不同价态铁元素对厌氧微生物降解2,4,6-三氯酚的影响

【目的】考察初始pH值为5.0?10.0时, 不同价态铁元素(Fe0、Fe2+和Fe3+)对厌氧微生物降解2,4,6-三氯酚(2,4,6-TCP)的影响。【方法】采用间歇试验, 接种驯化3个月的厌氧污泥, 向其中分别投加Fe0、Fe2+和Fe3+, 测定体系中2,4,6-TCP浓度、pH值、铁离子浓度和微生物脱氢酶活性。【结果】“Fe0/Fe2+/Fe3+-微生物”体系对2,4,6-TCP的降解效率, 在初始pH值为中性偏酸性时, “Fe2+-微生物”体系>“Fe0-微生物”体系>“Fe3+-微生物”体系; 而当初始pH值为碱性时, “Fe0-微生物”体系>“Fe2+-微生物”体系>“Fe3+-微生物”体系; “Fe0/Fe2+/Fe3+-微生物”三种体系均有调节pH值的能力, 其中“Fe0-微生物”体系调节能力最强; 在不同初始pH值条件下不同价态铁元素对厌氧微生物活性的影响结果与其对2,4,6-TCP的影响规律基本相同。【结论】不同价态铁元素对厌氧微生物降解2,4,6-TCP的影响与初始pH值、体系实时pH值和铁元素价态及浓度等因素有关。     

零价铁对2,4-二氯酚生物还原脱氯的影响研究

采用间歇试验, 接种驯化两月的厌氧混合微生物, 考察厌氧体系中添加零价铁(Fe0)对2,4-二氯酚(2,4-DCP)生物还原脱氯效果的影响, 并对影响“Fe0+微生物”体系的一些因素进行了探索。结果显示：与零价铁或微生物的单独作用相比, “Fe0+微生物”体系能够有效促进2,4-DCP的脱氯反应, 最佳Fe0投加量和微生物接种量分别为0.5 g/L和376.2 mgVSS/L; 初始pH = 8.0对2,4-DCP的转化效果最好, 偏酸性环境不利于污染物转化; 微生物接种量与铁用量之间有一适宜比例, 一定范围内增加微生物接种量可催生出更多可降解污染物的酶或酶系, 提高2,4-DCP的降解效果。     

硝酸盐还原条件下Fe0/厌氧微生物联合体系降解2,4,6-三氯酚

本文采用间歇试验,对硝酸盐还原条件下Fe0/厌氧微生物联合体系降解2,4,6-三氯酚(2,4,6-TCP)进行了研究。考察了不同硝酸盐浓度下,体系中pH、硝酸盐浓度以及硝酸盐还原活性的变化情况。结果表明:当2,4,6-TCP初始浓度为20mg/L时,硝酸盐对Fe0/厌氧微生物联合体系降解2,4,6-三氯酚具有明显的抑制作用;且随着硝酸盐浓度的升高,2,4,6-TCP的去除率降低,硝酸盐还原活性升高;体系先发生硝酸盐还原再进行2,4,6-TCP还原脱氯。     

Fe掺杂纳米ZnO光催化处理硝基苯废水

以高压荧光汞灯为光源,以自制Zn1-xFexO为催化剂,研究了悬浆体系中硝基苯污染废水的降解过程及降解规律。考察了硝基苯初始质量浓度、Zn1-xFexO光催化剂的质量浓度、Fe与Zn摩尔比值以及反应温度、pH、反应时间对硝基苯降解过程的影响。结果表明:以Zn1-xFexO作为催化剂可以有效地去除废水中的硝基苯,同时硝基苯的光催化降解过程符合一级反应动力学模型;反应活化能为9.3 k J·mol-1;当Zn0.99Fe0.01O的质量浓度为0.8 g·L~(-1)(Fe/Zn摩尔比为1∶99)、在125 W高压荧光汞灯照射下、硝基苯的初始浓度为400 mg·L~(-1)、反应温度为30℃、pH为3.27、取样时间为4 h时,硝基苯废水的反应速率常数和去除率分别为0.0136 min-1和98.88%;硝基苯的去除率和反应速率常数与Zn0.99Fe0.01O的质量浓度、Fe/Zn掺杂比例以及硝基苯初始浓度、溶液pH、反应温度等因素有关;同时,自制的Zn0.99Fe0.01O催化剂显著降低了反应活化能,从而提高了硝基苯污染废水的光降解效果。     

