首页 | 本学科首页   官方微博 | 高级检索  
相似文献
 共查询到18条相似文献,搜索用时 125 毫秒
1.
枯草芽孢杆菌(Bacillus subtilis)HBS-4是从油田中分离出来的一株能高效降解有机物萘的菌株。当萘的初始浓度为100mg时,该菌株在pH为8.0,温度为40℃下具有较好的降解效果,作用69h能降解50%以上的萘。通过HBS-4菌株降解萘的动力学研究,在Williams结构模型的基础上建立了HBS-4作用萘的四组分动力学模型,并用此模型解释菌株HBS-4在降解萘的过程中,葡萄糖含量、菌液浓度、pH、Eh随时间的变化特征。  相似文献   

2.
为了探究热活化过硫酸盐(PS)技术对水中氧氟沙星(OFX)的氧化降解作用,考察了反应温度、体系的初始pH、PS的初始浓度、OFX的初始浓度对OFX降解效果的影响;并在单因素实验的基础上,选取反应时间、体系的初始pH、PS的初始浓度和OFX的初始浓度4个因素进行了响应面优化实验。结果表明:最佳降解条件为,反应温度60℃、PS初始浓度4.0 mmol/L、pH=4.7、OFX初始浓度0.03 mmol/L、反应时间60 min,此时OFX的降解率为81.29%;4个因素对热活化PS降解OFX均有影响,其影响显著性从大到小为反应时间、OFX的初始浓度、PS的初始浓度、初始pH。利用响应曲面法模拟出反应体系的最佳条件,经实验验证,OFX降解率为93.78%,与预测最佳结果95.00%基本相符,表明模型可靠有效。  相似文献   

3.
常影  姜宁  雷抗  孙艳丰  周睿 《世界地质》2014,33(3):702-707
零价铁和硝基苯反应后生成二价铁和苯胺,而苯胺也是地下水污染物。硫酸根自由基具有强氧化性,可以降解苯胺。而二价铁可以活化过硫酸盐产生硫酸根自由基,进而去除苯胺。本文研究了二价铁浓度、过硫酸盐浓度、苯胺初始浓度、体系初始pH、反应温度等因素对二价铁活化过硫酸盐去除水中苯胺处理效率的影响。结果表明:1)Fe2+活化过硫酸盐生成SO-4·能快速并有效氧化降解苯胺,对于目标浓度为1 000 mg/L的苯胺而言,Fe2+浓度为3.3 mmol/L,Na2S2O8浓度为4.4 mmol/L时,对苯胺有较佳降解效果,苯胺的降解率为86.33%。2体系对较低浓度的苯胺降解效果较好,当污染物初始浓度由1 000 mg/L降低到500 mg/L和100 mg/L时,苯胺降解率由86.33%升高为90.27%和97.16%。3初始pH对苯胺的降解率影响较大,中性条件下(pH=7左右)降解率较好,高初始pH(pH=9,11)和低初始pH条件(pH=3,5)下均低于中性条件下苯胺的降解效率。4体系的温度变化对降解率影响不明显。  相似文献   

4.
从长期受硝基苯严重污染场地中筛选出一株以硝基苯为唯一碳源和氮源的降解菌,命名为ZG。对ZG 进行了16S rDNA 和nbzA 基因克隆与序列分析,并研究了该菌的降解特性。结果表明,ZG 菌为革兰氏阴性细菌,初步鉴定该菌株为pseudomonas putida。ZG 菌含有nbzA 基因,并且该基因在质粒上,说明该菌降解硝基苯是通过半还原途径。ZG 菌对硝基苯浓度、培养温度、pH 值等外界环境因素具有一定的适用范围,但随着硝基苯浓度升高,硝基苯的降解速率和降解率表现出下降的趋势。在最佳降解条件下,即硝基苯浓度300 mg /L、温度20℃、pH 为7,ZG 菌对硝基苯的降解率达到99. 98%。 ZG 菌可适用于不同的硝基苯污染场地。  相似文献   

