功能菌强化应急处理苯胺突发污染事故研究

近年来各种环境污染事故频发，据统计仅2001~2003年间，发生的各类环境污染事故就高达5606次，其中水污染事故3235次，占全部的57.7%。这些事故不仅给人民生命财产造成巨大损失，也给生态环境造成严重的破坏。因此开发安全高效的应急处理技术迫在眉睫。本研究以筛选高效苯胺降解菌为基础，通过对高效菌降解性能的研究指导将高效菌作为功能郡主投加到已有生物处理系统强化应急处理苯胺突发污染事故废液，取得了良好的效果。 苯胺高效降解菌AN-P1为红球菌（Rhodococcus sp.），其通过间位途径降解苯胺，AN-P1利用苯胺生长和降解的最佳pH为6，最适浓度为2000 mg/L，最适温度为30 ℃，最佳接种量为0.3‰。AN-P1降解含500 mg/L、1000 mg/L、2000 mg/L苯胺的培养物分别经过28 h、24 h、32 h降解，出水苯胺含量能达到《污水综合排放标准》（GB8978-1996）一级标准。但由于苯胺降解过程中释放了大量氨氮，出水氨氮仍较高未能达标排放。而常规SBR系统应急处理效果较差，苯胺和COD去除率均低于10%，出水未能达标排放。活性碳吸附后的回收和后续处理也会带来操作不变和二次污染问题，且处理后出水往往难于达标排放，尚需进行进一步处理。 生物处理系统应急处理后恢复运行处理效果监测和PCR-DGGE图谱分析显示，用AN-P1菌强化应急处理系统后不仅能快速高效的去除苯胺，而且可以有效保障处理系统对污染物的净化性能，有效的保护系统中的功能微生物免受苯胺毒害。 研究结果表明，从实际处理效果、对原有生物系统性能保护及实际应用操作等多方面考虑，用AN-P1菌强化应急处理苯胺突发污染事故在技术上都是可行的。本研究为应急处理苯胺突然污染事故废液提供了新的方法。 Recent years, environment pollution accidents happened frequently, the data showed that there are 5606 accidents between 2001 and 2003, including 3235 water environment accidents, which is 57.7% of all. These accedents not only caused money lost and life lost but also caused serious damage to the ecologicl environment. So exploring highly-effective and secure methods to solve these accidents is an urgent mission. We screened a highly-effective aniline-degrading bacterium and did some researches on its ability to degrade aniline, in order to guide the emergency treatment of aniline containing wastewater that caused by sudden accident pollution with bioaugmentation. A highly-effective aniline-degrading bacterium AN-P1 was isolate and characterized as Rhodococcus sp. It degrades aniline through meta-cleavage pathway. The optimal pH and temperature for cell growth and aniline degradation were 6 and 30 ℃, respectively, and the opitimal concentration of aniline was 2000 mg/L, the optimal inoculation amount was 0.3‰.It took bacterium AN-P1 only 18 h, 24 h and 32 h, respectively, for the treatment of MSB containing 500 mg/L, 1000 mg/L, 2000 mg/L aniline to meet the first grade of national some of the NH4+-N which caused by aniline degradation. It took bacterium AN-P1 only 10 h, 20 h and 32 h, respectively, for the treatment of wastewater containing 500 mg/L, 1000 mg/L, 2000 mg/L aniline to meet the first grade of national integrated wastewater discharge standard. The bacterium AN-P1 can also remove some of the NH4+-N which caused by aniline degradation. It took bacterium AN-P1 only 10 h, 20 h and 32 h, respectively, for the treatment of wastewater containing 500 mg/L, 1000 mg/L, 2000 mg/L aniline to meet the first grade of national integrated wastewater discharge standard. By combing AN-P1 with regular SBR system, it took only 36 h for the emergency treatment of wastewater containing 2000 mg/L aniline under simulating engineering conditions to meet the discharge standard. While the NH4+-N of effluent can not meet the standard because of the high amount NH4+-N caused by aniline degradation. The regular SBR system was not good at aniline and COD removal. The removal efficiency of which are less than 10%. It cost 67.8 g activated carbon to absorbed 1000 mg aniline. It is inconvenient to transport and use it for the emergency treatment of aniline when the sudden pollution accident happened. Meanwhile, it was complex ad hard to recycle the activated carbon and treat the aniline wastewater get from activated carbon recycling too. Hard to meet the effluent standard was also a problem of activated carbon absorption method. According to the PCR-DGGE profile and removal efficiency of pollutants and COD when the systerm recover from emergency treatment, AN-P1 can efficiently protect the microbial community of regular activated sludge system against the aniline. It proved that combing AN-P1 with regular biological system is a feasible strategy for emergency treatment of aniline sudden pollution accident. The research offered a new way for emergency treatment of aniline sudden pollution accident.

