镰刀菌HJ01对苯酚的降解性能

为了研究真菌对苯酚的降解能力，采用本实验室分离的一株镰刀菌HJ01，考察了外加碳源、降解体系初始pH、温度对HJ01菌体生长量和苯酚降解效果的影响，初步探讨了镰刀菌降解苯酚的动力学与机理。实验结果表明，该菌能以苯酚为惟一碳源生长，添加适量的蔗糖可促进HJ01菌体的生长及苯酚的降解。在蔗糖加入量为3g／L、降解体系初始pH为6．0、温度为30℃的最佳条件下，经HJ01菌处理4d后的质量浓度为420mg／L苯酚废水中的苯酚完全降解。镰刀菌的生长和苯酚降解动力学符合Andrews模型。     

镰刀菌HJ01对对氯苯酚的降解特性

采用实验室分离的一株镰刀菌HJ01,以对氯苯酚(4-CP)为降解底物,以蔗糖为外加碳源,考察了蔗糖质量浓度、降解温度、初始pH对4-CP降解效果的影响,初步探讨了镰刀菌HJ01对4-CP的降解动力学和降解机理.实验结果表明:该菌株能以4-CP为惟一碳源和能源生长;在外加蔗糖为碳源,蔗糖质量浓度为3 g/L、降解温度为30℃、初始pH为8的条件下,50 mg/L4-CP能在6 d内被完全降解.以4-CP为惟一碳源和外加蔗糖下的降解动力学分别符合Haldane模型和一级动力学方程.     

一株吡啶降解菌的筛选及其降解性能

以吡啶为唯一碳源,从焦化厂活性污泥中分离得到一株对吡啶具有高效降解能力的菌株B1,对其进行了菌种鉴定。通过单因素实验研究了菌株B1适宜的降解条件,对反应过程进行了动力学拟合,并考察了菌株B1对焦化废水中吡啶的降解效果。实验结果表明:菌株B1为革兰氏阴性菌,属于不动杆菌属(Acinetobacter sp.);菌株B1适宜的降解条件为降解温度30℃、初始pH为7、摇床转速150 r/min;菌株B1对吡啶的降解过程符合零级反应动力学模型,当初始吡啶质量浓度为300 mg/L时,降解速率常数最高达到21.103 mg/(L·h);用菌株B1对初始吡啶质量浓度为430 mg/L的实际焦化废水处理74 h后,吡啶降解率可达74.26%。     

超声辐射法降解废水中的二甲苯、苯酚和丙烯腈

采用频率为20kHz的超声波处理二甲苯、丙稀腈、苯酚溶液。实验结果表明，在二甲苯初始质量浓度为27．6mg／L、H2O2质量浓度为1．68g／L、溶液温度为25℃、声强为141．32W／cm^2、辐射全程时间为60min的条件下，二甲苯降解率可达99．20％；在丙烯腈初始质量浓度为100．0mg／L、通氧量为15mL／rain、溶液温度为28℃、声强为141．32W／cm^2、辐射全程时间为30rain的条件下，丙烯腈降解率可达98．20％；在苯酚初始质量浓度为20．0mg／L、H202质量浓度为1．50g／L、FeSO4质量浓度为0．22g／L、溶液温度为28℃、声强为48．92W／cm^2、辐射全程时间为40rain的条件下，苯酚降解率可达99．81％。     

一株对二甲苯降解菌的筛选鉴定及其降解特性

以对二甲苯为惟—碳源和能源,从某石化废水处理厂活性污泥中筛选得到一株对二甲苯降解菌株.生理生化实验、16S rDNA基因鉴定结果表明,该菌属于假单胞杆菌属(Pseudomonas sp.).通过对降解过程的动力学分析可知,该菌对底物的降解过程符合零级动力学特征,在初始对二甲苯质量浓度为800 mg/L时,降解速率常数最大,达18.43 mg/(L·h).在降解温度为30 ℃、废水pH为7.5、摇床转速为150 r/min的条件下,将5 mL菌液投加至32 mL对二甲苯质量浓度分别为840 mg/L和830 mg/L的焦化废水和石化废水中,降解84 h后基本无对二甲苯检出.     

Fe-Ce/ZSM-5复合催化剂的制备及其催化性能

采用浸渍法制备了Fe-Ce/ZSM-5复合催化剂,并将其用于甲基橙的催化降解。利用单因素实验考察了溶液pH、初始甲基橙质量浓度、催化剂加入量、初始H_2O_2浓度及反应温度对准一级动力学方程反应动力学常数的影响,对催化剂的稳定性进行了测试,并探讨了甲基橙的催化降解机理。实验结果表明:在溶液pH 5.0、初始甲基橙质量浓度100 mg/L、催化剂加入量1.0 g/L、初始H_2O_2浓度20 mmol/L、反应温度20℃的优化条件下反应60min,反应动力学常数高达0.034 min~(-1),甲基橙降解率高达87%,铁离子流失量仅为0.019 mg/L;催化剂重复使用3次后,甲基橙降解率仍高于80%,保持了较高活性。     