5.
臭氧-超声联用处理聚乙烯醇废水   总被引:2,自引:0,他引:2  
本研究采用臭氧-超声(O3/US)联用技术处理聚乙烯醇(PVA)废水,分别考察了PVA初始质量浓度、初始pH、臭氧通入速率、超声功率、超声频率及反应时间对PVA和COD去除效率的影响,并在此基础上通过正交实验确定了降解PVA和COD的最佳实验条件。研究结果表明,超声频率对去除率有显著影响,PVA初始质量浓度对去除效率的影响较大,反应时间、超声功率、臭氧通入速率和初始pH的影响相对较小。通过影响实验和正交实验确定的最佳降解条件为:PVA初始质量浓度100 mg/L、初始pH=9、臭氧通入速率4 g/h、超声功率320 W、超声频率40 kHz、反应时间20 min,此时COD和PVA的去除效率分别为86.4%和99.3%。超声对臭氧降解聚乙烯醇废水具有明显的协同作用,在最佳条件下,臭氧-超声联用技术比单独臭氧技术对PVA的去除率增加了5.1%,对COD去除率增加了19.4%。  相似文献   

6.
通过对取自MBR膜生物反应器中的活性污泥加入菲进行富集培养、驯化,分离、纯化出一株能以菲为唯一碳源和能源的短杆状革兰氏阴性菌J-1,细菌长2~5μm,宽1~3μm;研究了初始底物浓度、温度、pH对菌株J-1降解菲的影响,探讨了菌株J-1胞内酶对菲降解的底物抑制动力学。试验表明:菌株J-1在48h内能将不同浓度菲的水溶液中的菲完全降解;菲浓度增加,达到完全降解的时间延长。温度对细菌的降解能力影响较大,菌株J-1对菲降解的最佳温度为28℃。1.15mg·L-1的菲,28℃时48h内能完全降解,而相同时间内10℃时的降解率仅为36.65%。菌株J-1对pH的波动具有一定的适应性,pH在一定范围内(6.0~8.4)变化对菲降解的影响不大,降解反应的最佳pH为7.2。菌株J-1对菲的降解符合一级动力学反应方程。较高的底物浓度对酶促降解反应具有抑制作用,酶促反应的最大速率常数vm=1.17mg·L-1·h-1,米氏常数Km=61.70mg·L-1;底物抑制常数kS=49.60mg·L-1;最佳底物浓度[S]opt=55.32mg·L-1。  相似文献   

7.
以蒙脱土为载体制备负载型Fe/Al复合氧化物(FeAlOx/MMT)用于催化Fenton反应降解高浓度苯酚废水。实验结果表明,活性相FeAlOx中Fe/Al摩尔比为0.22时制备所得催化剂对Fenton反应具有最佳活性,且Fe/Al复合氧化物并未嵌入蒙脱土层间。在低温和高pH条件下催化体系存在诱导期,诱导期内FeAlOx/MMT缓释出Fe离子并进而由Fe离子催化溶液中的Fenton反应。通过对非均相催化降解苯酚废水的动力学研究发现,H2O2初始浓度、溶液的pH和反应温度对COD降解效率具有显著影响。调节降解过程中的温度序列和氧化剂引入程序能够缓解高温和高双氧水浓度双重因素耦合导致的HO.自消耗。在优化的降解条件下使用理论用量的H2O2可使得1 g/L的苯酚废水中苯酚降解率达到100%,而COD的降解率则达到97%。  相似文献   

8.
采用30 W石英紫外灯作为光源,研究了乐果在二氧化钛悬浮体系中光催化降解反应的动力学规律。考察了乐果起始浓度、TiO2用量、溶液pH值及温度对乐果光催化降解速率的影响,结果表明,乐果光催化降解符合表观零级动力学规律。由于速率常数k与乐果起始浓度有关,表明乐果光催化降解反应不是一个简单的零级反应。  相似文献   

9.
阿特拉津低温降解菌的筛选及降解机理研究   总被引:1,自引:1,他引:0  
以阿特拉津为唯一氮源, 在低温条件下(10℃),从吉林市污水处理厂的活性污泥中分离、筛选出1株能够高效降解地下水中阿特拉津的菌株W4.通过16S rDNA碱基测序和比对,初步确定该菌为假单胞菌属;通过室内降解条件优化,确定W4的最佳降解条件:初始pH范围为7~9,最佳碳源为蔗糖和乳糖,最佳碳源加入量为0.4 g/L.在最佳降解条件下,W4对初始质量浓度为34 mg/L、22 mg/L和10 mg/L的阿特拉津的生物降解反应符合零级反应动力学方程,对初始质量浓度为5 mg/L的阿特拉津的生物降解反应符合一级反应动力学方程.GC/MS分析结果显示,菌株W4降解阿特拉津遵循氯水解途径,代谢产物为2-羟基-4-乙胺基-6-异丙胺基-1,3,5-三嗪.  相似文献   