大功率电子加速器的辐射灭菌效果研究

To study the effects of radiation sterilization of the electron beam,the three species of microorganisms,Escherichia.coli,Staphylococcus aureus and Proteus vulgaris were irradiated with the electron beam,delivered by the electron accelerator independently developed by the Institute of Modern Physics,Chinese Academy of Sciences,and the changes of superoxide dismutase(SOD) activity of these irradiated microorganisms were also tested.The results indicated that the Staphylococcus aureus were fully radio-sterili...中文摘要：在中国科学院近代物理研究所自行研制的大功率电子加速器上,研究了不同辐照剂量的电子束对大肠杆菌、金黄色葡萄球菌和变形杆菌3种微生物的杀灭效果,同时检测了辐照后菌体超氧化物歧化酶(SOD)活性的变化。结果显示:辐照剂量达到2.0 kGy时,可完全杀灭金黄色葡萄球菌,2.2 kGy时可完全杀灭大肠杆菌和变形杆菌;辐照对3种微生物的SOD活性有较显著的影响。

Kinetic modeling of growth and biodegradation of phenol and m-cresol using Alcaligenes faecalis

A phenol-degrading. microorganism, Alcaligenes faecalis, was used to study the substrate interactions during cell growth on phenol and m-cresol dual substrates. Both phenol and m-cresol could be utilized by the bacteria as,the sole carbon and energy sources. When cells grew on the mixture of phenol and m-cresol, strong substrate interactions were observed. m-Cresol inhibited the degradation of phenol, on the other hand, phenol also inhibited the utilization of m-cresol, the overall cell growth rate was the co-action of phenol and m-cresol. In addition, the cell growth and substrate degradation kinetics of phenol, m-cresol as single and mixed substrates for A. faecalis in batch cultures were also investigated over a wide range of initial phenol concentrations (10-1400 mg L-1) and initial m-cresol concentrations (5-200 mg L-1). The single-substrate kinetics was described well using the Haldane-type kinetic models, with model constants of it mu(m1) = 0.15 h(-1), K-S1 = 2.22 mg L-1 and K-i1 = 245.37 mg L-1 for cell growth on phenol and mu(m2) = 0.0782 h(-1), K-S2 = 1.30 mg L-1 and K-i2 = 71.77 mgL(-1), K-i2' = 5480 (mg L-1)(2) for cell growth on m-cresol. Proposed cell growth kinetic model was used to characterize the substrates interactions in the dual substrates system, the obtained parameters representing interactions between phenol and m-cresol were, K = 1.8 x 10(-6), M = 5.5 x 10(-5), Q = 6.7 x 10(-4). The results received in the experiments demonstrated that these models adequately described the dynamic behaviors of phenol and m-cresol as single and mixed substrates by the strain of A. faecalis.

3株细菌对土壤中芘和苯并芘的降解及其动力学

研究了3株多环芳烃(PAHs)高效降解菌对土壤中芘和苯并芘(BaP)的降解动态,用Michaelis-Menton和Monod动力学模型对结果进行拟合.结果表明,3株细菌对芘和BaP的降解率有显著性差异.芽孢杆菌(Bacillus sp.SB02)42 d对芘和BaP的降解率均最高.当土壤中芘和BaP的初始浓度为50 mg/kg时,芽孢杆菌(Bacillus sp.SB02)、动胶杆菌(Zoogloea sp.SB09)、黄杆菌(Flavobacterium sp.SB10)42 d对芘的降解率分别为42.69%、32.88%、25.07%,对BaP的降解率分别为33.04%、25.39%、22.02%.3株细菌对芘和BaP的降解速率也存在显著性差异.芽孢杆菌(Bacillus sp.,SB02)最快,1周可降解20.88%芘和12.6%的BaP,动胶杆菌(Zoogloea sp.SB09)次之,黄杆菌(Flavobacterium sp.SB10)降解速率最慢.

