物理场协同作用降解有机污染物研究进展

有机污染物是环境污染物的主要类型,通过物理场外加能量的作用可实现各种有机污染物的高效降解.对微波、超声波、紫外光、电场、磁场、等离子体这几类主要物理场相互协同降解有机污染物的研究现状进行综述,重点介绍了物理场协同作用降解有机污染物的机制、效果、影响因素及污染物类型,并展望了该类研究今后的应用前景和发展趋势.     

二维单体同位素分析在有机污染物转化研究中的运用进展

单体同位素分析(CSIA)作为一门新技术日渐应用于有机污染物的降解研究。降解过程中,同位素分馏受环境因素影响较大,导致CSIA技术应用存在一定的不足。多维同位素分析通过对不同元素同位素分馏的相关性分析,可消除有机污染物降解过程中环境因素变化对同位素分馏行为的影响,因而对有机污染物降解的评价更为准确。主要总结了二维单体同位素分析(2-D CSIA)技术在有机污染物降解、转化机制等领域的研究进展,并对未来的发展方向进行了展望。     

芦苇湿地对造纸废水中有机污染物的去除效果及机理

为了对芦苇湿地对造纸废水中有机污染物的去除效果及降解机理进行研究,本文采用GC-MS联用仪对经芦苇湿地处理前后造纸废水中有机污染物的组成和含量进行测定,并通过叠放色谱图的方法对造纸废水中有机污染物的降解效果进行分析。结果表明:(1)经芦苇湿地处理前造纸废水中共测出30种有机污染物,其中8种被列入美国EPA环境优先控制污染物黑名单。(2)纸浆造纸废水生物塘-芦苇湿地复合处理系统对有毒有机污染物基本上达到了较好的去除效果:有机污染物总量减少80%以上,且降解后的产物多为毒性较小的烷烃类。(3)利用质谱手段对有机污染物的降解规律进行了初步研究。该研究为造纸废水处理和资源化利用提供了科学依据,为"造纸废水-芦苇-造纸"生态纸业循环经济模式的进一步推广应用奠定了基础。     

声光催化降解水中有机污染物

声光催化是水处理降解有机污染物的一种新技术。在分析中，探讨了该技术降解有机污染物的机理，以及国内外研究现状，包括降解效果和主要的影响因素。     

超声波与其他技术联用在水污染控制中的研究现状

主要介绍了国内外利用超声波与其他技术的联用方法降解水中污染物的进展 ,显示出超声波在降解有机污染物领域潜在的应用前景。     

新型过硫酸盐活化技术降解有机污染物的研究进展

在利用过硫酸盐氧化降解有机污染物过程中,以过硫酸盐活化所产生强氧化性的硫酸根自由基至为关键,综述了近来过硫酸盐的新型活化技术,其中以零价金属材料,含铁矿石,含铁复合材料,活性炭及含碳复合材料,含醌结构有机物活化为主线展开。通过介绍各种活化机理以及相应活化技术在降解有机污染物的研究,继而提高过硫酸盐降解有机污染物的潜在研究与应用价值。     

环境生物技术信息学进展

环境生物技术信息学通过计算机将生物信息学的技术与成果用于环境生物技术 ,控制污染。降解污染物基因DNA的碱基组成 -结构 -功能的核酸信息 ,降解污染物酶的氨基酸组成 -结构 -功能的蛋白多肽信息 ,为应用环境生物技术控制污染 ,注入了新的灵魂与力量。构建遗传工程特效菌株 ,高效降解危险有机污染物 ;创造高效工艺系统 ,去除危险有机污染物 ;有效降低或消除污染物对人体健康的危害 ,维护生态环境安全 ;是环境生物技术信息学的基本任务和光辉前景     

环糊精在环境科学中的应用

本文从环糊精对有机污染物的增溶作用：环糊精用于环境中有机污染物的富集和去除;环糊精对有机污染物降解过程的影响;环糊精衍生物去除土壤中的重金属;环糊精对污染物生物活性的影响等几个方面讨论了环糊精在环境科学方面的应用。     

超声波与其他技术联用在水污染控制中的研究现状

主要介绍了国内外利用超声波与其他技术的联用方法降解水中污染物的进展，显示出超声波在降解有机污染物领域潜在的应用前景。     

有机污染物的超声波降解技术

论述了超声波降解有机污染物技术的原理和效果，指出超声波的空化作用是其主要的作用机制，超声波与其它(H2O2、O2、紫外光以及磁场等)的联合运用，可以大大加速有机污染物的降解速度。     

