偶氮染料直接大红GBE脱色细菌的筛选及研究

从保定市某印染厂曝气池废水中分离到一株对染料直接大红GBE有高效脱色效果的菌株HD 1,经鉴定 ,该菌为沙门氏菌属 (Salmonella) ,在 2 5— 3 7℃都有较高的脱色率 ,最佳脱色温度为 3 7℃ ,在pH 6— 8范围内对染料具有明显的脱色效果 ,最佳脱色 pH值为 7.0 ,氧气对脱色具有一定的抑制作用。染料脱色产物的紫外 -可见光谱分析表明 ,可见光区 488nm处的吸收峰完全消失 ,而在紫外区出现了两个吸收峰     

偶氮染料直接大红GBE脱色细菌的筛选及研究

从保定市某印染厂曝气池废水中分离到一株对染料直接大红GBE有高效脱色效果的菌株HD－1，经鉴定，该菌为沙门氏菌属（Salmonella)，在25－37℃都有较高的脱色率，最佳脱色温度为37℃，在pH6－8范围内对染料具有明显的脱色效果，最佳脱色pH值为7.0，氧气对脱色具有一定的抑制作用。染料脱色产物的紫外－可见光谱分析表明，可见光区488nm处的吸收峰完全消失，而在紫外区出现了两个吸收峰。     

一组优势菌对活性染料的脱色研究

本文作者从成功运用"优势菌处理工业废水技术”的某织染公司水解池中取得10株纯菌.为了解该系统保持稳定脱色效果的原因,对分离到的10株纯菌进行进一步的脱色研究.分别对10株纯菌的完整细胞及其细胞破碎液进行活性染料的脱色实验,结果发现这10株菌均具有较高脱色率,且其混合菌群完整细胞的脱色效果优于各单株菌.混合菌群及各单株菌破碎细胞脱色实验结果与完整细胞的结果一致.     

一组优势菌对活性染料的脱色研究

本文作者从成功运用“优势菌处理工业废水技术”的某织染公司水解池中取得10株纯菌。为了解该系统保持稳定脱色效果的原因，对分离到的10株纯菌进行进一步的脱色研究。分别对10株纯菌的完整细胞及其细胞破碎液进行活性染料的脱色实验，结果发现这10株菌均具有较高脱色率，且其混合菌群完整细胞的脱色效果优于各单株菌。混合菌群及各单株菌破碎细胞脱色实验结果与完整细胞的结果一致。     

紫外诱变黄孢原毛平革菌染料脱色研究

对黄孢原毛平革菌孢子悬浮液进行了紫外诱变,并将筛选出的优势菌ZWYB1与未经诱变的菌作对比实验,结果表明:诱变筛选得到的ZWYB1不仅可缩短对染料的脱色时间,提高对杂环类染料蕃红花红及高浓度染料400 mg/L的孔雀石绿的脱色效果,而且诱变后的菌种具有一定的脱色能力稳定性.     

紫外诱变黄孢原毛平革菌染料脱色研究

对黄孢原毛平革菌孢子悬浮液进行了紫外诱变，并将筛选出的优势菌ZWYB1与未经诱变的菌作对比实验，结果表明：诱变筛选得到的ZWYB1不仅可缩短对染料的脱色时间，提高对杂环类染料蕃红花红及高浓度染料400mg／L的孔雀石绿的脱色效果，而且诱变后的菌种具有一定的脱色能力稳定性。     

一株嗜热偶氮染料脱色菌的分离鉴定及其脱色特性

从纺织厂的工业废水排污口取样,分离筛选出了一株嗜热的高效偶氮染料脱色菌PDR2。通过形态学、生理生化特征以及16S r DNA基因序列分析等方法对该菌株进行鉴定,发现该菌为厌氧芽孢杆菌,与Anoxybacillus sp(GQ471935)同源性最高。此外,分别考察了菌株PDR2在不同碳源、氮源、p H以及培养温度等条件下对偶氮染料直接黑38脱色性能的影响,在此基础上进一步研究了菌株PDR2对不同浓度直接黑38染料的耐受性。结果表明,菌株PDR2在55℃、p H 6.0且以葡萄糖为碳源,牛肉膏和蛋白胨为混合氮源时其脱色效果最佳,且菌株对偶氮染料直接黑38有着较强的耐受能力,在染料浓度低于0.4 g·L~(-1)时其脱色效果良好。在最佳条件下静置培养24 h时,菌株PDR2对0.1 g·L~(-1)直接黑38染料的脱色率高达92.34%,展出了良好的应用潜力。     

