种泥预处理和发酵温度对暗发酵产氢的影响研究进展

生物质暗发酵产氢不仅可以处理有机废物,同时可以获得清洁能源,实现了废物资源化利用。然而产氢种泥中大量耗氢菌的存在会导致暗发酵氢气产量低等问题,因此种泥预处理是暗发酵产氢的必需条件。随着暗发酵产氢基质的多样化,产氢种泥的预处理方法也不断发展。对近十年来产氢种泥预处理方法的发展进行了综述,并且结合发酵温度,讨论了种泥预处理方法和发酵温度两方面条件对暗发酵产氢的影响,并对该研究方向提出了展望,以期为后续暗发酵产氢的进一步研究提供参考。     

种泥预处理和发酵温度对暗发酵产氢的影响研究进展

生物质暗发酵产氢不仅可以处理有机废物,同时可以获得清洁能源,实现了废物资源化利用。然而产氢种泥中大量耗氢菌的存在会导致暗发酵氢气产量低等问题,因此种泥预处理是暗发酵产氢的必需条件。随着暗发酵产氢基质的多样化,产氢种泥的预处理方法也不断发展。本文对近十年来产氢种泥预处理方法的发展进行了综述,并且结合发酵温度,讨论了种泥预处理方法和发酵温度两方面条件对暗发酵产氢的影响,并对该研究方向提出了展望,以期为后续暗发酵产氢的进一步研究提供参考。     

不同预处理条件对海水养殖废弃物发酵产氢的影响

【目的】利用海水养殖场有机废弃物厌氧发酵产氢,可在减少有机污染物的同时获取氢气。【方法】以海水养殖场有机废弃物为底物,比较嗜热酶(S-TE)、酸、碱、灭菌、微波不同预处理方法对厌氧发酵产氢效果的影响,并对发酵过程中底物性质变化[SCOD、可溶性蛋白质、可溶性糖、pH、VFAs(挥发性脂肪酸)和乙醇]进行探讨。【结果】灭菌预处理产氢效果最好,产氢率为22.0 mL/g VSS,酸处理的效果最差,产氢率为7.6 mL/g VSS。可溶性糖大量消耗之后,氢气不再产生。接种S-TE预处理污泥的底物能更多地释放营养物质,并在整个发酵过程中保持较为稳定的pH值。发酵过程中产生的VFAs主要成分是乙酸,在发酵后期出现乙醇。【结论】灭菌预处理是海水养殖场有机废弃物厌氧发酵产氢的最佳预处理方法,可溶性糖为这一过程主要的营养来源。     

啤酒废水的厌氧发酵产氢

对经热处理后的厌氧污泥利用啤酒废水厌氧产氢的影响因素（温度、初始pH值和有机物浓度）进行了研究。结果表明,温度与初始pH值对厌氧产氢过程均有显著影响。最佳温度为35℃,此时,比产氢速率、氢气产率、VFA含量与总糖降解率均达到最大,分别为10.16mL/g-VSS.h、0.1673mL/mg.COD、4640.0mg/L和95.20%。最适初始pH值为6.0～7.0,在此范围内氢气产率、VFA含量、总糖降解率均可获得最大值。一个半经验模型适用于描述初始pH值与氢气产率之间的相互关系。在35℃、初始pH值6.5的条件下,有机物浓度COD1000mg/L～2000mg/L时,总糖降解率与VFA产率均获得最大值。底物抑制模型分析结果显示COD1587mg/L时,氢气产率（0.1935mL/mg.COD）达到最大。     

微胶囊固定化混合菌群发酵产氢——构建一种虚拟“细胞工厂”的尝试

采用硫酸纤维素钠(NaCS)/聚二甲基二烯丙基氯化铵(PDMDAAC)微胶囊体系,固定混合产氢菌群,构建成一个能高效产氢的虚拟"细胞工厂"。经过菌群活化预处理,激活了产氢活力,进一步通过NaCS/PDMDAAC微胶囊固定化,形成适宜的内部微环境,有效增强了菌群对温度的适应能力,提高了底物浓度,氢气产量比游离细胞增长30%以上,菌体浓度提高2倍到3.2g/L。连续15批培养,囊内菌体浓度显著提高,发酵时间缩短,氢气产率保持在1.73～1.81molH2/molglucose,平均产氢速率提高了198.6%。同时还发现发酵产物中有较高比例的丁酸和乙酸,由此可以使该虚拟"细胞工厂"成为一个多产物联产体系。     

