土壤还原过程对氯代有机污染物还原脱氯的影响与机制

自然环境中,大多数氯代有机污染物厌氧还原脱氯反应是与土壤环境中一些生源要素的生物化学还原过程相伴生。有机污染物的种类、生物有效性以及毒性能够显著影响这些生源要素的转化,反过来,土壤中活跃的氧化还原反应也可以显著影响有机污染物的动力学转化过程。本文从氧化还原顺序上综述了反硝化过程、铁还原过程、硫酸盐还原过程和产甲烷过程对氯代有机污染物厌氧还原脱氯过程的影响与作用机制,旨在为氯代有机污染物在厌氧环境中还原脱氯的过程与机理的进一步研究、以及还原脱氯与微生物介导的生源要素氧化还原过程的耦合作用机制的揭示提供参考。     

利用厌氧颗粒污泥处理氯代有毒有机物

用能进行还原脱氯的微生物富集物接种，在小型试验装置内成功地培养出了具有还原脱氯功能的颗粒污泥。五氯苯酚能被这种颗粒污染完全脱氯并进一步分解为甲烷和二氧化碳。四氯乙烯和其他氯代乙烯能被颗粒污还原脱氯为乙烯。这种脱氯的颗粒污泥可用来处理含有五氯苯酚和氯乙烯类的废水和地下水。     

氯代芳烃催化氢转移脱氯的研究

本文以甲酸钠为氢源,对聚乙烯吡咯烷酮锚定的ＰｄＣｌ２催化氯代芳烃脱氯进行了研究,考察了反应条件对反应的影响,研究了脱氯的选择性。结果表明;该方法具有卓越的脱氯选择性,催化剂用量少,反应条件温和,操作简便。本文并对其脱氯反应机理进行了初步探讨。     

氯代烃在铜电极上的电还原特性和pH值的影响

采用循环伏安法,对氯代烃类化合物在铜电极表面上的电还原特性进行了研究,结果表明,氯代烷烃类化合物能在铜电极表面被直接还原,氯代芳烃不易在铜电极上被直接还原．碱性条件有利于中间体碳负离子的形成;在酸性条件下,碳负离子与氢离子之间反应的几率增大,导致通过溶液的电流值增加．pH值对不同氯代烃在铜电极上的电还原特性有不同程度的影响,这主要取决于碳链(或苯环)上其它取代基的性质、结构、数量和它与氯在苯环上的相对位置．     

厌氧颗粒污泥对五氯苯酚脱氯过程中的影响因素

在间歇培养血清瓶中,研究了厌氧颗粒污泥对五氯酚脱氯过程中的影响因素.结果表明,葡萄糖、酵母膏和蛋白胨显著提高了PCP的脱氯速率.添加甲酸、乙酸、乙醇对PCP脱氯速率有一定提高,丙酸和丁酸对脱氯速率没有影响.20%氢气的加入对PCP脱氯速率的影响显著.废水中硝酸盐和硫酸盐等电子受体的存在降低了PCP的脱氯速率.微生物抑制剂氯仿、青霉素降低了PCP脱氯速率,表明厌氧微生物尤其是甲烷菌对还原脱氯有重要影响.PCP最佳还原脱氯温度为38℃,最佳pH为7,低的氧化还原电位(<-200mV)有利于脱氯的进行.图5参13     

细菌二氯甲烷脱氯酶基因对拟南芥的转化

卤代烷烃是一类很普遍的环境污染物 ,在工业生产中常伴随着废气废物释放出来 ,严重污染土壤及地下水 ,并且严重破坏臭氧层 .在此类污染物含量较高的土壤中分离出一些细菌 ,它们能以卤代烷烃为唯一碳源进行生长 ,且将这些有毒废物分解成无毒的化合物 .我们曾经将细菌卤代烷烃脱卤酶基因克隆到拟南芥中并得到高效表达[1] .Ｍｅｔｈｙｌｏｂａｃｔｅｒｉｕｍ和Ｈｙ ｐｈｏｍｉｃｒｏｂｉｕｍ属的细菌能利用二氯甲烷作为唯一碳源进行生长[5] ,其代谢过程如图 1.其中参与反应的关键酶是二氯甲烷脱氯酶 ,此酶属于谷胱甘肽转移酶类 ,在脱ＣＩ时 ,先…     

共价三嗪有机框架材料对水中氯酚类污染物的光催化脱氯降解

利用共价三嗪有机框架材料(CTF-1)对4-氯酚(4-CP)、2,4-二氯酚(2,4-DCP)、2,4,6-三氯酚(2,4,6-TCP)和五氯酚(PCP)等4种不同氯原子取代数目的氯酚类污染物进行光催化降解研究,探讨了底物结构对氯酚脱氯降解效率的影响及机制.结果表明,氯酚脱氯降解过程明显受苯环氯原子取代数目的影响,氯原子数目越多,脱氯降解效率越高,氯原子数目与表观速率常数呈显著正相关,氯酚降解及脱氯速率均为：PCP>2,4,6-TCP>2,4-DCP>4-CP.对CTF-1光催化降解氯酚机制研究表明,活性物种在反应中不起作用,体系反应机制为针对氯酚上取代氯位点进行水解脱氯过程.本研究结果为深入揭示氯酚脱氯降解机制提供了理论依据,也为光催化技术处理卤代酚类废水提供了技术参考.     

