 per liter of crude OMW. The main parameters that govem the complex reactive system, i.e., time, pH, [H2O2] and [Fe(ll)] were studied. 相似文献
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196.
Fenton试剂预处理高浓度丁腈胶乳生产废水 总被引:1,自引:1,他引:0
采用Fenton试剂预处理高浓度丁腈胶乳生产废水,确定最佳操作条件为:[H2O2]= 2 664 mg/L,[Fe2 ]=219 mg/L,初始pH=5.0,25 ℃下反应60 min,此条件下废水COD去除率可达80%以上.经正交试验得出各因素对废水COD去除率的影响顺序为:pH>[H2O2]>[Fe2 ]>反应时间.动力学研究表明,在此最佳操作条件下,反应近似符合一级反应动力学,动力学方程ln(C0/C)=0.018 7t 0.783 1,反应速率常数k=0.018 7 min-1,半衰期t 1/2=37.1 min. 相似文献
197.
酸析-Fenton试剂氧化-混凝法处理制浆废水 总被引:1,自引:1,他引:0
用酸析-Fenton试剂氧化-混凝法对自偶氧化清洁制浆废水进行预处理,考察了各种因素对处理效果的影响。最佳处理条件:酸析时的废水pH为3.0;酸析后上层清液无需调节pH,加水稀释至COD为2000mg/L后进行Fenton试剂氧化,H2O2加入量为84.56mmol/L,FeS04加入量为8.44mmol/L,反应时间60min;混凝时Ca(OH):加入量为2g/L。最终出水的COD为577.20mg/L(COD去除率为71.14%),色度为36倍,pH为8.60。 相似文献
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199.
Chemical oxidation of cable insulating oil contaminated soil 总被引:2,自引:0,他引:2
Leaking cable insulating oil is a common source of soil contamination of high-voltage underground electricity cables in many European countries. In situ remediation of these contaminations is very difficult, due to the nature of the contamination and the high concentrations present. Chemical oxidation leads to partial removal of highly contaminated soil, therefore chemical oxidation was investigated and optimized aiming at a subsequent bioremediation treatment. Chemical oxidation of cable oil was studied with liquid H2O2 and solid CaO2 as well as permanganate at pH 1.8, 3.0 and 7.5. Liquid H2O2 most effectively removed cable oil at pH 7.5 (24%). At pH 7.5 poor oil removal of below 5% was observed with solid CaO2 and permanganate within 2 d contact time, whereas 18% and 29% was removed at pH 1.8, respectively. A prolonged contact time of 7 d showed an increased oil removal for permanganate to 19%, such improvement was not observed for CaO2.Liquid H2O2 treatment at pH 7.5 was most effective with a low acid use and was best fit to a subsequent bioremediation treatment. To further optimize in situ chemical oxidation with subsequent bioremediation the effect of the addition of the iron catalyst and a stepwise liquid H2O2 addition was performed. Optimization led to a maximum of 46% cable oil removal with 1469 mM of H2O2, and 6.98 mM Fe(II) chelated with citric acid (H2O2:FeSO4 = 210:1 (mol mol−1). The optimum delivery method was a one step addition of the iron catalyst followed by step wise addition of H2O2. 相似文献
200.