复合脱色絮凝剂的制备及其在活性艳红X-3B染料废水处理中的应用

以双氰胺和甲醛为主原料,在添加改性剂的条件下制备了改性双氰胺-甲醛缩聚物,并直接与硫酸亚铁复合成脱色絮凝剂;以活性艳红X-3B染料废水的脱色率和CODCr去除率为考核指标,探讨了硫酸亚铁投加方式、复合质量比、pH等因素对活性艳红X-3B处理效果的影响。研究结果表明,在一定投加量下,复合脱色絮凝剂处理活性艳红X-3B染料废水的脱色率和COD去除率分别为99%和约75%左右。     

加压溶氧光催化反应器降解活性艳红X-3B

探讨了加压溶氧条件对活性艳红X-3B的降解与脱色的作用,考察了加压条件下pH值,TiO2投加量及温度等对活性艳红X-3B降解的影响.结果表明,加压条件与常压条件下变化趋势基本一致.加压充氧有助于活性艳红X-3B的降解与脱色,加压充N2对反应基本没有作用,说明增加活度不是关键因素,加压使溶液中溶解氧增加是导致活性艳红X-3B降解与脱色的主要原因.光催化降解过程,发色基团最易被打碎,60min内降解效果显著,而萘环和苯环降解效果不十分明显.CODCr的降解与色度的褪除成正相关,脱色率越高,COD的降解率也越高.     

紫外强化湿式催化过氧化氢氧化降解活性艳红X-3B的实验及机理分析

比较湿式催化过氧化氢氧化(CWPO)和光催化联合湿式催化过氧化氢氧化(UV-CWPO)对活性艳红X-3B的处理效果,结果发现后者具有较大的优势,反应150 min后,染料脱色率分别为84.10%和99.28%.动力学实验表明,两者均符合一级反应动力学方程,且相同反应温度下,UV-CWPO工艺表观动力学系数为CWPO工艺的1.64—2.75倍;两者表观活化能Ea分别为40.24 kJ·mol-1和32.79 kJ·mol-1,UV-CWPO工艺具有更低的反应活化能,意味着该工艺下染料分子更容易氧化为各种中间体,进而引起染料脱色.比较CWPO工艺和UV-CWPO工艺反应机理,发现两者在链的引发期不同,并通过叔丁醇作为羟基自由基捕获剂证实前者羟基自由基(·OH)产生量较后者更少.利用GC-MS检测分析CWPO工艺和UV-CWPO工艺降解活性艳红X-3B过程中产生的中间产物,结果表明两者产生了相同的中间产物,但是前者产生量明显更少,这说明UVCWPO工艺对活性艳红X-3B降解更充分.     

酵母菌株Pseudozyma rugulosa对合成染料脱色的初步研究

通过筛选实验,从土壤中分离出一株对活性艳红KBP具有明显脱色效果的酵母菌株,鉴定为Pseudozymarugulosa.采用含50mg·l-1活性艳红K2BP的液体培养基同步培养脱色,发现该菌株在9h时对活性艳红K2BP的脱色率为99%.此外,该菌株对另外九种染料的脱色率在22%—98%之间.其中,对偶氮染料——弱酸艳红B、活性黑KNB和活性红M3BE的脱色率都达到了96%以上,对三苯甲烷染料——酸性媒介漂蓝B的脱色率达到了89%.     