零价铁对土壤中4-氯苯酚还原脱氯研究

氯苯酚是常见的环境污染物，它们在土壤中的加速分解可以减少对人类健康的危害。以恒温培养为方法，GC-MS为检测手段，研究了在常温常压下土壤中4-氯苯酚(4-CP)在零价铁作用下的还原脱氯反应。结果表明：4-CP可以被来自零价铁的电子还原，零价铁能够有效促进土壤中的4-CP脱除苯环上的氯原子，从而达到降低毒性、增加可生化性目的。反应条件如初始pH、时间、零价铁用量等均对4-CP还原脱氯效率有重要影响，特别是当初始pH值控制在偏酸时更有利于反应的进行。在零价铁加入量500mg、初始pH=4、反应时间7d的条件下，零价铁对土壤中4-CP还原脱氯效率最高可以达到65％。利用实验数据，对零价铁作用下4-CP还原脱氯的反应机理也进行了初步探讨。     

水介质中催化剂Raney Ni催化2-氯酚加氢脱氯

选择水作为反应介质,以氢气为氢源,研究了Raney Ni催化下、水溶液中2-氯酚的加氢脱氯,调查了溶剂、碱助剂和碱金属或碱土金属氯化物对加氢脱氯反应的影响.发现在水体系中,2-氯酚更容易被加氢脱氯,水作为反应介质时显著改善了加氢脱氯的反应环境,消除了无机氯化物在催化剂表面的吸附和累积,使催化剂保持了高活性.     

多氯联苯微生物厌氧脱氯研究进展

多氯联苯是一种典型的持久性有机污染物,其在环境中的转化归趋备受关注.在厌氧条件下,多氯联苯可以通过微生物脱氯进行降解,该降解方式虽然广泛存在于自然界中,但是受生物地球化学因素的影响较大,调控较为复杂.本文对多氯联苯的厌氧微生物脱氯降解进行综述,讨论了脱氯路径和自然界中8种主要脱氯历程;脱氯微生物及相关的微生物还原脱卤酶;影响脱氯速率、程度和历程的主要物理和地球化学因素(温度、pH和氧化还原水平、碳源、电子受体、电子供体及抑制物).最后分析了多氯联苯厌氧脱氯研究中存在的问题并对其前景进行展望.     

Iron-carbon composite microspheres prepared through a facile aerosol-based process for the simultaneous adsorption and reduction of chlorinated hydrocarbons

Iron-carbon (Fe-C) composite microspheres prepared through a facile aerosol-based process are effective remediation agents for the simultaneous adsorption and reduction of chlorinated hydrocarbons. Complete dechlorination was achieved for the class of chlorinated ethenes that include tetrachloroethylene (PCE), trichloroethylene (TCE), cis- and trans-1,2-dicloroethylene (c-DCE, t-DCE), 1,1-dichloroethylene (1,1-DCE) and, vinyl chloride (VC). The Fe-C particles potentially provides multi-functionality with requisite characteristics of adsorption, reaction, and transport for the effective in situ remediation of chlorinated hydrocarbons. The carbon support immobilizes the ferromagnetic iron nanoparticles onto its surface, thereby inhibiting aggregation. The adsorptive nature of the carbon support prevents the release of toxic intermediates such as the dichloroethylenes and vinyl chloride. The adsorption of chlorinated ethenes on the Fe-C composites is higher (>80%) than that of humic acid (<35%) and comparable to adsorption on commercial activated carbons (>90%). The aerosol-based process is an efficient method to prepare adsorptive-reactive composite particles in the optimal size range for transport through the porous media and as effective targeted delivery agents for the in situ remediation of soil and groundwater contaminants.     

Free ‐ living animals as indicators of environmental pollution by chlorinated hydrocarbons

As some species of game and free‐living animals promptly respond to ecosystem damage by a reaction that is easy to interpret, they are important ecological indicators in assessing the total contamination of the environment. Consumers of the highest order like predators, predatory and fish‐eating birds are among the most important bioindicators of environmental contamination by chlorinated hydrocarbons and PCB.

Data on chlorinated hydrocarbons and PCB levels were collected throughout 1988–1992 and obtained from 16 species of free‐living animals from 9 protected areas of Slovakia. Muscle tissue, liver, kidney and egg samples were examined for HCB, HCH isomers, DDT and its analogues, and PCB.

Levels of organic chlorinated contaminants reveal a decreasing tendency and thus cease to be a toxicologically important risk factor in game, with the exception of predatory birds, as significant values have been recorded in their eggs and reproductive organs.     