表层土壤中菲的紫外光降解研究

多环芳烃化合物(PAHs)由于致癌、致畸和致突变而受到广泛关注。本实验以多环芳烃菲(Phe)为目标污染物,研究了温度、腐植酸和紫外辐射强度对Phe光降解的影响并对不同因素对降解动力学的影响作了研究。结果表明,Phe的降解在20℃到30℃范围内,随着温度的升高,光降解率增加;腐植酸在Phe污染土壤的光降解中起敏化作用,可显著促进光解,腐植酸浓度为5mg·kg-1足以达到敏化的效果;Phe光降解速率常数随辐射强度的降低而降低,呈正相关,光解的半衰期随着辐射强度的降低而增加,呈负相关。

不同介质中多环芳烃光降解及与生物耦合降解研究现状

多环芳烃(PAHs)是环境中广泛存在的一类有机污染物。它的降解一直是人们关注的课题。光降解就是多环芳烃降解的一种重要形式。对在气相、液相和固相不同介质中的PAHs光降解研究进行了综合论述,重点对PAHs在液相介质的降解速率及影响因素、中间产物及降解机制和反应动力学进行了深入探讨,并介绍了光-生物耦合降解多环芳烃的研究进展。建立系统而有效的PAHs光降解研究技术与方法,是目前当务之急。进一步完善PAHs光降解研究的技术与方法,可更准确地研究PAHs光降解机制及影响因素。

长期灌溉含多环芳烃污水对稻田土壤酶活性与微生物种群数量的影响

以沈抚污水灌区为例,研究了长期灌溉含多环芳烃(PAHs)污水对稻田土壤酶活性、微生物种群数量的影响。结果表明,灌区稻田土壤PAHs含量在319.5～6362.8μg.kg-1。长期污水灌溉导致稻田土壤PAHs含量严重超过环境标准。随清水连续灌溉年限的增加,土壤PAHs总量不同程度降低直至低于土壤PAHs环境质量标准。相关性分析表明,在目前污染程度下,灌区稻田3大土壤微生物类群和主要功能群的种群数量主要受土壤理化性质的影响,受PAHs含量影响不明显。土壤全氮含量与细菌数量呈极显著正相关(P<0.01)。土壤酶活性受到土壤养分和PAHs污染的双重影响,土壤有机碳和全磷含量分别与脱氢酶、多酚氧化酶和脲酶活性呈极显著正相关(P<0.01),PAHs含量分别与脱氢酶和脲酶活性呈极显著正相关(P<0.01),与多酚氧化酶活性呈显著正相关(P<0.05)。

长期石油污水灌溉对东北旱田土壤微生物生物量及土壤酶活性的影响

以土壤微生物生物量和土壤酶活性等为土壤微生物变化指标,研究了含油污水长期灌溉对东北沈抚灌区农田土壤微生物的影响。结果表明:土壤微生物生物量碳和生物量氮随着污灌有机物污染程度的增加而增加,与土壤石油烃(TPH)含量极显著正相关,相关系数分别为0.955和0.962(P<0.01);与土壤多环芳烃(PAHs)含量也极显著正相关,相关系数为0.941和0.946(P<0.01)。土壤酶活性分析表明,土壤脱氢酶和多酚氧化酶与土壤TPH含量极显著正相关,相关系数分别为0.977和0.958(P<0.01);与PAHs含量也极显著正相关,相关系数分别为0.997和0.977(P<0.01)。土壤中的脲酶受污水灌溉中含N物质的影响与TPH含量显著相关,相关系数为0.713(P<0.05),与PAHs污染无明显相关性。而纤维素酶与土壤有机物污染无明显相关关系。土壤微生物生物量和土壤脱氢酶、多酚氧化酶可以作为污灌土壤TPH和PAHs污染敏感的生物学和生物化学指标。

多环芳烃降解菌ZL5分离鉴定及其降解质粒

通过选择性富集培养 ,从辽河油田石油污染土壤中分离到一株多环芳烃 (PAHs)降解菌ZL5 .它能以菲和芘为唯一碳源生长 ,但是不能利用萘 .16SrDNA核苷酸序列分析结果表明 ,ZL5属于变形细菌α亚类中的鞘氨醇单胞菌属 .该菌株含有一个大小约为 6 0kb的质粒 .丝裂霉素C消除实验表明 ,随着质粒的丢失 ,菌株利用菲和芘的能力也丧失 .用电转化和氯化铷转化法分别将菌株ZL5的质粒导入大肠杆菌JM10 9和DH5α中 ,随着质粒的获得 ,这些转化子获得了降解菲和芘的能力 .本研究结果表明 ,鞘氨醇单胞菌ZL5降解PAHs的功能和质粒有关 .图 4参 16

