高温好氧反硝化菌的分离鉴定及其反硝化性能研究

通过高温筛选,从燃煤电厂生物滴滤系统填料的生物膜上分离出1株高效好氧反硝化细菌TAD1.该菌株革兰氏染色呈阴性,短杆状,大小为(0.67～0.89)μm×(1.03～1.41)μm;经生理生化特性和基于16S rDNA序列分析,初步鉴定该菌为螯台球菌属(Chelatococcus 8p.).对菌株TAD1的反硝化性能进...     

高温下好氧污泥接种启动UASB的试验研究

采用高温UASB处理柠檬酸废水,研究利用好氧脱水污泥接种启动高温UASB的可行性。试验结果表明,在温度55℃,HRT为6天的条件下,UASB反应器能降解的柠檬酸废水浓度为10000mg/L,容积负荷为1.67gCOD/(L.d),柠檬酸废水的去除率达到90%以上。     

应用新型好氧堆肥反应器连续投加处理人粪便的研究

针对间歇式堆肥反应器处理效率低、不便移动、单次投加所需物料量大等不足,以及为更有效地处理分散型人粪便,使人粪便资源化,开发了梨形筒式好氧堆肥反应器。在获得该反应器的最佳通风与搅拌频率分别为3.0 L/min,5 min/h以及最佳m（粪便）︰m（锯末）为1︰2.5的条件下进行连续投加人粪便好氧堆肥。在不接种微生物的30 d堆制过程中,升-降温周期为36 h,平均温度为51.44℃,第15天时COD降解率达到63.99%并趋于稳定,TN损失率第17天时达到56.68%,GI于第21天时达到106.25%,堆肥完全腐熟,稳定期处理效率为23.81 g/（L·d）。接种土著菌种时,升-降温周期缩短至24 h,平均温度为53.96℃,COD降解率8 d可达65.28%,TN 损失率仅为25.75%,GI于第8天达到108.22%,稳定期处理效率可达35.71 g/（L·d）,比不接种时提高1.5倍,同时节约能耗50%。     

SFBR中好氧颗粒污泥的培养及特性研究

接种自行培养的活性污泥,以模拟废水为基质,采用连续进水、间歇出水及厌氧/好氧交替的运行模式,尝试了在SFBR中进行好氧颗粒污泥的培养,并研究了好氧颗粒污泥的特性及反应器对污染物的去除效果.结果表明,通过逐步缩短沉降时间,28 d时成功培养出好氧颗粒污泥,所形成的好氧颗粒污泥呈黄色、形状不规则,且粒径较小(平均粒径0.56 mm),正常情况下的SVI保持在70 mL·g-1以下,EPS在59 d时达到最大值(以MLVSS计)373.24 mg·g-1,较培养初期增加了约2.5倍,运行后期由于颗粒出现解体,导致EPS急剧下降;反应器在运行过程中未能保持较高的污泥量,中后期MLSS始终在3 000mg·L-1以下;在63 d的运行时间里,除异常波动外,反应器对COD的去除率基本维持在90%左右,正常情况下出水COD小于100 mg·L-1,反应器对NH+4-N、TIN的去除效果波动较大,去除率分别为44.45%~94.72%及43.87%~93.13%,反应器对TP的去除率在44.50%~97.40%之间,正常情况下TP去除率可维持在60%以上;限于自动控制水平,夜间长时间的好氧饥饿期容易造成丝状菌过度生长,使得AGS在生长竞争中处于劣势,最终导致了AGS的解体.     

海水异养硝化-好氧反硝化芽孢杆菌SLWX2的筛选及脱氮特性

从分离自刺参养殖环境的7株候选菌株中筛选出1株具有较强异养硝化和好氧反硝化能力的菌株SLWX_2,通过形态学特征、生理生化特性和16S rRNA基因测序分析鉴定其为花津滩芽孢杆菌(Bacillus hwajinpoensis).该菌株脱氮特性研究结果表明,SLWX_224 h对氨氮、亚硝酸氮和硝酸氮的去除率分别达到100%、99.5%和85.6%;当3种无机氮源同时存在时,菌株优先利用氨氮,再利用NO_2~--N和NO_3~--N,72 h 3种无机氮的质量浓度均降至0.013 mg·L~(-1)以下,表明该菌株能同时进行异养硝化和好氧反硝化完成脱氮;在氨氮负荷500 mg·L~(-1)、亚硝酸氮负荷100 mg·L·~(-1)和硝酸氮负荷200 mg·L~(-1)范围内,该菌的脱氮能力不受明显抑制,对3种形态的氮均有良好去除效果,96 h最多可去除180 mg NH_4~+-N、30 mg NO_2~--N和120 mg NO_3~--N,并且在硝化过程中没有亚硝酸氮积累.该菌株在海水养殖和高盐高氮工业废水的脱氮处理方面具有更大潜力.     