真菌和细菌对染料吸附脱色的高效共培养体系研究

在含有真菌G－1培养液中加入染料厂污水排放口的污泥样品，从发生快速脱色降解染料的混合培养液中分离出2株染料脱色细菌L－1和L－2，经API鉴定系统鉴定，确定菌株L－1为Enterobacter sp.，菌株L－2为Pseudomonas sp.,研究比较了单一和不同组合混合的真菌G－1菌株（Penicillium sp.)，细菌L－1菌株（Enterobacter sp.)和L－2菌株（Pseudomonas sp.)对偶氮染料红M－3BE（C.I.Reactive Red 241)和蒽醌染料艳蓝KN－R（C.I.Reactive Blue 19)的去除情况，发现G－1真菌和2种细菌组合的共培养体系对50mg/L红M－3BE和艳蓝KN－R处理5h去除率达100％和97．9％，并且是以脱色降解作用为主，建立了染料脱色降解菌的最佳组合，进一步测定了此最佳共培养体系对另外13种不同结构染料的脱色降解，结果表明，除对蒽醌染料R－478脱色降解较差外，对其他染料均可在1h-3d被完全脱色降解，表现出脱色降解染料的广谱性，向培养4d的共培养体系中依次加入8种染料，菌体可对染料连续脱色，维持脱色能力达8d左右。     

白腐菌J-6对五类化学结构染料的脱色性能

从白腐菌中筛出了一株能对五类不同化学结构的染料进行高效脱色的菌株——J-6。通过采用“批式”摇床培养法,测定染料脱色率,从而确定该菌株能高效脱色的最佳培养时间和连续处理染料的能力。发酵培养96h的菌体可使活性艳蓝R(A)SP在5h内脱色率达95％以上;活性翠蓝G、活性黑GRP、混合染料在9h内脱色率达90％以上;孔雀绿、Po1yR-478在24h内脱色率分别达95％、90％以上。另外,J-6对不同染料最佳脱色时间和最终脱色效率与菌体本身发酵培养的时间长短和染料的种类紧密相关。J6处理能力强,连续处理4次染料后仍保持较高的脱色率。     

真菌和细菌对染料吸附脱色的高效共培养体系研究

在含有真菌G 1培养液中加入染料厂污水排放口的污泥样品 ,从发生快速脱色降解染料的混合培养液中分离出 2株染料脱色细菌L_1和L_2 ,经API鉴定系统鉴定 ,确定菌株L_1为Enterobactersp .,菌株L_2为Peudomonassp .。研究比较了单一和不同组合混合的真菌G_1菌株 (Penicilliumsp .)、细菌L_1菌株 (Enterobactersp .)和L_2菌株 (Pseu domonassp .)对偶氮染料红M - 3BE(C .I .ReactiveRed 2 41)和蒽醌染料艳蓝KN -R(C .1.ReactiveBlue 19)的去除情况 ,发现G - 1真菌和 2种细菌组合的共培养体系对 5 0mg/L红M - 3BE和艳蓝KN -R处理 5h去除率达 10 0 %和 97.9% ,并且是以脱色降解作用为主 ,建立了染料脱色降解菌的最佳组合 ;进一步测定了此最佳共培养体系对另外 13种不同结构染料的脱色降解 ,结果表明 ,除对蒽醌染料R - 478脱色降解较差外 ,对其他染料均可在lh— 3d被完全脱色降解 ,表现出脱色降解染料的广谱性 ;向培养 4d的共培养体系中依次加入 8种染料 ,菌体可对染料连续脱色 ,维持脱色能力达 8d左右     

Biodecolorization of the azo dye Reactive Red 2 by a halotolerant enrichment culture.

The decolorization of the azo dye Reactive Red 2 (RR2) under anoxic conditions was investigated using a mesophilic (35 degrees C) halotolerant enrichment culture capable of growth at 100 g/L sodium chloride (NaCl). Batch decolorization assays were conducted with the unacclimated halotolerant culture, and dye decolorization kinetics were determined as a function of the initial dye, biomass, carbon source, and an externally added oxidation-reduction mediator (anthraquinone-2,6-disulphonic acid) concentrations. The maximum biomass-normalized RR2 decolorization rate by the halotolerant enrichment culture under batch, anoxic incubation conditions was 26.8 mg dye/mg VSSxd. Although RR2 decolorization was inhibited at RR2 concentrations equal to and higher than 300 mg/L, the halotolerant culture achieved a 156-fold higher RR2 decolorization rate compared with a previously reported, biomass-normalized RR2 decolorization rate by a mixed mesophilic (35 degrees C) methanogenic culture in the absence of NaCl. Decolorization kinetics at inhibitory RR2 levels were described based on the Haldane model (Haldane, 1965). Five repetitive dyeing/decolorization cycles performed using the halotolerant culture and the same RR2 dyebath solution demonstrated the feasibility of biological renovation and reuse of commercial-strength spent reactive azo dyebaths.     