利用餐厨垃圾循环半连续厌氧发酵产氢研究

利用餐厨垃圾采用半连续厌氧发酵进行产氢的研究。实验结果表明以高温(100℃)预处理15 min的厌氧活性污泥为种泥,在温度37℃,pH 6.0左右,较宽的稀释率(1.0~4.0 d-1)范围内,均能较好的实现厌氧发酵产氢。在稀释率D=2.4 d-1下,流出液中乙醇、乙酸、丙酸、丁酸和戊酸的质量分数分别为5.6%、29.6%、5.4%、58.5%和0.9%,产氢过程属于典型的丁酸型发酵,最终氢气的体积分数可达60%,氢气的产生速率为5.49 m3/(m3.d)。将厌氧发酵液相产物作为稀释液返回到反应器中,反应器的产氢能力大幅度的提高,当回流比R=0.8时,最大产氢速率可达10.9 m3/(m3.d),最终氢气的含量可达65%,厌氧发酵反应器的产氢能力提高了约130%。     

光合细菌产氢因子的研究进展

光合细菌在固氮的同时释放氢气。产氢与固氮是同步进行的。固氮酶与氢酶共同影响光合细菌的产氢活性,而外源生理条件又影响着固氮酶与氢酶的活性,其中有机碳阻抑吸氢酶表达,促进产氢;氨则抑制固氮活性而降低产氢量;氧气的存在使固氮酶与氢酶都失活,从而抑制放氢反应的进行。     

预处理对泔脚发酵产氢的强化研究

采用热(80℃,15 min)预处理的城市生活垃圾厌氧消化污泥为接种物,考察了不同预处理方法对泔脚中温(36℃)批式发酵产氢的影响。Gompertz模型拟合结果表明:微波850 W,4 min与pH9.0下预处理泔脚的发酵产氢延迟时间λ、最大比产氢率、产氢率、生物气中氢气的最高体积分数分别为:3.47 h,9.43 mL/(g.h),186.23 mL/g及46.0%时,具有更大的产氢优越性。泔脚的发酵产氢过程也是一个酸化过程,发酵产氢结束后,4个预处理方案的发酵产氢余物的pH在4.40~5.00之间,pH均有较大幅度的下降。     

玉米芯发酵法生物制氢

在批式培养试验中, 以牛粪堆肥为天然产氢菌源, 玉米芯为底物, 通过厌氧发酵生产氢气。系统考察了底物预处理条件、初始pH值和底物浓度对玉米芯产氢能力的影响。在初始pH 8.0, 1.0%盐酸预处理底物30 min, 底物浓度10 g/L的最佳产氢条件下, 玉米芯最大产氢能力〔每克TVS（总挥发性固体物）产氢量〕和最大产氢速率（每克TVS每小时产氢量）分别为107.9 mL /g、4.20 mL/g·h-1。玉米芯经酸预处理后半纤维素含量由42.2%下降至3.0%, 而酸预处理的玉米芯产氢前后纤维素、半纤维素和木质素含量只有少量变化。产氢菌主要用酸预处理产生的可溶性糖产氢, 故底物的酸预处理对玉米芯的发酵产氢非常重要。用傅里叶变换红外光谱(FTIR)分析显示酸预处理和产氢过程中玉米芯的特征峰发生变化, 酸预处理过程降解了底物纤维素的无定形区和半纤维素, 产氢微生物对纤维素的结晶区有破坏作用。     

玉米芯发酵法生物制氢

在批式培养试验中, 以牛粪堆肥为天然产氢菌源, 玉米芯为底物, 通过厌氧发酵生产氢气。系统考察了底物预处理条件、初始pH值和底物浓度对玉米芯产氢能力的影响。在初始pH 8.0, 1.0%盐酸预处理底物30 min, 底物浓度10 g/L的最佳产氢条件下, 玉米芯最大产氢能力〔每克TVS（总挥发性固体物）产氢量〕和最大产氢速率（每克TVS每小时产氢量）分别为107.9 mL /g、4.20 mL/g·h-1。玉米芯经酸预处理后半纤维素含量由42.2%下降至3.0%, 而酸预处理的玉米芯产氢前后纤维素、半纤维素和木质素含量只有少量变化。产氢菌主要用酸预处理产生的可溶性糖产氢, 故底物的酸预处理对玉米芯的发酵产氢非常重要。用傅里叶变换红外光谱(FTIR)分析显示酸预处理和产氢过程中玉米芯的特征峰发生变化, 酸预处理过程降解了底物纤维素的无定形区和半纤维素, 产氢微生物对纤维素的结晶区有破坏作用。     