10.
北京地区潮土对土霉素的吸附特性研究   总被引:2,自引:0,他引:2  
北京近1/4区域土壤属于潮土,潮土对四环素类抗生素的吸附特性还鲜有报道。采用OECD Guideline 106的方法,研究土霉素在北京地区潮土上的吸附特性。结果表明,土霉素在潮土中的吸附动力学过程符合Elovich方程,土霉素初始浓度会影响吸附速率,2 mg/L时最大,10 mg/L时最小。吸附百分比随着初始浓度的升高,先增大后减小。温度和平均吸附速率呈负相关。实验浓度下,吸附等温线符合线性等温方程和Freundlich方程,吸附是自发的吸热反应。潮土对土霉素的吸附量和粉粒及黏粒含量之和呈正相关。土霉素在潮土中的吸附受初始浓度、温度、土壤性质等因素的影响,深入了解其作用机理,有助于防治土霉素污染,保护土壤安全。  相似文献   

11.
石油脱硫微生物菌株的筛选及鉴定的研究   总被引:2,自引:0,他引:2  
从胜利油田和冀东油田采集被石油污染的土壤样品,经富集技术培养后,从中分离出21株脱硫菌,再从中筛选出一高效脱硫菌株TV9704。这一菌株不能以正十二烷、正十六烷、液体石蜡、萘和柴油为碳源和能源生长,因此不会明显地损失石油的燃烧值;但它能利用噻吩或二苯并噻吩(DBT)作为唯一硫源来生长。本实验中噻吩和DBT的浓度使用UV分光光度计测定。菌株TV9704在噻吩起始浓度为63.2mmol/L的培养基中分别培养48h和144h后,它对噻吩的降解率分别为39.0%、63.8%;在DBT起始浓度为2.7mmol/L的培养基中培养72h,DBT降解了1.46mmol/L。选择醋酸钠和甘油为碳源时,乙醇能显著提高TV9704对DBT的降解率。菌株TV9704经中国工业微生物菌种保藏管理中心(CICC)鉴定为芽孢杆菌(Bacillussp),革兰氏阳性,专性好氧,在营养肉汁平板上形成橙黄色的圆形菌落。对菌株TV9704所作16SrDNA基因序列测定和分析显示,它与最相似种Bacillus aquimaris,Bacillus marisflavi的同源性分别为99.2%和98.2%,但它们之间的细胞形态特征及生理生化特性相差较大,因此无法鉴定到种。菌株TV9704可能是一个新种。  相似文献   

12.
为探究长庆油田污染土壤中微生物对石油的降解特性,在该油田多个油井附近采集了10处含油污染土壤进行石油烃降解菌的筛选、分离及降解实验。通过对筛选出的四株石油烃降解菌株5-5、5-X、9-2、10-3进行革兰氏染色、菌落形态观察、生化理化试验及16S rDNA测序,鉴定出这四株菌株分别为醋酸钙不动杆菌(Acinetobacter calcoaceticus)、不动杆菌(Acinetobacter sp.)、蒙氏假单胞菌(Pseudomonas monteilii)和乳酸不动杆菌(Acinetobacter lactucae)。14 d降解实验结果显示,这四种菌株对总石油烃的降解率分别为50.92%、51.27%、78.30%和44.39%;尤其菌株Pseudomonas sp.9-2表现出优异的降解性能,且对不同组分石油烃(正构烷烃、异构烷烃及芳烃)的降解率分别达到了94.65%、69.73%和59.07%,对长链正构烷烃也体现出了较好的降解性能。另外,抗逆性试验结果表明菌株Pseudomonas sp.9-2对pH和盐度的耐受范围分别为5.0~10.0、0.5%~6.0%,表明该菌株对盐碱环境具有较好的适应性,可用于盐碱石油污染土壤的微生物修复研究。  相似文献   