厌氧微生物降解多环芳烃研究进展

多环芳烃(PAHs)是一类普遍存在于环境介质中的难降解有机污染物,相对于好氧微生物降解PAHs的研究,厌氧微生物降解PAHs的研究则相对较少.本文从厌氧微生物降解PAHs的研究背景,厌氧降解微生物的特点和不同厌氧降解还原反应体系的角度综述了厌氧微生物降解PAHs的概况;结合厌氧微生物降解萘和菲转化途径的介绍,推断了其降解机制的内在原因;同时通过总结影响厌氧微生物降解PAHs的主要因素(包括:PAHs的生物可利用性、外源营养物质的添加、外源电子受体的添加、特定厌氧降解菌的筛选强化和部分环境因素等),指出了制约降解进程的潜在限制因子;并对厌氧微生物降解PAHs研究目前存在的问题和未来的发展方向作了简述与展望.     

共存甲烷短杆菌Methanobrevibacter thaueri F1提高梨囊鞭菌Piromyces sp. F1对硝呋烯腙的耐受性

【背景】硝呋烯腙能够抑制厌氧真菌。共存甲烷菌可以促进厌氧真菌的生长以及对木质纤维素的降解,然而关于共存甲烷菌对厌氧真菌抗逆性影响的研究较少。【目的】旨在研究甲烷菌共存对厌氧真菌耐受硝呋烯腙的影响。【方法】采用体外批次培养,以稻草为底物,添加不同浓度的硝呋烯腙(0、5、10、25 mg/L),分别接种厌氧真菌纯培养和厌氧真菌与甲烷菌共培养悬浮液,于39°C静置培养96 h。测定不同时间点的产气量和甲烷产量,结束后测定p H、干物质降解率(DMD)、中性洗涤纤维消失率(NDFD)、半纤维素消失率(ADSD)、酸性洗涤纤维消失率(ADFD)以及上清液中甲酸、乳酸和乙酸的浓度。【结果】添加5、10和25 mg/L硝呋烯腙皆显著降低了厌氧真菌纯培养的发酵活性(P0.05);添加5 mg/L硝呋烯腙没有显著降低厌氧真菌与甲烷菌共培养的发酵活性(P0.05),添加10和25 mg/L硝呋烯腙则显著降低了共培养发酵活性(P0.05);比较5、10 mg/L硝呋烯腙对纯培养和共培养发酵活性影响的结果表明,共培养发酵活性显著高于纯培养发酵活性(P0.05)。【结论】硝呋烯腙对厌氧真菌纯培养和厌氧真菌与甲烷菌共培养的抑制作用都存在剂量效应,在一定添加浓度范围内(25 mg/L),甲烷菌共存可以显著提高厌氧真菌对硝呋烯腙的耐受性。     