Sludge minimisation technologies

The treatment and disposal of excess sludge represents a bottleneck of wastewater treatment plants all over the world, due to environmental, economic, social and legal factors. There is therefore a growing interest in developing technologies to reduce the wastewater sludge generation. The goal of this paper is to present the state-of-the-art of current minimisation techniques for reducing sludge production in biological wastewater treatment processes. An overview of the main technologies is given considering three different strategies: The first option is to reduce the production of sludge by introducing in the wastewater treatment stage additional stages with a lower cellular yield coefficient compared to the one corresponding to the activated sludge process (lysis-cryptic growth, uncoupling and maintenance metabolism, predation on bacteria, anaerobic treatment). The second choice is to act on the sludge stage. As anaerobic digestion is the main process in sewage sludge treatment for reducing and stabilising the organic solids, two possibilities can be considered: introducing a pre-treatment process before the anaerobic reaction (physical, chemical or biological pre-treatments), or modifying the digestion configuration (two-stage and temperature-phased anaerobic digestion, anoxic gas flotation). And, finally, the last minimisation strategy is the removal of the sludge generated in the activated sludge plant (incineration, gasification, pyrolysis, wet air oxidation, supercritical water oxidation).     

Sludge Reduction with a Novel Combined Worm-reactor

In China, as a result of economic, environmental and regulation factors, excess sludge treatment and disposal represents a rising challenge for small and mid-scale municipal wastewater treatment plants (WWTPs). Although the presence of worms in aerobic wastewater treatment may lead to substantial sludge reduction, the practical application is still uncontrollable because of unstable worm growth. To overcome unstable worm growth in activated sludge process, a combined worm-reactor, consisting of sections for both free-swimming and sessile worms, was developed to enhance worm growth. This plug flow type of worm-reactor has the sessile worm growing section filled with plastic carriers, and recirculation of sludge from the section for sludge settling was carried out in order to avoid worm washing out. Sludge reduction of treating the discharged excess sludge using this worm-reactor was investigated during 53 days. In the start-up phase the combined worm-reactor was inoculated with Tubificidae. Tubificidae mainly occurred in the carriers and on the bottom of the worm-reactor, however, neither Aeolosoma nor Nais was found in the worm-reactor. Results clearly showed that the average sludge reduction was 48%, and the COD removal was low, about 8%. High NH₄⁺ -N or NO₂⁻ -N concentrations or their combination may limit the growth of Tubificidae. Few PO ₄³⁻-P release into the effluent was observed in the worm-reactor. However, results obtained from this study cannot unequivocally be attributed to the presence of worms because it did not include a control system, and thus much more work will be needed in this concept in the further research.     

Biological Degradation of Crude Oil Refinery Sludge with Commercial Surfactant and Sewage Sludge by Co-Composting

This study determined the potential of surfactant and sewage sludge in enhancing degradation of oil sludge. A mixture of oil sludge, surfactant, and sewage sludge was co-composted for 24 weeks in the laboratory. Physical and chemical parameters in the compost were measured every four weeks. Isolated microorganisms were characterized by molecular techniques. The pH in all experiments remained between 8 and 6.4. CO₂ evolution reached 5503 µg/dwt/day by the twenty-fourth week. The dominant bacterial species were Acinectobacter, Rodococcus, mycobacterium, Pseudomonas, Bacillus, Arthrobacter, and Staphylococcus species and fungi were Pleurotus, Penicillium, and Aspergillus sp. TPH was reduced by 92% in the sewage sludge and surfactant treatment, 75 and 81% in other treatments, and 44.2% in the control. PAH concentrations were reduced by between 75 and 100%. The results indicate that a careful application of surfactant and sewage sludge could enhance oil sludge degradation in a compost system.     

活性污泥总DNA提取方法的研究

采用冻融＋玻璃珠、溶菌酶＋SDS和冻融＋玻璃珠＋溶菌酶＋SDS的方法提取活性污泥的微生物总DNA,并对以上三种方法进行比较,从中确定最佳的方法,以实现普通实验条件下成功提取符合PCR扩增要求的DNA。经紫外光度分析及电泳结果表明,冻融＋玻璃珠＋溶菌酶＋SDS方法所得的DNA的OD260/OD280为1．81,电泳结果显示,所提DNA片段分子量大于10kb,适于酶解和PCR扩增要求,为PCR技术应用于活性污泥的研究提供了一种简便、可靠的DNA提取方法。     

Enhanced Methane Production from Anaerobic Digestion of Disintegrated and Deproteinized Excess Sludge