纳米氧化锌的制备及其对对硝基氯苯的降解

采用蒸发氧化法制备纳米ZnO。当炉温为1100℃、空气流量为0．6m^3／h、锌粒加入量为5g时,得到高纯度类四锥体和柱形纳米ZnO。以该ZnO为光催化剂,对对硝基氯苯进行光催化氧化,考察了ZnO的加入量、对硝基氯苯的初始浓度、溶液pH等对对硝基氯苯降解率的影响。在ZnO质量浓度为0．5g／L、对硝基氯苯质量浓度为30mg／L、pH为7、光照时间为100min的条件下,对硝基氯苯降解率为98％。     

反硝化处理硝氮废水的动力学研究

对反硝化法处理高浓度硝氮废水的动力学进行了研究，获得了最佳动力学条件，在温度为30℃左右,pH为7－8，MLSS为3g/L左右，C／N为0．95－1．0，进水硝氮质量浓度为300mg/L，水力停留时间为6－8h的条件下，出水NOx^--N的质量浓度小于20mg/L,COD小于100mg/L。     

长链烷烃降解菌C6的鉴定及性能研究

从含油活性污泥中筛选出一株长链烷烃降解菌C6,进行了菌种鉴定,考察了该菌对正十六烷及柴油和石蜡的混合物的降解能力,并对由菌株C6产生的生物表面活性剂进行了鉴定。实验结果表明:该菌为鲍曼不动杆菌(Acinetobacterbaumannii);对液体培养基中质量浓度为1 000 mg/L的正十六烷降解48 h后,降解率接近100%,降解动力学曲线的拟合结果符合Monod模型;对液体培养基中质量浓度为1 000 mg/L的柴油和石蜡的混合物降解96 h后,降解率达93%;菌株C6产生的生物表面活性剂经FTIR分析鉴定为磷脂类表面活性剂,排油圈直径为60 mm,临界胶束质量浓度约为25 mg/L,可将水的表面张力降至27.09 mN/m。     

Fenton试剂降解选矿废水中残余黄药

采用Fenton试剂处理选矿废水中残余的黄药,分别考察了氧化时间、反应初始pH、Fe^2 浓度及H2O2用量对黄药降解效果的影响;用正交实验确定了4个因素的最佳条件。结果表明,反应初始pH和H2O2用量是影响黄药去除效果的主要因素。氧化时间为60min、反应初始pH为4、Fe^2 质量浓度为20mg／L、H2O2质量浓度为20mg／L、黄药质量浓度为：125mg/L时,黄药的去除率达到99．5％,COD去除率为87．5％。     

Microbial degradation of pyridine using Pseudomonas sp. and isolation of plasmid responsible for degradation

Pseudomonas (PI2) capable of degrading pyridine was isolated from the mixed population of the activated sludge unit which was being used for treating complex effluents, the strain was characterized. Aerobic degradation of pyridine was studied with the isolated strain and the growth parameters were evaluated. Pyridine degradation was further conformed by chromatography (HPLC) analysis. The process parameters like biomass growth and dissolved oxygen consumption were monitored during pyridine degradation. In order to conform with the plasmid capability to degrade pyridine, the requisite plasmid was isolated and transferred to DH 5alpha Escherichia coli. The subsequent biodegradation studies revealed the ability of the transformed plasmid capability to degrade the pyridine.     

一株双酚A降解菌的筛选、鉴定及其生长、降解条件

从沈阳北部污水处理厂曝气池活性污泥中驯化、分离及筛选得到一株以双酚A为唯一碳源的高效降解菌株D-17,通过菌体形态、生理生化反应特性及16S r DNA基因测序分析对其进行了鉴定,并研究了该菌株的生长及双酚A降解条件。菌种鉴定结果表明,该菌为乙酸钙不动杆菌(Acinetobacter calcoaceticus)。实验结果表明:该菌株的生长及降解双酚A的最适条件为溶液pH 7.0,接种量10%,摇床转速150 r/min,降解温度30℃,降解时间5d;当双酚A初始质量浓度为60 mg/L时,双酚A降解率达52.62%;投加蛋白胨后,双酚A降解率提高至57.15%。     

Ability of Fungal Strains to Degrade PVA Based Materials

The aim of this work was to select a fungal strain with degradative potential upon PVA based materials. The polymeric materials tested were PVA films which contain different percentages of PVA, starch and glycerol. These materials are of interest for food packaging applications, which presume to solve the problems concerning accumulation, disposal and degradation. Eleven strains were tested in solid culture for the ability to use PVA based composites as carbon and energy sources. The fungal strain selected was cultivated in liquid medium with different compositions. The scanning electron microscopy (SEM) investigations revealed the effects of microorganism growth upon polymeric films. Significant changes in polymer surface aspects were observed depending on the medium culture composition, the presence of supplementary carbon source facilitating microbial growth and degradation process.     