固定化催化剂TiO2膜光催化降解三氯乙醛的研究

研究了负载于玻璃上的固定化催化剂TiO2膜光催化降解水中三氯乙醛的效果,探讨了TiO2膜光催化降解三氯乙醛的机理,考察了溶液pH值和三氯乙醛初始浓度埘TiO2膜光催化降解三氯乙醛的影响,并研究了固定化催化剂TiO2膜光催化降解三氯乙醛的动力学.结果表明,固定化催化剂TiO2膜光催化降解水中三氯乙醛的效果良好,当三氯乙醛初始浓度为2.25 mg/L时,在紫外光照时间3 h下,三氯乙醛的降解率高达100%.在相司紫外光照时间下,三氯乙醛的光催化降解率随着三氯乙醛初始浓度的增大而下降.在溶液pH=6.5时,三氯乙醛的降解效率最高.固定化催化剂TiO2膜光催化降解三氯乙醛的反应遵循一级反应动力学,反应速率常数随三氯乙醛初始浓度的增大而减小.     

TiO2纳米管催化降解4，4’-二溴联苯的影响因素和动力学研究

利用TiO2纳米管催化降解水中的4，4’-二溴联苯，对催化降解过程和影响因素进行研究。结果表明，TiO2纳米管对其有较高的催化降解效率且降解过程符合Langmuir—Hinshelwood动力学模式。不同光源、4，4’-二溴联苯的初始浓度、纳米管添加量和pH值对催化降解过程都有较大影响，其中pH值的影响最为明显。反应液在中性状态下的降解率明显低于pH=1或11的情况。在pH=1时，4，4’一二溴联苯的降解率达86％。     

电化学降解与声电化降解苯胺溶液的对比实验研究

采用电化学和声电化两种方法处理苯胺溶液．考察了处理时间、苯胺浓度、pH、电解质浓度、电解电压等因素对苯胺降解率的影响,并对两种方法处理的溶液分别进行紫外分析。实验结果表明．在其他条件相同的情况下．声电化降解所得苯胺降解率远远大于采用电化学方法所得降解率。     

Monod kinetics rather than a first-order degradation model explains atrazine fate in soil mini-columns: Implications for pesticide fate modelling

Pesticide transport models commonly assume first-order pesticide degradation kinetics for describing reactive transport in soil. This assumption was assessed in mini-column studies with associated batch degradation tests. Soil mini-columns were irrigated with atrazine in two intermittent steps of about 30 days separated by 161 days application of artificial rain water. Atrazine concentration in the effluent peaked to that of the influent concentration after initial break-through but sharply decreased while influx was sustained, suggesting a degradation lag phase. The same pattern was displayed in the second step but peak height and percentage of atrazine recovered in the effluent were lower. A Monod model with biomass decay was successfully calibrated to this data. The model was successfully evaluated against batch degradation data and mini-column experiments at lower flow rate. The study suggested that first-order degradation models may underestimate risk of pesticide leaching if the pesticide degradation potential needs amplification during degradation.     

Anaerobic degradation of five polycyclic aromatic hydrocarbons from river sediment in Taiwan

This study investigated the anaerobic degradation of five polycyclic aromatic hydrocarbons (PAHs) from Erren River sediment in southern Taiwan. The degradation rates of PAH were in the order: acenaphthene > fluorene > phenanthrene > anthracene > pyrene. The degradation rate was enhanced when the five compounds were present simultaneously in river sediment. Comparison of the PAH degradation rates under three reducing conditions showed the following order: sulfate-reducing conditions > methanogenic conditions > nitrate-reducing conditions. The addition of electron donors (acetate, lactate and pyruvate) enhanced PAH degradation under methanogenic and sulfate-reducing conditions. However, the addition of acetate, lactate or pyruvate inhibited PAH degradation under nitrate-reducing conditions. The addition of heavy metals, nonylphenol and phthalate esters (PAEs) inhibited PAH degradation. Our results show that sulfate-reducing bacteria, methanogen and eubacteria are involved in the degradation of PAH; sulfate-reducing bacteria constitute a major microbial component in PAH degradation. Of the microorganism strains isolated from the sediment samples, we found that strain ER9 expressed the greatest biodegrading ability.     