磁铁矿对奥奈达希瓦氏菌MR-1厌氧还原甲基橙性能的影响

【目的】在微生物对染料的厌氧还原转化过程中,前人研究发现磁铁矿可以作为胞外电子传递介质提高或降低染料的微生物还原速率,这两种截然不同的作用结果背后的作用机制仍亟待阐明。【方法】利用水热法合成磁铁矿,选择甲基橙作为微生物胞外还原的典型偶氮染料,研究磁铁矿对奥奈达希瓦氏菌MR-1厌氧还原甲基橙(methyl orange, MO)的影响。【结果】研究发现磁铁矿对MO的降解表现出明显的浓度依赖性效应：同只添加细菌组相比,低浓度组(20-50 mg/L) MO的脱色效率提高了4.07%-10.64%,而高浓度组(100-200 mg/L)下降了3.92%-18.35%。进一步研究发现磁铁矿浓度变化对MO微生物还原的影响与染料在矿物表面的分配无关,主要体现在影响细胞表面形态、代谢活性和电子传递效率等方面。低浓度组ATP生成量提高了1.08%-7.65%,生成了0.033-0.051 mg/L Fe²⁺,而高浓度组ATP生成量降低了38.74%-60.14%,Fe²⁺浓度增至0.091 mg/L。此外,外源Fe²⁺的实验结果证明Fe²⁺对MO的厌氧还原同样表现出低浓度(0.01-0.02 mg/L)促进,高浓度(＞0.05 mg/L)抑制的影响趋势。【结论】低浓度磁铁矿未影响细菌细胞形态,提高了细胞代谢活性,体系中少量的溶解态Fe²⁺有利于MO微生物还原,而高浓度磁铁矿则表现出相反的影响趋势。本研究为全面理解磁铁矿对胞外电子传递的影响及其在有机污染物还原转化中的应用提供了参考。     

外源氧化铁对水稻土中有机酸含量的影响

在水稻土泥浆中添加Fe(OH) 3 可显著降低乙酸浓度 .在新鲜水稻土样品中 ,由于添加Fe(OH) 3导致对乙酸的竞争消耗 ,在培养 5d后 ,乙酸浓度降至 10～ 2 0 μmol·L-1的稳态浓度 ,而此刻对照中的乙酸浓度仍在 12 0 0 μmol·L-1以上 .在乙酸产生量较低的土壤中 ,添加Fe(OH) 3 可完全消耗体系中的乙酸 ,并导致产CH4过程的完全被抑制 .添加纤铁矿同样可使乙酸浓度显著减少 ,但作用效果不如无定形氧化铁 .添加赤铁矿可造成培养初期 (10d以内 )乙酸的大量积累 ,但并不引起产CH4量的增大 .添加Fe(OH) 3 、纤铁矿及铝取代针铁矿 ,能引起厌氧培养的水稻土中丙酸浓度的降低 ,其抑制效率为Fe(OH) 3 >纤铁矿 >铝取代针铁矿 .新鲜土样和经过 11周厌氧处理后的土样中 ,有机酸种类和含量有较大差别 .     

金属离子对嗜热菌BF80生长及苯酚降解的影响研究

探测了17种金属离子对嗜热菌BF80菌生长和降解苯酚的影响。结果表明：与对照相比, 0.01%的Cu2+、Zn2+、Co2+、Ba2+、Hg2+、Ni2+、Ag+ 和Al3+对嗜热菌BF80有强抑制作用; Cr2+对嗜热菌BF80的苯酚降解特性有强抑制作用, 而其生长量只受到一定的抑制作用; Sn2+、Fe2+、Fe3+和Pn2+ 对嗜热菌BF80的生长和苯酚降解有一定抑制作用, 该作用随金属粒子浓度的增加而增大; 低浓度Mn2+ 和Mo2+可以使其生长量增大且促进苯酚降解, 但超过0.1%的浓度则抑制其生长; Ca2+ 和Mg2+可以加速嗜热菌BF80的生长和降解苯酚的速率, 但对苯酚的最大降解率却几乎没有影响; Mo2+ 和Mn2+的复合作用使嗜热菌BF80的生长量更大, 但是苯酚降解率却比分别单独添加Mo2+ 和Mn2+时低。     