13.
近年来水环境中硝酸盐污染与抗生素污染的现象引起了人们的广泛关注,但目前复合抗生素污染对反硝化过程产生的影响并不明确。本研究以水环境中检出率较高的诺氟沙星和洛美沙星为代表进行模拟实验,探究ng级的两种抗生素复合对反硝化过程的影响。硝氮和亚硝氮的降解情况表明,实验浓度条件下,洛美沙星、诺氟沙星单用与二者联用对水环境中的反硝化过程存在不同的抑制作用。洛美沙星单用前期轻微促进反硝化,后期表现抑制作用,而诺氟沙星单用始终表现出抑制作用;洛美沙星和诺氟沙星联用抑制作用小于诺氟沙星单用,联用表现为拮抗作用。各体系的抑制作用大小为诺氟沙星>诺氟沙星+洛美沙星>洛美沙星。该模拟试验条件虽与实际条件有所差异,但在一定程度上表明抗生素联用表现出拮抗作用与反硝化体系内微生物数量、活性,反硝化酶活性,反硝化菌优势物种Achromobacter xylosoxidansAcinetobacter baumanniiPseudomonas sp.KY及功能基因nosZ和aac的丰度的变化有关。抗生素加入反硝化体系后会产生持续的影响,随反应时间的增加,反硝化菌逐渐适应有低浓度抗生素存在的环境,喹诺酮类抗生素耐药基因数量增加,微生物的耐药性增强,反硝化菌在数量和活性、反硝化酶活性及微生物群落层面均有回升趋势。  相似文献   

14.
The effects of Cd on the adsorption of an aquatic fulvic acid (FA) to the surface of Bacillus subtilis were investigated from pH 2.5 to 7.0, at fixed ionic strength (0.1 M NaClO4) and at ambient temperature (22 °C). Cd (14 mg/l) had no effect on FA adsorption at pH<5 but increased FA adsorption at pH>6. The effects of Cd (0, 14 mg/l) on FA adsorption to B. subtilis were further examined as a function of initial FA concentration (0–45 mg C/l) at pH 6.5. FA adsorption isotherms also were measured at pH 6.5 as a function of dissolved Cd concentration (0–14 mg/l) at three initial FA concentrations (4, 8, 22 mg C/l). At all FA concentrations studied at pH 6.5, FA adsorption increased with increasing initial total Cd concentration.

Under all studied conditions, preferential adsorption of high- to intermediate-molecular-weight FA components to B. subtilis resulted in a fractionation of the FA pool, with lower-molecular-weight components remaining in solution. At pH>6, Cd further enhanced the adsorption of high- to intermediate-molecular-weight FA components but did not significantly enhance the adsorption of lower-molecular-weight components. Hence, the overall process of adsorptive fractionation was not altered significantly by the presence of Cd.

Overall, the results of this study (1) demonstrate that FA adsorption to bacterial surfaces can be altered by the presence of a metal cation, and (2) provide further evidence that microbe–metal–ligand interactions may significantly affect the mobility and fate of natural organic matter in the subsurface.  相似文献   


15.
The biodegradability of polycyclic aromatic hydrocarbons such as naphthalene, fluorene, anthracene and phenanthrene by a halotolerant bacterial consortium isolated from marine environment was investigated. The polycyclic aromatic hydrocarbons degrading bacterial consortium was enriched from mixture saline water samples collected from Chennai (Port of Chennai, salt pan), India. The consortium potently degraded polycyclic aromatic hydrocarbons (> 95%) at 30g/L of sodium chloride concentration in 4 days. The consortium was able to degrade 39 to 45% of different polycyclic hydrocarbons at 60 g/L NaCl concentration. Due to increase in salinity, the percent degradation decreased. To enhance polycyclic aromatic hydrocarbons degradation, yeast extract was added as an additional substrate at 60g/L NaCl concentration. After the addition of yeast extract, the consortium degraded > 74 % of polycyclic aromatic hydrocarbons at 60 g/L NaCl concentration in 4 days. The consortium was also able to degrade PAHs at different concentrations (5, 10, 20, 50 and 100 ppm) with 30 g/L of NaCl concentration. The polycyclic aromatic hydrocarbons degrading halotolerant bacterial consortium consists of three bacterial strains, namely Ochrobactrum sp., Enterobacter cloacae and Stenotrophomonas maltophilia.  相似文献   