Anaerobic degradation of five polycyclic aromatic hydrocarbons from river sediment in Taiwan

This study investigated the anaerobic degradation of five polycyclic aromatic hydrocarbons (PAHs) from Erren River sediment in southern Taiwan. The degradation rates of PAH were in the order: acenaphthene > fluorene > phenanthrene > anthracene > pyrene. The degradation rate was enhanced when the five compounds were present simultaneously in river sediment. Comparison of the PAH degradation rates under three reducing conditions showed the following order: sulfate-reducing conditions > methanogenic conditions > nitrate-reducing conditions. The addition of electron donors (acetate, lactate and pyruvate) enhanced PAH degradation under methanogenic and sulfate-reducing conditions. However, the addition of acetate, lactate or pyruvate inhibited PAH degradation under nitrate-reducing conditions. The addition of heavy metals, nonylphenol and phthalate esters (PAEs) inhibited PAH degradation. Our results show that sulfate-reducing bacteria, methanogen and eubacteria are involved in the degradation of PAH; sulfate-reducing bacteria constitute a major microbial component in PAH degradation. Of the microorganism strains isolated from the sediment samples, we found that strain ER9 expressed the greatest biodegrading ability.     

土壤和沉积物中多氯联苯污染的生物修复机理研究进展

概述了多氯联苯 (PCBs)生物修复过程中影响因素和机理的研究进展 ,重点讨论了PCBs厌氧脱氯 ,好氧降解、真菌对PCBs降解、表面活性剂对PCBs降解的促进及抑制机理 ,以及完全矿化PCBs基因工程菌的构建 ,提出了今后工作展望     

Anaerobic degradation of nonylphenol in soil

This study investigated the effects of various factors on the anaerobic degradation of nonylphenol (NP) in soil. The results show that the optimal pH for NP degradation was 7.0 and that the degradation rate was enhanced when the temperature was increased. The addition of compost enhanced NP degradation. The individual addition of the electron donors lactate, acetate, and pyruvate inhibited NP degradation. The high-to-low order of NP degradation rates under three anaerobic conditions was sulfate-reducing conditions > methanogenic conditions > nitrate-reducing conditions. The results show that sulfate-reducing bacteria, methanogen, and eubacteria are involved in the anaerobic degradation of NP, with sulfate-reducing bacteria being a major component of the soil. Of the anaerobic strains isolated from the soil samples, strain AT3 expressed the best ability to biodegrade NP.     

Anaerobic degradation of nonylphenol in soil

This study investigated the effects of various factors on the anaerobic degradation of nonylphenol (NP) in soil. The results show that the optimal pH for NP degradation was 7.0 and that the degradation rate was enhanced when the temperature was increased. The addition of compost enhanced NP degradation. The individual addition of the electron donors lactate, acetate, and pyruvate inhibited NP degradation. The high-to-low order of NP degradation rates under three anaerobic conditions was sulfate-reducing conditions > methanogenic conditions > nitrate-reducing conditions. The results show that sulfate-reducing bacteria, methanogen, and eubacteria are involved in the anaerobic degradation of NP, with sulfate-reducing bacteria being a major component of the soil. Of the anaerobic strains isolated from the soil samples, strain AT3 expressed the best ability to biodegrade NP.     

Microbial aspects of the interaction between soil depth and biodegradation of the herbicide isoproturon

Factors controlling change in biodegradation rate of the pesticide isoproturon with soil depth were investigated in a field with sandy-loam soil. Soil was sampled at five depths between 0-10 and 70-80 cm. Degradation rate declined progressively down the soil profile, with degradation slower, and relative differences in degradation rate between soil depths greater, in intact cores relative to sieved soil. Neither the maximum rate of degradation, or sorption, changed with soil depth, indicating that there was no variation in bioavailability. Differences in degradation rate between soil depths were not associated with the starting population size of catabolic organisms or the number of catabolic organisms proliferating following 100% degradation. Decreasing degradation rates with soil depth were associated with an increase in the length of the lag phase prior to exponential degradation, suggesting the time required for adaptation within communities controlled degradation rates. 16S rRNA PCR denaturing gradient gel electrophoresis showed that degradation in sub-soil between 40-50 and 70-80 cm depths was associated with proliferation of the same strains of Sphingomonas spp.