Electrochemical reduction characteristics and the mechanism of chlorinated hydrocarbons at the copper electrode

The electrochemical reduction characteristics of chlorinated hydrocarbons were investigated by cyclic voltammetry technique. The reduction mechanism and activity of the chlorinated hydrocarbons at the copper electrode were explored. The relationship between the structure of chlorinated hydrocarbons and their reductive activity were discussed. The experimental results showed that chlorinated alkanes and a portion of chlorinated aromatic hydrocarbons could be reduced directly at the copper electrode. However, chlorinated aromatic hydrocarbons were not easy to reduce at the copper electrode. The results provided a theoretical basis for the catalyzed iron inner electrolysis method.     

Fenton process for degradation of selected chlorinated aliphatic hydrocarbons exemplified by trichloroethylene, 1,1-dichloroethylene and chloroform

The degradation of selected chlorinated aliphatic hydrocarbons (CAHs) exemplified by trichloroethylene (TCE), 1,1-dichloroethylene (DCE), and chloroform (CF) was investigated with Fenton oxidation process. The results indicate that the degradation rate was primarily affected by the chemical structures of organic contaminants. Hydroxyl radicals (·OH) preferred to attack the organic contaminants with an electron-rich structure such as chlorinated alkenes (i.e., TCE and DCE). The dosing mode of Fenton’s reagent, particularly of Fe²⁺, significantly affected the degradation efficiency of studied organic compound. A new “time-squared” kinetic model, C = C _o exp(?k _obs t ²), was developed to express the degradation kinetics of selected CAHs. This model was applicable to TCE and DCE, but inapplicable to CF due to their varied reaction rate constants towards ?OH. Chloride release was monitored to examine the degree of dechlorination during the oxidation of selected CAHs. TCE was more easily dechlorinated thanDCE and CF.Dichloroacetic acid (DCAA) was identified as the major reaction intermediate in the oxidation of TCE, which could be completely removed as the reaction proceeded. No reaction intermediates or byproducts were identified in the oxidation of DCE and CF. Based on the identified intermediate, the reaction mechanism of TCE with Fenton’s reagent was proposed.     

有机毒物对水蚤的急性毒性

对水蚤的毒笥试验数据是被广泛用于评价化合物水生生态效应的重要依据，检测有机化合物的毒性时，需特别注意待测物的难溶性，挥发性及易光解性，检测了多种氯代芳烃的ＥＣ５０值，其１８ｈ的结果与２４ｈ的结果相近，检测了２４种硝基芳烃的毒性，不同方法计算的ＥＣ５０值一致。     

Photodegradation of the herbicide goal

Photodegradation products of the herbicide Goal active ingredient were obtained with a xenon lamp and analyzed using direct inlet mass spectrometry, MS/MS and GC/MS. A number of products were identified and their generation pathways were established to be mainly Ar—O bond cleavage, dechlorination and photocyclisation. The latter process gives chlorinated and unchlorinated dibenzofurans some of which may be toxic.     

Meeressäuger als Bioindikatoren

Marine mammals are at the top of the marine food chain and, the-refore, show high concentrations of chlorinated organic compounds in their fatty tissue (blubber) By choosing the proper species it is possible to use marine mammals as bioindicators for chlorinated hydrocarbons in different marine environments. It is essential to choose a species whose habitat is confined to a restricted range. In addition to recording the age, sex, and, condition index of the bioindicator, information about its diet and metabolism should also be analyzed.     

Distribution,fate and persistence of organochlorine compounds formed during production of bleached pulp

The processes governing distribution of a xenobiotic compound discharged initially into the environment are discussed, and attention is drawn to (a) binding to organic matter in the sediment phase which affects both persistence and toxicity to biota and (b) the role of atmospheric transport for compounds of low water solubility and high vapour pressure. Important limitations in the use of sum parameters such as EOCI are pointed out. The important distinction between biodegradation and biotransformation is pointed out, and significant experimental determinants noted. Pathways for the aerobic metabolism of chlorophenolic compounds are discussed, and attention is drawn to the role of O‐methylation as an environmentally significant alternative to biodegradation. Evidence for the biodegradation of chlorinated aliphatic acids and hydrocarbons under both aerobic and anaerobic conditions is presented. Anaerobic metabolism of chlorophenolic compounds is discussed with respect to (a) de‐O‐methylation of chloroguaiacols, (b) dechlorination of chlorocatechols and (c) reduction of chlorovanillins. It is emphasized that current evidence provides a complex metabolic picture, and that only partial dechlorination may occur. Brief attention is given to the important issue of the persistence of chlorolignin, and attention drawn to technical issues which render this problem difficult of access by traditional procedures. Biohalogenation—particularly by fungi—is noted, though its quantitative contribution cannot be estimated at the moment. A number of important unresolved issues are underscored: (a) the problem of determining rates of microbial reactions which may be translated to environmental situations, (b) the cardinal role not only of the number of chlorine atoms in an aromatic compound but also the substitution pattern and (c) limitations in current understanding of the role of anaerobic bacteria in bringing about biodegradation and biotransformation.