微生物烟气脱硫中硫酸盐还原阶段的限制性因素及其影响

【目的】利用硫酸盐还原菌(SRB)厌氧活性污泥进行烟气脱硫,探索硫酸盐生物还原的最适条件及重金属离子对硫酸盐生物还原的影响,以提高硫酸盐还原阶段的效率。【方法】对取自污水处理厂的SRB厌氧活性污泥进行高浓度硫酸盐胁迫驯化。分析生物脱硫过程中SRB厌氧污泥还原硫酸盐的限制性因素及影响。【结果】在最适生长条件下(pH 6.5,32°C),经驯化获得的SRB厌氧活性污泥有较强的硫酸盐还原能力。Fe2+的适量添加对硫酸盐还原有一定促进作用。SRB厌氧污泥还原硫酸盐的ThCOD/SO42-最适值为3.00,ThCOD=3.33为最适理论化学需氧量,硫酸盐还原率可达72.15%。SRB厌氧污泥还原硫酸盐反应体系中抑制SRB活性的硫化物浓度为300 mg/L。Pb2+和Ni2+在较低的浓度下(1.0 mg/L和2.0 mg/L)对硫酸盐的还原产生较强的抑制作用,而Cu2+在稍高的浓度下(8.0 mg/L)显示出明显的抑制作用。【结论】经驯化,SRB厌氧活性污泥显示出较强的硫酸盐还原能力,具有应用于工业烟气生物脱硫的潜力。去除重金属离子Pb2+、Ni2+和Cu2+可有效解除对硫酸盐生物还原作用的抑制。     

Reduction of nitrobenzene with H2 using a microbial consortium

Proof of concept was obtained that nitrobenzene can be reduced to aniline by a mixed reductive microbial culture using H2 as the sole electron donor source. In a continuous-flow anaerobic bioreactor, both pH and temperature affected nitrobenzene reduction with optima of pH 6.5-6.8 and 30 degrees C. The efficiency of nitrobenzene degradation increased with H2 up to 10% (v/v). An increase in sulfate concentration decreased the removal rate of nitrobenzene.     

Response of the microflora in outdoor experimental streams to pentachlorophenol: environmental factors

The 2nd year of a 2-year study of the fate of pentachlorophenol in outdoor artificial streams focused on details of microbial degradation by a combination of in situ and laboratory measurements. Replicate streams were dosed continuously at pentachlorophenol concentrations of 0, 48, and 144 micrograms/L, respectively, for an 88-d period during the summer of 1983. Pentachlorophenol was degraded both aerobically and anaerobically. Aerobic degradation was more rapid than anaerobic degradation. Mineralization of pentachlorophenol was concommitant with pentachlorophenol disappearance under aerobic conditions, but lagged behind loss of the parent molecule under anaerobic conditions. Biodegradation in the streams, or in specific stream compartments such as the sediment or water column, was characterized by an adaptation period (3-5 weeks for the stream as a whole, and reproducible from the previous year), which was inversely dependent on the concentration of pentachlorophenol and microbial biomass. The adaptation in the streams could be attributed to the time necessary for selective enrichment of an initially low population of pentachlorophenol degraders on surface compartments. The extent of biodegradation in the streams (percent loss of initial concentration of pentachlorophenol) increased with increasing pentachlorophenol input, which was explicable by an increase in the pentachlorophenol degrader population with increasing pentachlorophenol concentration. The sediment zone most significant to overall pentachlorophenol biodegradation was the top 0.5- to 1-cm layer as shown by pentachlorophenol migration rates and depth profiles of degrader density within the sediment. Pentachlorophenol profiles in sediment cores taken during and after the adaptation period for degradation showed that diffusion of pentachlorophenol into the sediment was rate limiting to degradation in this compartment.(ABSTRACT TRUNCATED AT 250 WORDS)     

Anaerobic biodegradation of 1,4-dioxane by sludge enriched with iron-reducing microorganisms

The potential on anaerobic biodegradation of 1,4-dioxane was evaluated by use of enriched Fe(III)-reducing bacterium sludge from Hangzhou municipal wastewater treatment plant. The soluble Fe(III) supplied as Fe(III)-EDTA was more available for the Fe(III)-reducing bacterium in the sludge compared to insoluble Fe(III) oxide. The addition of humic acid (HA) further stimulated the anaerobic degradation of 1,4-dioxane accompanying with apparent reduction of Fe(III) which is believed that HA could stimulate the activity of Fe(III)-reducing bacterium by acting as an electron shuttle between Fe(III)-reducing bacterium and Fe(III), especially for insoluble Fe(III) oxides. After 40-day incubation, the concentration of 1,4-dioxane dropped up to 90% in treatment of Fe(III)-EDTA+HA. Further study proved that more than 50% of the carbon from 1,4-dioxane was converted to CO2 and no organic products other than biomass accumulated in the growth medium. The results demonstrated that, under the appropriate conditions, 1,4-dioxane could be biodegraded while serving as a sole carbon substrate for the growth of Fe(III)-reducing bacterium. It might be possible to design strategies for anaerobic remediation of 1,4-dioxane in contaminated subsurface environments.     