Biodegradation mechanisms and kinetics of azo dye 4BS by a microbial consortium

A microbial consortium consisting of a white-rot fungus 8-4* and a Pseudomonas 1-10 was isolated from wastewater treatment facilities of a local dyeing house by enrichment, using azo dye Direct Fast Scarlet 4BS as the sole source of carbon and energy, which had a high capacity for rapid decolorization of 4BS. To elucidate the decolorization mechanisms, decolorization of 4BS was compared between individual strains and the microbial consortium under different treatment processes. The microbial consortium showed a significant improvement on dye decolorization rates under either static or shaking culture, which might be attributed to the synergetic reaction of single strains. From the curve of COD values and the UV-visible spectra of 4BS solutions before and after decolorization cultivation with the microbial consortium, it was found that 4BS could be mineralized completely, and the results had been used for presuming the degrading pathway of 4BS. This study also examined the kinetics of 4BS decolorization by immobilized microbial consortium. The results demonstrated that the optimal decolorization activity was observed in pH range between four and 9, temperature range between 20 and 40 degrees C and the maximal specific decolorization rate occurred at 1,000 mg l(-1) of 4BS. The proliferation and distribution of microbial consortium were also microscopically observed, which further confirmed the decolorization mechanisms of 4BS.     

氯甲烷与偶氮染料混合废水的超声脱色

使用40 kHz超声(US)脱色氯甲烷(包括CCl4、CHCl3和CH2Cl2)与偶氮染料(包括甲基橙与铬黑T)混合模拟废水,考察了氯甲烷初始浓度对偶氮染料超声脱色和TOC去除的影响.结果表明:偶氮染料的单独超声脱色速率很慢;而在CCl4与CHCl3存在时超声能使偶氮染料短时间内脱色至无色,但对其TOC的超声去除促进作...     

缺氧-好氧生物滤池中高效菌对活性红KN-3B的降解特性

为了研究高效脱色菌在缺氧好氧生物滤池（A/O biofilter）中对偶氮染料的降解特性，以活性红KN-3B（C.I. reactive red 180）为降解对象，缺氧生物滤池以火山碎石为填料，接种高效脱色菌CK3柯氏柠檬酸杆菌启动，好氧生物滤池以牡蛎壳为填料，接种污水处理厂活性污泥启动。试验考察了不同工况下缺氧-好氧生物滤池对色度和COD的去除效果，结果表明：生物滤池中微生物对偶氮染料活性红KN-3B的脱色和对COD降解的最适pH条件为弱酸性；缺氧滤池中高效菌对色度的去除需要外加碳源，且增加外加碳源有助于脱色率的提高；该高效菌为耐盐菌，当进水NaCl浓度达30 g/L时，色度去除率仍可达93%以上；当染料负荷达500 mg/L时，脱色率仍可达95%。通过紫外-可见扫描图谱分析初步推断CK-3柯氏柠檬酸杆菌对偶氮染料活性红KN-3B的脱色主要是生物降解作用。     

亚铁羟基络合物还原转化水溶性偶氮染料

偶氮染料是印染工艺中应用最广泛的一类染料,目前染料废水脱色是污水处理难题。亚铁混凝处理染料废水过程中可能存在亚铁的还原作用,本实验制备了比溶解态亚铁更具还原反应活性的亚铁羟基络合物(ferrous hydroxycomplex,FHC),以5种不同类型的水溶性偶氮染料为目标污染物,研究FHC还原水溶性偶氮染料的脱色性能。实验结果表明,FHC对活性艳红X-3B、酸性大红GR和阳离子红X-GRL有较好的还原脱色效果,仅投加含铁89.6 mg/L的FHC,染料脱色率达到90%以上,继续增大FHC投加量可以完全脱色;中性枣红GRL的FHC还原脱色效果较差,需加入313.6 mg/L的FHC才能达到90%以上脱色率;134.4 mg/L的FHC能够将直接耐酸大红4BS完全脱色,但其脱色主要以混凝沉淀为主;溶液pH对FHC的还原性能产生重要影响,FHC还原染料脱色的适宜的pH值范围为4～10。该研究为亲水性染料脱色提供了一种新的技术,也为FHC运用于印染废水脱色提供了理论基础。     

