Na-CMC固定化烟曲霉对活性艳蓝KN-R的吸附脱色研究

采用羧甲基纤维素钠(Na-CMC)固定化烟曲霉对活性蒽醌染料活性艳蓝KN-R吸附脱色.通过批式吸附实验探讨了吸附体系的pH值、温度、供氧条件、盐度,固定化小球的粒径、接种量等对吸附脱色效率的影响.结果表明,适合于固定化小球吸附脱色的吸附体系的pH值在弱酸或碱性(4.3～9.0)范围内,不调pH值时(pH=4.3),48h的吸附率为94.5%,pH值为6～9时,48 h的吸附率在98%以上;固定化小球的最佳脱色温度为40℃,该温度下24h的吸附率达94.4%;氧充足情况下(摇床转速调节为50r·min-1)的吸附体系较静止状态能显著提高吸附脱色率;固定化小球脱色过程中能承受一定的盐度,NaCl浓度为0.1%时,吸附脱色效果最好;盐度为2.5%时,48h的吸附率降低至68.4%;粒径为2.0～3.85mm的固定化小球对活性艳蓝KN-R的吸附率相差不大;接种量为3.0%时的吸附脱色效果最好,24h对活性艳蓝KN-R的吸附率达91.0%.在烟曲霉生长期内,固定化小球吸附脱色动力学符合一级动力学方程.     

用Co3O4催化剂光催化氧化活性染料

以沉淀一热解法制备了纳米级Co3O4催化剂,并用X射线衍射仪、红外光谱仪对Co3O4催化剂进行了表征。以300W高压汞灯为光源,研究了Co3O4催化剂对不同活性染料的光催化氧化活性。实验结果表明：在活性染料质量浓度为20mg／L、250mL染料溶液中Co3O4催化剂加入量为150mg、反应2h的条件下,Co3O4催化剂对B—GFF黑、B—RN蓝、K—NR艳蓝3种活性染料溶液的脱色率分别为95％,87％,77％;适当加入酸或碱有利于提高处理效率,反应后染料溶液的pH为7．12～8．37,染料溶液初始pH为10．00时的脱色率最高为100％;Co3O4催化剂具有一定的再利用价值。     

酸改性δ-MnO2去除水中染料的特性和机理

用硫酸对层状δ-MnO2进行改性,以亚甲基蓝和刚果红为目标分子,考察了改性方式、改性条件、接触时间、pH值和温度对改性去除染料的影响.利用原子力显微镜、傅立叶红外光谱和X射线光电子衍射仪对二氧化锰改性前后的表面性质进行了考察,结果表明:改性后的二氧化锰,其表面理化特性均发生了改变,使中性时去除阴离子染料的能力和碱性时去除阳离子染料的能力明显增强.     

水溶性磺化聚苯乙烯在阳离子染料废水处理中的应用

本文采用水溶性磺化聚苯乙烯（ＰＳＳＡ）的助剂,用硫酸铝作混凝剂,对系列含典型阳离子染料垢模拟废水进行脱色试验。试验结果表明：ＰＳＳＡ分子具有较强的助凝作用,令带正电荷的染料离子大量集结于ＰＳＳＡ分子链周围而形成新的聚集体,这些聚集在硫酸铝或碱式氯化铝的作用下会进一步发生凝聚,在控制水溶液中的ｐＨ值接近于７的情况下,硫酸铝絮凝作用使含有染料离子的凝聚体形成钒花,该矾花可经静置沉淀或离心分离而被除去。     

优势菌处理印染废水的工艺及脱色机理研究

采用不完全厌氧－好氧工艺处理印染废水,工程运行前在水解池中投入了主要用于脱色的优势菌群,经３年多的运行,系统的脱色率均稳定在９０％以上。从池中取菌进行分离鉴定,并进行各单株菌脱色能力实验,对其中具有最佳脱色能力的菌株进行偶氮染料活性黑ＫＮＢ的脱色产物的化学分析,从而探讨水解池中染料的脱色机理。结果发现：分离到的１０株菌对试验染料有较好脱色效果,高效液相色谱检测发现产物只有苯胺类物质的存在。该菌的脱色作用主要是破坏了染料的发色基团——偶氮双键。     

水中直接染料的多相催化脱色的试验条件研究

实验结果表明,金属氧化物催化剂与活性炭和过氧化氢配合使用,对直接染料有很高的催化脱色率。反应进行迅速,以直接耐酸大红4BS和直接红棕RN为代表的正交实验表明影响催化脱色作用的主要因素为催化剂,其次是活性炭和过氧化氢。直接深蓝L－3RB,直接铜蓝2R,直接黑L－3BQ,直接耐晒黄RS,直接青莲RB等的最大脱色率为92.9%-99.5%。     