Biodegradation of naphthalene by enriched marine denitrifying bacteria

Numerous studies have been investigated on the PAHs biodegradation in aerobic and anaerobic environments; however, the biodegradation of PAHs under anoxic conditions, especially denitrifying conditions, has drawn less attention. In this study, four series of batch experiments were conducted to investigate the effect of temperature, pH, naphthalene concentration and nitrate concentration on the naphthalene degradation under denitrification condition. Our results showed that the degradation of naphthalene was most favorable at pH 7 and 25 °C. Results also indicated that 30 mg/l naphthalene inhibited the biodegradation and the removal efficiency was only 20.2%. Significant degradation (91.7% and 96.3%) of naphthalene occurred when nitrate concentrations were 1.0 and 5.0 mM. Moreover, the maximum degradation rates were 0.13 and 0.18 mg-NAP/(l h) depending on the concentration of nitrate. Based on 16S rDNA analysis, the denitrifying enriched culture was mainly composed of ??-Proteobacteria (19 clones out of a total of 23 clones) and Actinobacteria (4 clones). Using a primer set specific for naphthalene degrading functional gene nahAc, two operational taxonomy units were obtained in the clone library of nahAc. Both of them were closely related to nahAc genes of known species of Pseudomonas. Quantitative polymerase chain reaction (qPCR) was employed to quantify the change of naphthalene-degrading population during the degradation of naphthalene using nahAc gene as the biomarker. The maximum degradation rate and removal efficiency were strongly correlated with nahAc gene copy number, with R² of 0.69 and 0.79, respectively.     

不同电子供体对2,4-二氯酚还原脱氯的影响

以葡萄糖、乙酸钠、Fe0、Fe0 葡萄糖、Fe0 乙酸钠作为电子供体,接种未驯化厌氧混合菌,考察2,4-二氯酚(2,4-DCP)的还原脱氯特性及Fe0作为电子供体的最佳作用条件与持续性特征.结果表明:与葡萄糖的作用相比,Fe0 葡萄糖可有效提高目标物脱氯效果;乙酸钠、Fe0及Fe0 乙酸钠均为有效电子供体,其中Fe0作为电子供体时目标物脱氯效果最佳,最佳作用条件为初始pH8.0,Fe0投加量2.0 g/L,4-CP为其主要脱氯中间产物;Fe0可持续供给2,4-DCP还原脱氯所需电子,而乙酸钠不断消耗后其脱氯效果与Fe0作为电子供体有明显差距.     

金属离子对嗜热菌BF80生长及苯酚降解的影响研究

探测了17种金属离子对嗜热菌BF80菌生长和降解苯酚的影响.结果表明:与对照相比,0.01%的Cu2 、Zn2 、CO2 、Ba2 、Hg2 、Ni2 、Al 0和Al3 对嗜热菌BF80有强抑制作用;Cr2 对嗜热菌BF80的苯酚降解特性有强抑制作用,而其生长量只受到一定的抑制作用;Sn2 、Fe2 、Fe3 和Pn2 对嗜热菌BF80的生长和苯酚降解有一定抑制作用,该作用随金属粒子浓度的增加而增大;低浓度Mn2 和Mo2 可以使其生长量增大且促进苯酚降解,但超过0.1%的浓度则抑制其生长;Ca2 和Mg2 可以加速嗜热菌BF80的生长和降解苯酚的速率,但对苯酚的最大降解率却几乎没有影响;Mo2 和Mn2 的复合作用使嗜热菌BF80的生长量更大,但是苯酚降解率却比分别单独添加Mo2 和Mn2 时低.     