曲霉菌丝球HX对偶氮染料的吸附脱色

采用富积和驯化方法选育出的曲霉菌丝球HX对不同种类染料表现出高效吸附性能，可在12h内完全吸附200mg／L的直接染料、分散染料及活性黄X-R的颜色，并且研究了碳源质量浓度、氮源质量浓度、盐度、培养条件及优化条件组合对菌丝球HX吸附活性艳红X-3B的影响，结果表明：随碳源质量浓度的增加，吸附率相应增加，质量浓度为10．0g／L以上时，72h及以上的吸附率大于92．3％；氮源质量浓度高于0．75g／L时对吸附率影响不大；随盐度增加，染料吸附率有所下降．在温度为25～35℃、染料培养基pH为5．0～7．0、供氧充足的条件下吸附率较高．在所筛选的最佳吸附条件下，菌丝球HX对活性艳红X-3B表现出了更好的吸附效果．图6表3参9     

壳聚糖/膨润土复合絮凝剂处理染料废水的研究

利用壳聚糖/钠基膨润土复合絮凝剂对活性艳红X3B等11种染料模拟废水及实际印染废水进行絮凝脱色处理。考察了复合絮凝剂投加量、pH值、搅拌速率、搅拌时间等因素对模拟染料废水絮凝脱色的影响。结果表明,在染料浓度为100 mg.L-1,pH为5的条件下,复合絮凝剂投加量为1.25 g.L-1时,3种质量比的复合絮凝剂对活性艳红X3B的脱色率分别达到75%、90%和97%以上;质量比为1∶10的壳聚糖/钠基膨润土复合絮凝剂,对其它活性、还原性、分散性、水溶性等8种印染厂常用染料也具有很好的絮凝脱色作用,脱色率均可达94%以上。对印染废水处理厂进水口废水和经过A/O处理后废水的色度去除率和COD去除率分别可以达到81.05%、83.74%和53.21%、41.22%,具有一定的应用前景。     

絮凝剂P(AM-DMC)对活性艳红K-2BP的脱色作用

絮凝剂P(AM-DMC)对染料活性艳红K-2BP具有很好的脱色及去除CODCr性能,脱色率和CODCr去除率分别为97.18%、75.7%。脱色效果受絮凝剂用量、电荷密度、特性粘度、外加盐浓度及溶液pH值影响。红外光谱、可见吸收光谱及电荷量分析表明,P(AM-DMC)对活性艳红K-2BP的絮凝脱色过程中电荷中和起着重要作用,絮凝剂分子中的—N+(CH3)结构与染料分子中的-SO3-发生化学反应,同时也有分子间氢键形成,从而使水中染料分子聚集沉降。     

中性条件下超声波/零价铁协同降解活性艳红X-3B

考察了中性条件下超声波降解、零价铁还原及超声波-零价铁联用对活性艳红X-3B模拟废水的降解效果,通过对比降解过程中UV-Vis光谱的变化,探讨了超声波-零价铁协同处理活性艳红X-3B的可行性.结果表明,在中性条件下超声波对活性艳红X-3B降解缓慢,经过25min辐射后,活性艳红X-3B的分解率不足7.5%;零价铁直接还原速率较慢,反应25min后,活性艳红X-3B的分解率仅为48.82%;"超声波/零价铁"对降解活性艳红X-3B有明显的协同效应,25min后分解率达99.42%(600W),反应符合准一级动力学过程.与零价铁直接还原相比,在200W,400W和600W超声波的协同作用下,X-3B降解的表观反应速率常数分别提高了2.12,2.76和4.00倍,半衰期相应缩短.另外,添加H2O2会抑制协同效应.     

一株染料脱色酵母菌的鉴定及脱色特性

从土壤中分离到一株活性艳红K-2BP脱色酵母菌株Y-63,根据其生理生化特征和26S rRNA基因序列相似性分析,鉴定为Pseudozyma rugulosa.该菌在16 h内对100 mg/L的活性艳红K-2BP脱色率为94%,其机理属于降解脱色.该染料脱色的最佳接种量(φ)应不低于5%,最适pH在4～9之间,(NH4)2SO4浓度(w)不低于0.1%,葡萄糖浓度(w)不低于0.2%.此外,该菌株对其它9种50 mg/L的染料(活性艳蓝X-BR、媒介漂蓝B、活性翠蓝KN-G、酸性媒介黄GG、媒介红S-80、依加仑蓝FBL 200%、弱酸艳红B、活性黑KN-B和活性红M-3BE)的脱色率在10%～96%之间.该研究表明酵母Y-63在染料废水的处理上具有较好的应用潜能.     