16.
Phenol biodegradation in an aerobic batch reactor was investigated using mixed two co-aggregating strains (Flavobacterium sp. and Acetobacter sp.). Response surface methodology by the Box–Behnken model was used to evaluate the optimal cell growth and phenol degradation conditions. The optimum temperature, pH value and inoculum size were found to be 33 °C, 6.06 and 13 %, respectively. In the conditions, phenol degradation rate and biomass were predicted to be 96.97 % and 410.78 mg/L within the range examined, respectively. Less toxic acetaldehyde, ethanol and acetic ether were identified as main intermediate products from the degraded samples using GC–MS. Substrate inhibition was calculated from experimental biomass growth and phenol degradation parameters using the Haldane equation. Kinetic parameters derived from nonlinear regression with correlation factors (R 2) were 0.9682 for phenol degradation and 0.9594 for biomass growth, respectively. The phenol concentration to avoid substrate inhibition was 278.17 mg/L.  相似文献   

17.
The purpose of the present work is to extend our knowledge of metal–cyanobacteria interactions and to contribute to the database on adsorption parameters of aquatic microorganisms with respect to metal pollutants. To this end, the surface properties of the cyanobacteria (Gloeocapsa sp. f-6gl) were studied using potentiometric acid–base titration methods and ATR-FTIR (attenuated total reflection infrared) spectroscopy. The electrophoretic mobility of viable cells was measured as a function of pH and ionic strength (0.01 and 0.1 M). Surface titrations at 0.01–1.0 M NaCl were performed using limited residence time reactors (discontinuous titration) with analysis of Ca, Mg and dissolved organic C for each titration point in order to account for alkali-earth metal–proton exchange and cell degradation, respectively. Results demonstrate that the cell-wall bound Ca and Mg from the culture media contribute to the total proton uptake via surface ion-exchange reactions. This has been explicitly taken into account for net proton balance calculations. Adsorption of Zn, Cd, Pb and Cu was studied at 25 °C in 0.01 M NaNO3 as a function of pH and metal concentration. The proportion of adsorbed metal increases as a function of culture age with cells of 44 days old having the largest adsorption capacities. A competitive Langmuir sorption isotherm in conjunction with a linear programming method (LPM) was used to fit experimental data and assess the number of surface sites and adsorption reaction constants involved in the binding of metals to the cyanobacteria surface. These observations allowed the determination of the identity and concentration of the major surface functional groups (carboxylate, amine, phosphoryl/phosphodiester and hydroxyl) responsible for the amphoteric behavior of cyanobacterial cell surfaces in aqueous solutions and for metal adsorption. Results of this work should allow better optimizing of metal bioremediation/biosequestration processes as they help to define the most efficient range of pH, cell biomass and duration of exposure necessary for controlled metal adsorption on cyanobacteria cultures. It follows from comparison of adsorption model parameters between different bacteria that technological application of cyanobacteria in wastewater bioremediation can be as efficient as other biological sorbents.  相似文献   

18.
The potential of various organisms to metabolize organic compounds has been observed to be a potentially effective means in disposing of hazardous and toxic wastes. Phenols and their compounds have long been recognized as one of the most recalcitrant and persistent organic chemicals in the environment. The bioremediation potential of an indigenous Pseudomonas fluorescence was studied in batch culture using synthetic phenol in water in the concentration range of (100–500) mg/L as a model limiting substrate. The effect of initial phenol concentration on the degradation process was investigated. Phenol was completely degraded at different cultivation times for the different initial phenol concentrations. Increasing the initial phenol concentration from 100 mg/L to 500 mg/L increased the lag phase from 0 to 66 h and correspondingly prolonged the degradation process from 84 h to 354 h. There was decrease in biodegradation rate as initial phenol concentration increased. Fitting data into Monod kinetic model showed the inhibition effect of phenol The kinetic parameters have been estimated up to initial phenol concentration of 500 mg/ L. The rsmax decreased and Ks increased with higher concentration of phenol. The rsmaxhas been found to be a strong function of initial phenol concentration. The culture followed substrate inhibition kinetics and the specific phenol consumption rates were fitted to Haldane, Yano and Koga, Aiba et al., Teissier and Webb models. Between the five inhibition models, the Haldane model was found to give the best fit. Therefore, the biokinetic constants estimated using these models showed good potential of the Pseudomonas fluorescence and the possibility of using it in bioremediation of phenol waste effluents.  相似文献   

设为首页 | 免责声明 | 关于勤云 | 加入收藏

Copyright©北京勤云科技发展有限公司  京ICP备09084417号