Characterization of the nitrobenzene-degrading strain Pseudomonas sp. a3 and use of its immobilized cells in the treatment of mixed aromatics wastewater

A bacterial strain Pseudomonas sp. a3 capable of degrading nitrobenzene, phenol, aniline, and other aromatics was isolated and characterized. When nitrobenzene was degraded, the release of NH(4) (+) was detected, but not of NO(2) (-). This result implied that nitrobenzene might have a partial reductive metabolic pathway in strain a3. However, aniline appeared as one of the metabolites during the aerobic degradation of nitrobenzene. Moreover, the appearance of 2-aminophenol during aniline degradation by strain a3 indicated that novel initial reactions existed during the degradation of nitrobenzene and aniline by strain a3. Strain a3 was immobilized in the mixed carrier of polyvinyl alcohol and sodium alginate to improve its degrading efficiency. The optimal concentrations of polyvinyl alcohol and sodium alginate in the mixed carrier were 9 and 3 %, respectively. The immobilized cells had stable degradation activity and good mechanical properties in the recycling tests. The immobilized cells also exhibited higher tolerances in acidic (pH 4-5) and highly saline (10 % NaCl) environments than those of free cells. The biodegradation of nitrobenzene mixed with aniline and phenol using immobilized cells of Pseudomonas sp. a3 was also greatly improved compared with those of free cells. The immobilized cells could completely degrade 300 mg L(-1) nitrobenzene within 10 h with 150 mg L(-1) aniline and 150 mg L(-1) phenol. This result revealed that the immobilized cells of Pseudomonas sp. a3 could be a potential candidate for treating nitrobenzene wastewater mixed with other aromatics.     

Studies on the physiology of microbial degradation of pentachlorophenol

Summary The requirements and conditions for pentachlorophenol (PCP) biodegradation by a mixed bacterial culture was studied. The effects of oxygen, nutrients, additional carbon sources, pH and temperature are described. Up to 90% of PCP was degraded into CO₂ and inorganic chloride in 1 week at an input concentration of <600 M. Degradation continued when pO₂ was lowered to 0.0002 atm but ceased when pO₂ was further decreased to 0.00002 atm. Supplementary carbon sources, such as phenol, hydroxybenzoic acids or complex nutrients did not affect the biodegradation, but the presence of ammonium salts enhanced the rate of PCP degradation without affecting the yield of CO₂. The degrading organisms were shown to be procaryotic mesophiles; no degradation was shown at temperatures below +8° and above +50°C. The optimum pH for degradation was from 6.4 to 7.2 and at higher pH value (8.4) degradation was inhibited more than at lower pH (5.6).     

Biodegradation of high concentration of nitrobenzene by Pseudomonas corrugata embedded in peat-phosphate esterified polyvinyl alcohol

Efficiency on biodegradation of high concentration of nitrobenzene (NB) by peat-phosphate esterified polyvinyl alcohol-embedded NB-degrading bacteria Pseudomonas corrugata was conducted compared to free bacteria cells. Its biodegradation kinetics, reuse ability, degradation effect in the absence of the essential element needed for the growth of bacteria and degradation efficiency of the raw water from the contaminated site were also invested. Results show that the degradation rate when the concentration of NB was at 600, 750, and 900 mg/L reached 91.02, 83.23, and 55.9 %, which was higher than that observed in free bacteria at the same concentration levels. Biodegradation kinetics of the material could be well described by first- and zero-order kinetics when the concentration of NB was at 300, 450 mg/L and 600, 750, 900 mg/L, respectively. Stable degradation activity (stayed at a level of approximately 70 %) was displayed during the 11th repeat-batch experiment. The affect of absence of phosphorus in the medium can be abated ascribed to the addition of peat, which contributes with organic matter and other elements such as nitrogen and phosphorus necessary to maintain metabolically active the microorganisms. Effective biodegradation of the raw water from the experimental site revealed that the material can be a potential candidate for treating NB-contaminated wastewater in the practical setting.