To improve biogas yield and methane content in anaerobic digestion of excess sludge from the wastewater treatment plant, the sludge was disintegrated by using various methods (sonication, alkaline and thermal treatments). Since disintegrated sludge contains a high concentration of soluble proteins, the resulting metabolite, ammonia, may inhibit methane generation. Therefore, the effects of protein removal from disintegrated sludge on methane production were also studied. As a result, an obvious enhancement of biogas generation was observed by digesting disintegrated sludge (biogas yield increased from 15 to 36 ml/g COD_added·day for the raw excess sludge and the sonicated sludge, respectively). The quality of biogas was also improved by removing proteins from the disintegrated sludge. About 50% (w/w) of soluble proteins were removed from the suspension of disintegrated sludge by salting out using 35 g MgCl₂·6H₂O/l and also by isoelectric point precipitation at pH 3.3. For deproteinized sludge, methane production increased by 19%, and its yield increased from 145 ml/g COD_removed to 325 ml/g COD_removed. Therefore, the yield and quality of biogas produced from digestion of excess sludge can be enhanced by disintegrating the sludge and subsequent protein removal. Revisions requested 14 November 2005; Revisions received 13 January 2006     

利用污泥提取液制备微生物絮凝剂

以污水厂剩余污泥作为培养基原料,经过一系列处理,探索微生物絮凝剂产生菌的最适发酵培养基配方,结果表明,污泥预处理条件以pH 12碱解条件最优,碳氮源产出量最大,补加8 g/L葡萄糖后灭菌,微生物絮凝剂产生菌LLin6可正常产絮,絮凝率达91.55%。该结果为降低微生物絮凝剂的制备成本,并实现污泥的减量化和污泥资源化利用提供了基础。     

Sludge and lignin as growth media for the production of antimicrobial substances by selected microorganisms

Abstract

The ability of sludge, lignin and humic acid to support the growth and production of antimicrobial substances by 19 microorganism strains was tested. Organisms from seven genera: Bacillus, Pseudomonas, Streptomyces, Beauveria, Paecilomyces, Trichoderma and Trichosporon grew on the tested media. On these media, they were also examined for the production of anti-phytopathogenic activity against Fusarium oxysporum P1 BIM, Botrytis cinerea B1 BIM and Pseudomonas syringae. pv. glicinea B-280 BIM. Strains Pseudomonas aurantiaca S-1, Bacillus sp. 19 and Streptomyces sp. 11 synthesize antimicrobial metabolites on the different media. Protease, cellulase, α-amylase, xylanase and peroxidase were also produced by the same microorganisms, which can explain their ability to grow on sludge, and laccase was produced only by P. aurantiaca S-1. HPLC analysis of the lignin culture media before and after P. aurantiaca S-1 growth has shown that the major lignin peak in the culture broth disappeared.     

城市污泥好氧发酵菌种放线菌的初步筛选

目的：微生物好氧发酵处理城市污泥是解决我国大中城市污水厂污泥的一种切实可行的方法,放线菌在其中起关键作用,该研究尝试分离筛选降解污泥的放线菌。方法：采用菌种分离方法,淀粉、蛋白质、纤维素水解实验进行进一步筛选。结果：从城市污泥中筛选到8个放线菌菌株。这些菌株对淀粉、蛋白质和纤维素都有一定的水解能力,其中A1和A7菌株分解淀粉和蛋白质的能力都比较强,淀粉水解实验的透明圈Up值分别为9．0和11．1,明胶液化程度也最高。A7和A8菌株分解纤维素的能力较强,透明圈Up值均为4．0。结论：A1、A7和A8菌株可以应用于城市污泥的好氧发酵。     

含油污泥微生物处理技术研究

针对胜利油田现河采油厂和滨南采油厂联合站罐底污泥的含油污泥进行了微生物处理技术研究工作。主要是利用微生物分离含油污泥的油、泥和降解污泥中的污染物的性能,达到油泥分离和污染物降解的目的。经过了微生物的分离、筛选和诱导培养,选育到了合适的菌株,利用该菌株对含油污泥经厌氧处理后再进行好氧脱油实验,对污泥中脱出原油进行回收。结果表明：所选菌株可以使含油23000mg/kg的含油污泥在4h内脱油到。10100mg/kg,脱油率达到53．4％;微生物降解实验中,随着时间的延长,油去除率越高,降解效果越明显,当处理时间为60d处理后的污泥达到排放标准。     

厌氧颗粒污泥微生物总DNA的提取

目的:为了从分子水平上了解厌氧颗粒污泥中微生物的种类和数量,研究一种高效提取环境微生物DNA的方法。方法:厌氧颗粒污泥样品经液氮速冻、沸水浴融化、溶菌酶处理和SDS裂解后,琼脂糖凝胶电泳检测所提取的DNA,以提取的总DNA为模板,进行细菌核糖体小亚基16S rDNA基因V8、V9区的PCR扩增。结果:经检测,其DNA片段约为20 kb,样品D260nm/D280nm值为1.88,扩增结果理想,与OMEGA公司提供的试剂盒提取效果基本一致。结论:为薯类酒糟厌氧发酵污泥中微生物群落的分子生态学研究提供了一种简便、可靠的DNA提取方法。