JAZ型絮凝剂对活性染料的絮凝效果

本文介绍了新近开发的ＪＡＺ絮凝凝剂地水样中活性艳红Ｋ－２ＢＰ，活性紫Ｈ－２Ｒ和活性黑Ｋ－ＢＲ染料的絮凝效果及ＰＨ值和投药比对脱色率的影响。在中性和弱酸性中絮凝效果好。投药比增大脱色率增加。对活性艳红和活性紫，起始浓度增加则达到８８．５％脱色率的投药比降低。对三种活性染料配水和活性 染料配水和活性黑染料生产水脱色率均可达到９９％，处理液残余色度在２０倍以下。     

零价铁还原降解活性染料

在分别通氮气,不通氮气和曝气的情况下,在水溶液中用零价铁还原降解活性染料。实验发现：在不同的氛围中,活性染料的降解程度不同,其降解程度为：暴气〉不通氮气〉通氮气。在不同通氮 和曝气的条件下,活性染料的降解过程中有黄色絮状沉淀生成,经红外光谱鉴定为三聚氯氰的取代产物。     

新型双槽光电化学反应器对活性艳红的降解研究

用热氧化法制备了TiO2/Ti薄膜电极,并用XRD和AFM对TiO2/Ti薄膜电极的晶形和表面形貌进行了表征。结果表明：热氧化法制备的TiO2主要为锐钛型纳米颗粒,直径在40 nm左右。设计了一种新型双槽光电化学反应器,用于废水的处理。以热氧化法制备的TiO2/Ti薄膜电极为阳极进行光电催化反应,同时以石墨电极为阴极用于产生双氧水,并与紫外光组成UV/H2O2体系。考察了双槽反应器中活性艳红X-3B在不同条件下的降解效果。降解结果表明：在新型反应器的阴阳两极槽中,活性艳红不仅在TiO2/Ti阳极槽中被降解,而且在石墨阴极槽中也得到降解;活性艳红在酸性条件下的降解效果最好;相对于单纯的电化学氧化和光催化,光电化学协同作用对X-3B的降解效果最好。     

A simple and cheap method for preparation of coupled ZrO2/ZnO with high photocatalytic activities

The objective of this study was to prepare a new photocatalyst with high activities for degradation of organic pollutants. Coupled ZrO₂/ZnO photocatalyst was prepared with a simple precipitation method with cheap raw materials zinc acetate and zirconium oxychloride, and was characterized by X-ray diffraction (XRD) and transmission electron microscopy (TEM). Reactive brilliant red X-3B was used as a model compound to investigate the photocatalytic activity of synthesized catalysts in water under 254 nm UV irradiation. Results show that the optimal calcination temperature and coupling molar ratio of Zr were 350°C And 2.5%, respectively. At the calcination temperature of 350°C, ZrO₂ was dispersed on the surface of hexagonal ZnO in the form of amorphous clusters. The particle size of ZrO₂/ZnO decreased with the decrease of calcination temperature and the increase of Zr coupling amount. ZrO₂/ZnO has better photocatalytic activity for degradation of reactive brilliant red (RBR) X-3B than pure ZnO and P25-TiO₂.     

七种染料对鲤鱼肝微粒体芳烃羟化酶的诱导

以鲤鱼肝微粒体为实验体系,研究了七种染料化合物对其芳烃羟化酶（AHH）的诱导,发现七种染料都可诱导AHH的活性,随染料浓度增大AHH的活性升高。七种染料对AHH活性诱导能力大小为：酸性红B＞派拉丁蓝RRN＞普拉红B＞活性艳红K－2BP＞活性艳红K－2G,媒介大红S－80＞分散红E－4B,与其毒性大小相关。     