多环芳烃微生物降解基因的研究进展

多环芳烃(PAHs)是环境中普遍存在的一类有机污染物,微生物的降解是PAHs去除的主要途径。近年来,有关PAHs微生物降解途径和代谢产物的研究已有很多报道。小分子PAHs一般可以直接被微生物降解,而大分子PAHs则需要微生物以共代谢的方式降解。在过去20年中,微生物降解PAHs的基因相继被发现,各种基因在调控PAHs降解过程中的功能也越来越清晰。本文概述了PAHs微生物降解基因方面的研究进展,详细介绍了微生物对萘、菲的降解基因,最后对PAHs微生物降解基因的应用前景进行了展望。

多环芳烃污染土壤的生物泥浆法修复

通过小型泥浆反应器的运行 ,确定了生物泥浆法修复多环芳烃污染土壤的温度、水土比和通气量参数 .采用 2 :1的水土比 ,控制温度、通气量分别为 2 0℃～ 2 5℃ ,60L/h可以达到较好的修复效果 .用从污染土壤中分离出的真菌在纯培养条件下对多环芳烃进行降解 ,经 34d的培养 ,镰刀菌对芘和苯并蒽的降解率为 90 %和33 3% ,毛霉可以分别降解 81 .5%和 4 9.2 % ,青霉可以分别降解 52 %和 4 6%

多环芳烃污染土壤生物修复的强化方法

生物降解是去除环境中多环芳烃(PAHs)的重要途径,通过采取一些强化措施,如使用表面活性剂,添加营养物质和提供共代谢底物等,可显著提高PAHs降解速度和程度,为生物修复技术的成功应用提供前提。在分析中,对近年来国内外在PAHs污染土壤生物修复强化方面的研究进展进行了综述。

多环芳烃胁迫下稻田土壤细菌及分支杆菌种群多样性研究

多环芳烃(PAHs)污染对土壤微生物群落特别是微生物功能群的影响一直备受关注。本文应用变性梯度凝胶电泳(DGGE)技术,从群落和功能群多样性两个角度,分析了PAHs胁迫条件下稻田土壤细菌遗传多样性及与PAHs降解有密切关系的分支杆菌种群多样性变化。结果表明,PAHs污染对稻田土壤细菌群落多样性指数无显著影响,但造成土壤细菌群落结构的改变,重度PAHs造成一些对污染敏感的细菌种类消失,而使一些与PAHs降解有关的细菌种类丰度增加。而对与多环芳烃降解有密切关系的分支杆菌而言,中度PAHs污染稻田土壤分支杆菌种群多样性指数较重度和轻度PAHs污染土壤的略高,不同PAHs污染程度稻田土壤的优势分支杆菌种类不尽相同,PAHs污染造成稻田土壤1种或几种分支杆菌得到富集。长期PAHs污染造成土壤细菌群落和分支杆菌种群结构的变化,将直接影响土壤生态系统功能的发挥,间接改变土壤质量。

非流体介质中多环芳烃污染的微生物固定化修复技术

非流体介质中多环芳烃(PAHs)污染的修复是目前环境工作者所面临的艰巨而紧迫的任务.由于非流体介质环境的特殊性,常规修复方法难以高效地发挥作用,传统微生物修复技术采用的游离微生物也存在许多弊端.而微生物固定化能大幅度地提高参加反应的微生物浓度,避免优势菌受土著菌的恶性竞争,增强微生物的耐环境冲击性.微生物固定化技术在一定程度上克服了传统工艺的不足,因而广泛应用于流体介质(废水等)和半流体介质(泥浆等)环境污染的修复.在概述固定化微生物技术的特点和分析国内外研究进展的基础上,指出将该技术应用于非流体介质中PAHs污染的原位修复领域的可行性,并论述了需要解决的关键科学问题,提出了利用微生物固定化技术修复非流体介质中PAHs污染的未来研究课题.

菲对土壤酶活性的影响

采用室内培养方法,选择菲作为PAHs代表物,探讨了菲与土壤酶活性之间的关系。结果表明,当菲的添加浓度>100μg·kg-1时,添加菲后的3d时间里,土壤中脲酶活性有被抑制的现象;添加菲后的7d时间里,土壤中脱氢酶活性被抑制,土壤磷酸酶的活性却被激活;当菲的添加浓度为100～2400μg·kg-1时,土壤过氧化氢酶活性没有显著变化。土壤脲酶、脱氢酶、磷酸酶的活性可以作为菲污染土壤的生态毒理指标,并且观察它们在添加菲后的第1d到第7d的变化最为重要。