Fenton试剂处理青霉素废水实验研究

以青霉素废水为研究对象 ,初步探讨了 Fenton试剂处理有毒有机废水时各影响因素的作用机制 ,通过实验确定了 Fenton试剂氧化降解青霉素废水的适宜操作条件为 :CODCr为 30 0 0 mg/L左右的青霉素废水 ,p H为 6.0、H2 O2 (30 % )投加量为 0 .6% (体积分数 )、Fe SO4 · 7H2 O投加量为 0 .2 % (质量分数 )、反应时间为 lh,此条件下废水 CODcr的去除率可达 70 % ,而且该方法设备简单 ,易于下一步实现工业放大 ,是一种有较好开发前景的处理青霉素废水工艺。     

土壤生态系统微量元素的生物有效性研究现状

土壤中植物必需的微量营养元素的供给以及有害元素的毒性大小并不仅仅与元素的总量有关,而取决于元素的有效性。文章论述了元素生物有效性的含义,介绍了元素有效性的研究方法,即连续偏提取法和单提取法,并对一些相关问题进行了深入的分析讨论。     

Fenton试剂处理酸性染料废水的研究

采用Ｆｅｎｔｏｎ试剂处理酸性染料废水，在ｐＨ＝３，〔ＦｅＳＯ４〕＝４０ｍｇ／Ｌ，〔Ｈ２Ｏ２〕＝８００ｍｇ／Ｌ时，酸性媒介漂蓝废水的色度及ＣＯＤ去除率分别达９８．６％和８０．１％。     

Fe(Ⅲ,Ⅱ)/H2O2体系中Fe(Ⅲ)水解特征的对比

利用Fe Ferron逐时络合比色法对类Fenton与Fenton体系中Fe(Ⅲ )水解形态的转化规律进行了比较 .结果表明 ,水解度越高 ,两体系中Fe(Ⅲ )的水解速度也越快 ,但水解度相同时 ,与Fenton体系相比 ,类Fenton反应生成的Fe(Ⅲ )的水解速率要低 ,且Feb 所占比例也较少 .与Fenton体系一致 ,类Fenton体系中的Fe(Ⅲ )水解速率随H2 O2 浓度的增加而减缓     

Fenton法处理线路板生产废水中有机物质

比较传统Fenton法和电解Fenton法对线路板生产中高浓度有机废水的处理效果。根据模拟实际生产情况，确定健鼎公司电解Fenton法的最佳处理条件。     

太阳光助Fenton体系氧化降解苯酚废水的研究

探讨了太阳光助Fenton体系对苯酚的氧化降解。结果表明，太阳光能有效地增强Fenton试剂对苯酚的氧化降解，在晴天较强太阳光照下，Fenton试剂可在较短时间内使较高浓度的苯酚完全矿化。反应体系的初始pH值及Fe^2 用量均对苯酚的氧化降解有明显影响，反应的适宜pH值在3—4的酸性范围内；适量Fe^2 参与的太阳光—Fenton反应有助于苯酚的降解，但过高的Fe^2 用量反而不利于苯酚的降解。实验结果还表明，采用分批多次投加的方式可明显提高氧化剂H202的利用效率，降低H202的消耗量；苯酚废水降解的主要中间产物为苯醌和有机酸；一定程度的太阳光—Fenton预氧化处理可使废水的BOD5／C02cr比值由0.10捉高到0.32，可生化性明显提高。     

2-Chlorophenol oxidation kinetic by photo-assisted Fenton process

Experimental data are presented to test and validate a kinetic model for the oxidation of 2-chlorophenol wastewater by photo-assisted Fenton process. The data showed that this process had produced good effects under acidic conductions. Up to 90% 2-chlorophenol was removed after 90-minute reaction time with H2O2 of 25% CODCr. in, while in UV/H2O2 system ordy 16.8% 2-chlorophenol was removed after one hour treatment. The optimal pH in this reaction occurred between pH 3.0 and pH 4.0. The reaction kinetics for photo-assisted Fenton process experimented in this research was investigated. Kinetic models were proposed for the treatment of 2-chlorophenol wastewater. The reaction was found to follow the 2nd order. The equations of reaction kinetics are as follows:-d[RH]/dt=KRH[RH][H2O2]0exp(-KH2o2t);-d[CODCr]/dt=KCODCr[CODCr][H2O2]0exp(-K′t).The prediction of the models was found to be in a good agreement with experimental results, thus confimfing the proposed reaction mechanism.     

Treatment of 2-phenylamino-3-methyl-6-di-n-butylaminofluoran production effluent by combination of biological treatments and Fenton＇s oxidation

High strength refractory organic stream is produced during the production of 2-phenylamino-3-methyl-6-di-n-butylaminofluoran （One Dye Black 2, abbr. ODB 2）, a novel heat-sensitive material with a promising market. In this study, a combination of acidificationprecipitation, primary biological treatment, Fenton＇s oxidation and another biological treatment was successfully used for the removal of COD from 18000-25000 mg/L to below 200 mg/L from the ODB 2 production wastewater in a pilot experiment. A COD removal of 70%-80% was achieved by acidification-precipitation under a pH of 2.5-3.0. The first step biodegradafion permitted an average COD removal of 70% under an hydraulic residence time （HRT） of 30 h. By batch tests, the optimum conditions of Fenton＇s oxidation were acquired as： Fe^2＋ dose 6.0 mmol/L; H2O2 dose 3000 mg/L; and reaction time 6 h. The second step biological treatment could ensure an effluent COD below 200 mg/L under an HRT of 10 h following the Fenton＇s treatment.     

Fenton法氧化降解聚乙烯醇的机制

为深入了解Fenton法氧化降解聚乙烯醇（PVA）的机制，通过考察反应过程中COD、BOD5、总有机碳及pH等随反应时间的变化，研究了聚乙烯醇Fenton氧化降解过程的特点，结果表明，当PVA被Fenton试剂氧化时，可生成大量CO2，同时生成酸性中间产物。进一步分析认为，当Fenton试剂中H2O2不足景时PVA氧化的中间产物以醛为主，而当H2O2足量时醛会被继续氧化生成有机酸，最终COD去除率达到80％。     

A study on oxidative degradation of polyacrylamide in wastewater with UV/FENTON/C4H4O62−

The degradation of polyacrylamide (PAM) in simulate wastewater was studied in UV/Fenton/C₄H₄O₆^2? system. The factors such as molecular ratio of H₂O₂/Fe²⁺/C₄H₄O₆^2?, pH, and the dosage of Fenton reagent that could affect the PAM degradation in the UV/Fenton/C₄H₄O₆^2? system were investigated. The experimental results showed that adding C₄H₄O₆^2? to UV/Fenton system could form photosensitive ferrous complexes, which led to higher degradation efficiency of PAM. The degradation rate of PAM could be up to 95.2% under the following conditions: the concentration of H₂O₂, Fe²⁺, and C₄H₄O₆^2? were 22.5, 2.25, and 2.25 mmol/L, respectively (i.e., molecular ratio of H₂O₂/Fe²⁺/C₄H₄O₆^2? was 10:1:1), the pH value was 3.0.