微波诱导催化剂Fe2O3／沸石氧化处理印染废水

以自制改性沸石为催化剂,通过微波诱导氧化技术,对活性嫩黄模拟废水进行氧化处理。采用尿素均匀沉淀包裹法制备Fe2O3／沸石微波诱导催化剂。利用SEM、XRD、IR等分析手段分别对催化剂的表面形态、物相结构等特性进行表征。实验考察了催化剂用量、微波辐射时间、微波辐射功率对活性嫩黄废水的降解效果。结果表明：在催化剂用量3g／L、微波功率900W、辐射时间4min的条件下,对50mg／L活性嫩黄的处理率达到97％。     

Application of 'waste' wood-shaving bottom ash for adsorption of azo reactive dye

The utilization of wood-shaving bottom ash (WBA) for the removal of Red Reactive 141 (RR141), an azo reactive dye, was investigated. WBA/H(2)O and WBA/H(2)SO(4) were made by treating WBA with water and 0.1M H(2)SO(4), respectively, to increase adsorption capacity. Adsorption of RR141 from reactive dye solution (RDS) and reactive dye wastewater (RDW) by WBA/H(2)O and WBA/H(2)SO(4) involved the BET surface area and pore size diameter. Properties of adsorbents, effect of contact time, initial pH of solution, dissolved metals and elution studies indicated that the decolorisation mechanism involved both chemical adsorption and precipitation with calcium ions. In addition, the WBA/H(2)SO(4) surface might contain sulphate-cation complexes that were specific to enhancing dye adsorption from RDW. The adsorption isotherm had a best fit by the Freundlich model. Freundlich parameters showed that WBA/H(2)O used more heterogeneous surface than WBA/H(2)SO(4) and activated carbon for RDW adsorption. A thermodynamic study indicated that RDW adsorption was an endothermic process. The maximum dye adsorption capacities of WBA/H(2)O, WBA/H(2)SO(4) and activated carbon obtained from a Langmuir model at 30 degrees C were 24.3, 29.9, and 41.5mgl(-1), respectively. In addition, WBA/H(2)O and WBA/H(2)SO(4) could reduce colour and high chemical oxygen demand (COD) of real textile wastewater. According to the difficulty in the elution study, it was an environmentally safe disposal of this waste. Therefore, WBA, a waste from combustion of wood shavings, was suitable to be used as an effective adsorbent for azo reactive dye removal.     

染料废水生物膜中酶的作用特性与条件优化

通过对兼氧-好氧染料废水处理系统兼氧生物膜中脱氢酶、脂肪酶和酯酶的活性分析,研究了3种酶的作用特性以及最佳条件优化。试验结果表明,脱氢酶作为一种胞内酶,在出水水样中仍能检测到2.2%的活性存在;82.5%脂肪酶和79.9%的酯酶分布在生物膜中,这说明绝大多数脂肪酶和酯酶是与细胞相连或固定在细胞外多聚絮体基质中。0.4 mmol/L的抑制剂EDTA对脱氢酶活性有促进作用,而对脂肪酶和酯酶的抑制率分别达到59.8%和18.9%。正交试验结果表明,待测3种酶有最大活性的条件均为：温度为60℃,底物浓度为50 μmol/L,pH为8,在优化条件下待测酶活性可达常规作用条件的2.58～6.44倍。各因素对待测酶活性的影响强弱排序为：温度>底物浓度>pH。     

Degradation of anthraquinone dye C.I. Reactive Blue 19 in aqueous solution by ozonation

This study investigated the degradation of anthraquinone reactive dye C.I. Reactive Blue 19 (RB-19) with initial concentration of 100 mg L⁻¹ in aqueous solution by ozone oxidation. The results of UV/VIS and FTIR spectra showed that the anthraquinone structures, nitrogen linkages and amino groups of RB-19 were destroyed under direct ozone reaction. The identification by LC–MS and GC–MS analyses indicated that some organic acids (e.g., phthalic acids) and 1,3-indanone could be the primary degradation products, respectively. The Microtox toxicity of the ozonated RB-19 solution initially increased but subsequently decreased when ozonation time increased. This detoxification accompanied biodegradability enhancement revealed by BOD/COD ratio increasing from 0.15 to 0.33 after 10 min of ozonation.