生物刺激与生物强化联合修复柴油污染土壤

从柴油污染土壤中筛选分离出一株高效降解柴油的菌株CY-1,考察了自然衰减修复、生物刺激修复、生物强化修复以及生物刺激-生物强化联合修复等4种修复方法对土壤中柴油的降解能力及降解过程中几种土壤微生物酶活性的变化。实验结果表明:该菌为假单胞菌属;采用生物刺激-生物强化联合修复初始柴油质量分数为2.70%的柴油污染土壤,经过31 d的降解,柴油质量分数降至1.09%,柴油去除率达59.6%;经生物刺激-生物强化联合修复,土壤脱氢酶活性和荧光素二乙酸酯水解酶活性最高;通过生物刺激处理可使土壤脲酶活性和磷酸酶活性达到最高。     

Mechanism and Characterization of Polyamide 4 Degradation by <Emphasis Type="Italic">Pseudomonas</Emphasis> sp.

We identified a biodegrading microorganism of polyamide (nylon) 4, a linear polymer of γ-aminobutyric acid (GABA). From activated sludge, the biodegrading bacteria strains of Pseudomonas sp. were isolated and identified by their taxonomic characteristics and nucleotide sequences of 16S rDNA. One strain, ND-11, was grown on a minimal medium containing polyamide 4 (PA4) as the sole carbon source. The strain produced GABA as a degradation intermediate, as identified by analyzing the NMR spectra of degraded products. The culture supernatant of strain ND-11 degraded the emulsified PA4 completely within one day. These results suggest that the ND-11 strain degraded PA4 using its extracellular enzymes to hydrolyze amide bonds.     

Complete Degradation of Hexahydro‐1,3,5‐Trinitro‐1,3,5‐Triazine (RDX) by a Co‐Culture of Gordonia sp. KTR9 and Methylobacterium sp. JS178

The presence of hexahydro‐1,3,5‐trinitro‐1,3,5‐triazine (RDX) in soil and groundwater is a major contamination issue at many military facilities around the world. Gordonia sp. KTR9 metabolizes RDX as a nitrogen source for growth producing 4‐nitro‐2,4‐diazabutanal (NDAB) as a dead‐end product. Methylobacterium sp. strain JS178 degrades NDAB as a sole source of nitrogen for growth. A mixed culture of strains KTR9 and JS178 was able to completely degrade RDX. There was no difference in rate of RDX degradation by KTR9 alone or in co‐culture with JS178. The first‐order degradation coefficients of RDX and NDAB in the co‐culture were 0.08 hr^?1 and 0.002 hr^?1, respectively. In the co‐culture that initially contained RDX plus NDAB, strain JS178 degraded the NDAB that was produced by KTR9 as shown by a decrease in the molar yield of NDAB (from RDX) from 1.0 to –0.11. Co‐cultures of strains KTR9 and JS178 could be used to promote complete degradation of RDX in soils or groundwater. ©2016 Wiley Periodicals, Inc.     

H_4SiW_(12)O_(40)/TiO_2/空心微珠光催化降解联苯胺

采用复合型光催化剂H_4SiW_(12)O_(40)/TiO_2/空心微珠(cenospheres)光催化降解联苯胺,考察了联苯胺降解效果的影响因素,并运用FTIR和GS-MS技术分析了联苯胺光催化降解过程的主要中间产物,探讨了联苯胺可能的降解路径。实验结果表明:以125 W中压汞灯为光源,在溶液pH为6.3,初始联苯胺质量浓度为10 mg/L的条件下光反应240 min,联苯胺降解率达78%,比Ti_O2/空心微珠提高了24百分点;H_4SiW_(12)O_(40)/TiO_2/空心微珠光催化降解联苯胺符合表观一级动力学特征,且反应速率常数随初始联苯胺质量浓度的增加而减小;H_4SiW_(12)O_(40)/TiO_2/空心微珠具有较好的稳定性,易于分离,可重复利用;联苯胺光催化降解过程的主要中间产物为4-氨基联苯、4-氨基苯酚、对苯二酚和1,4-苯醌。     

Biodegradation of Poly(vinyl alcohol) and Bacterial Cellulose Composites by <Emphasis Type="Italic">Aspergillus niger</Emphasis>

The ability of fungal strains to attack a composite material obtained from poly(vinyl alcohol) (PVA) and bacterial cellulose (BC) is investigated. The fungal strain tested was Aspergillus niger. This fungal strain was able to change not only the polymer surface from smoother to rougher, but also to disrupt the polymer. The degradation results were confirmed by visual observations, scanning electron microscopy (SEM) analyses, X-ray diffraction analyses and FTIR spectra of the film samples. SEM micrographs confirmed the growth of fungi on the composite film surface. The degree of microbial degradation depends on culture medium and on composition of polymeric materials, especially on PVA content. The biodegradation process is accelerated by the presence of glucose in the culture medium as an easily available carbon source.