Fe-Mn-sepiolite as an effective heterogeneous Fenton-like catalyst for the decolorization of reactive brilliant blue

A study of the decolorization of reactive brilliant blue in an aqueous solution using Fe-Mn-sepiolite as a heterogeneous Fenton-like catalyst has been performed. The Fourier transform infrared (FTIR) spectra of the catalyst showed bending vibrations of the Fe-O. The X-ray diffraction (XRD) patterns of the catalyst showed characteristic diffraction peaks of α-Fe₂O₃, γ-Fe₂O₃ and MnO. A four factor central composite design (CCD) coupled with response surface methodology (RSM) was applied to evaluate and optimize the important variables (catalyst addition, hydrogen peroxide dosage, initial pH value and initial dye concentration). When the reaction conditions were catalyst dosage= 0.4 g, [H₂O₂]= 0.3 mL, pH= 2.5, [reactive brilliant blue]_o = 50 mg·L⁻¹, and volume of solution= 500 mL at room temperature, the decolorization efficiency of reactive brilliant blue was 91.98% within 60 min. Moreover, the Fe-Mn-sepiolite catalyst had good stability for the degradation of reactive brilliant blue even after six cycles. Leaching of iron ions (<0.4 mg·L⁻¹) was observed. The decoloring process was reactive brilliant blue specific via a redox reaction. The benzene ring and naphthalene ring were first oxidized to open ring; these were then oxidized to the alcohol and carboxylic acid. The reactive brilliant blue was decomposed mainly by the attack of ·OH radicals including surface-bound ·OH radicals generated on the catalyst surface.     

NKY功能化树脂静态吸附混合染料的研究

探讨了NKY功能化树脂对混合染料(活性艳蓝：KN-R和活性艳橙K-GN)的静态吸附行为．结果表明：NKY树脂吸附单组分染料的能力大于其对混合染料的吸附，而且对混合体系中的染料有一定的选择性，吸附KN-R的速率较大．从动力学研究来看，NKY对混合染料的吸附速率其决定步骤是液膜扩散．等温曲线的结果显示，NKY对混合染料中每种组分的吸附行为同吸附单组分体系的类似，同时，随温度的升高，吸附速率常数增大，标准自由能变的绝对值增大。     

湘南红壤对NO_3~-和SO_4~(2-)的吸附机理研究

本文研究了湘南第四纪红粘土发育的红壤对NO_3和SO_4~(2-)的吸附等温线。结果表明红壤对NO_3~-的吸附在浓度低时为负吸附,浓度高时为正吸附,吸附机理为非专性吸附,红壤对SO_4~(2-)的吸附等温式以Freundlich方程最好,在达到最大吸量(X_m)之前,SO_4~(2-)以置换羟基(—OH)的配位吸附为主;而在达到最大吸附量以后,以非专性物理吸附为主。     

Decolorization of anthraquinone dye by Aspergillus ficuum in various physiological states

Decolorization of reactive brilliant blue KN-R by Aspergillus ficuum was investigated on suspended spores, mycelial pellets, immobilized cells. It was found that Aspergillus ficuum could effectively decolorize reactive brilliant blue KN-R especially when grown as pelleted mycelia. Many factors affecting the decolorization process in nitrogen-limited media (NLM) were studied, including: initial pH, temperature, and mycelial age. Results showed that the media containing reactive brilliant blue KN-R at 50 mg/L could be decolorized by 96% of the initial color in 42 h, in most conditions tested, the dye degraded products assayed by UV-visible spectrophotometer and macroscopic observation showed that the decolorization of reactive brilliant blue KN-R by mycelial pellets includes two important processes: biodegradation and biosorption. Kinetic study revealed that reactive brilliant KN-R biodegradation by mycelial pellets and suspended spores conformed to first-order reaction model while reactive brilliant blue KN-R biodegradation by immobilized cell followed zero-order model. In addition, mycelial pellets was found to biodegrade KN-R more quickly than suspended spores and immobilized cell.