Kinetics of chemical decolorization of the azo dye C.I. Reactive Orange 96 by sulfide

The mechanism of decolorization of azo dyes based on the extracellular chemical reduction with sulfide (H2S, HS-, S2-) was postulated for sulfate reducing environments. To design technical decolorization processes of textile wastewater treatment with sulfide produced by sulfate reducing bacteria (SRB), kinetics is of great significance. Batch experiments were made in order to investigate the kinetics of abiotic decolorization of the reactive mono-azo dye C.I. Reactive Orange 96 (RO 96) with sulfide, with varying pH. The decolorization of RO 96 by sulfide under the exclusion of O2 corresponded to first-order kinetics with respect to both dye and sulfide concentration. The decolorization of RO 96 with sulfide at neutral pH (7.1) was advantageous compared with that at pH for 4.1, 6.3, and 6.5. This is attributed to an increase in the fraction of HS- of total sulfide species at neutral pH. The rate constants k for the decolorization at 37 degrees C were obtained as 0.01 for pH = 4.1, 0.06 for pH = 6.3, 0.08 for pH = 6.5, and 0.09 for pH = 7.1 in mM(-1) min(-1). The high rate constants for sulfide at pH 6.5-7.1 support that the decolorization through SRB (i.e. by bio-sulfide) can be effective in anaerobic bacterial systems with sulfate.     

Decolorization of azo dye reactive black B by Bacillus cereus strain HJ-1

Reactive black B (RBB) is a group of azo dyes that are widely used in the textile industry. In this study, a new microbial strain was isolated from azo dye contaminated river sediment which is capable of degrading RBB. The strain was identified as Bacillus cereus strain HJ-1 by 16S rRNA gene sequences analysis. The optimal conditions for RBB decolorization by B. cereus strain HJ-1 are: 25 °C, pH 8, 1 CMC of triton X-100, 0.15 g L^?1 of added yeast extract, 0.125 g L^?1 of added glucose and static culture. Then the toxicity of RBB on the green algae Chlorella vulgaris was determined. The results showed that the median effective concentration (EC₅₀) of RBB for C. vulgaris is 48 mg L^?1 and toxicity will really decrease after decolorization. In the end, B. cereus strain HJ-1 was amended into the origin river sediment and analyzed the whole microbial community structure of river sediment samples by PCR-DGGE technique. The result showed that B. cereus strain HJ-1 could survive in the river sediment after 12 d of incubation. Based on this work, we hope that these findings could provide some useful information for applying the decolorization of RBB in our environment.     

Functional group influences on the reactive azo dye decolorization performance by electrochemical oxidation and electro-Fenton technologies

Electrochemical water treatment technologies are highly promising to achieve complete decolorization of dyebath effluents, as demonstrated by several studies reported in the literature. However, these works are focused on the treatment of one model pollutant and generalize the performances of the processes which are not transposable since they depend on the pollutant treated. Thus, in the present study, we evaluate, for the first time, the influence of different functional groups that modify the dye structure on the electrochemical process decolorization performance. The textile azo dyes Reactive Orange 16, Reactive Violet 4, Reactive Red 228, and Reactive Black 5 have been selected because they present the same molecular basis structure with different functional groups. The results demonstrate that the functional groups that reduce the nucleophilicity of the pollutant hinder the electrophilic attack of electrogenerated hydroxyl radical. Thereby, the overall decolorization efficiency is consequently reduced as well as the decolorization rate. Moreover, the presence of an additional chromophore azo bond in the molecule enhances the recalcitrant character of the azo dyes as pollutants. The formation of a larger and more stable conjugated π system increases the activation energy required for the electrophyilic attack of ^?OH, affecting the performance of electrochemical technologies on effluent decolorization.     

Decolorization of structurally different synthetic dyes using cobalt(II)/ascorbic acid/hydrogen peroxide system

The cobalt(II)/ascorbic acid/hydrogen peroxide system was used for decolorization of azo, acridine, anthraquinone, thiazine and triphenylmethane dyes. More than 90% decolorization was obtained with all dyes except Remazol Brilliant Blue R (75%). With other transition metals the system was less efficient. With copper, higher concentration and prolonged incubation time was necessary to obtain the same extent of decolorization. The rate of decolorizaton was not affected by pH in the range of 3-9. The reaction is very fast, with more than 90% decolorization being attained within 15 min. The system produces hydroxyl radicals which are responsible for the decolorization.     

Degradation of azo dyes using low iron concentration of Fenton and Fenton-like system

This study investigated Fenton and Fenton-like reactions at low iron concentration (相似文献