温度对好氧颗粒污泥处理纤维素乙醇废水脱氮效能的影响

采用SBR反应器,考察了温度对好氧颗粒污泥处理纤维素乙醇废水脱氮性能的影响.研究结果表明,当进水为纤维素乙醇废水原水时,稳定阶段不同温度(10、20、30℃)条件下体系对COD的去除率分别为10.2%、12.7%、13.7%;总无机氮的去除率分别为42.8%、53.6%、70.5%,温度的升高明显地提高了硝化菌的活性和生长速率,进而促进了脱氮效果.当进水为纤维素乙醇废水经IC工艺处理后的厌氧出水时,3个温度条件下系统对废水中有机物的去除效果无较大差异,去除率均低于15%,主要因为纤维素乙醇废水的厌氧处理出水中的有机物很难被微生物利用;而温度对脱氮效果影响较大,30℃下NH_4~+-N去除率达到60.9%,分别是10℃和20℃时的2.0和1.3倍,并且,随着温度的升高总无机氮的去除率增强,NO_3~--N的去除量增加.由于体系COD去除率低说明反硝化可利用的碳源不足,因此,系统内可能存在内碳源反硝化作用,而且内碳源反硝化作用也随着温度的升高而增强.通过氮平衡计算可知,3个温度条件下氮损失分别为37.6%、45.0%、53.6%,说明温度的升高不仅提高了硝化菌活性,还促进了内碳源反硝化,进而提高了对氮素的去除.     

Degradation of Polylactic Acid (PLA) Plastic in Costa Rican Soil and Iowa State University Compost Rows

In this study the degradation of polylactic acid (PLA) plastic films in Costa Rican soil and in a leaf composting environment was investigated. Three types of PLA films were used: Ch-I, (PLA monolayer plastic films from Chronopol, Golden, CO), GII (PLA trilayer plastic films from Cargill Dow Polymers LLC, Minnetonka, MN), and Ca-I (PLA monolayer plastic films from Cargill Dow Polymers LLC). The average soil temperature and moisture content in Costa Rica were 27°C and 80%, respectively. The average degradation rate of PLA plastic films in the soil of the banana field was 7675 M _w/week. Two compost rows were set up at the Iowa State University (ISU) (Ames) compost site. Temperature and relative humidity of the compost rows were kept at 55 ± 5°C and 50 ± 10% RH, respectively. The degradation rates of GII and Ca-I in the compost rows were 113,290 and 71,283 M _w/week, respectively. Therefore, it was estimated that in Costa Rican soil and in compost rows, PLA would be visibly degraded in 6 months and in 3 weeks, respectively.     

Miscibility and Biodegradability of Poly(Butylene Succinate)/Poly(Butylene Terephthalate) Blends

As one of the biodegradable polymers, the blend of poly(butylene succinate) and poly(butylene terephthalate) is dealt with in this study. In our previous work, it was demonstrated that PBS and PBT are immiscible not only from the changes of T _g but also from logG–log G plots. It is expected that the biodegradability of the blends could be improved by enhancing the miscibility. We tried to induce the transesterification reaction between two polyesters with various time intervals to enhance the miscibility of the blends. The extent of transesterification reaction was examined by ¹H-NMR. We utilized a dynamic mechanical thermal analyzer and a rotational rheometer to investigate the changes in miscibility. We also verified the biodegradability of PBS/PBT blends after the transesterification reaction by the composting method.     

利用城市生活垃圾制取有机复合肥

用城市生活垃圾经好氧高温制成堆肥,并向其中加入无机化肥和微量元素添加剂可制成有机复合肥。本文简要阐述了好氧高温堆肥的生产工艺,推荐了用垃圾生产有机复合肥的两类配方。     

Dynamic of functional microbial groups during mesophilic composting of agro-industrial wastes and free-living (N2)-fixing bacteria application

Although several reports are available concerning the composition and dynamics of the microflora during the composting of municipal solid wastes, little is known about the microbial diversity during the composting of agro-industrial refuse. For this reason, the first parts of this study included the quantification of microbial generic groups and of the main functional groups of C and N cycle during composting of agro-industrial refuse. After a generalized decrease observed during the initial phases, a new bacterial growth was observed in the final phase of the process. Ammonifiers and (N₂)-fixing aerobic groups predominated outside of the piles whereas, nitrate-reducing group increased inside the piles during the first 23 days of composting. Ammonia-oxidizing bacteria (AOB) and nitrite-oxidizing bacteria (NOB), showed an opposite trend of growth since ammonia oxidation decreased with the increase of the nitrite oxidation activity. Pectinolytics, amylolytics and aerobic cellulolytic were present in greater quantities and showed an upward trend in both the internal and external part of the heaps.Several free-living (N₂)-fixing bacteria were molecularly identify as belonging especially to uncommon genera of nitrogen-fixing bacteria as Stenotrophomonas, Xanthomonas, Pseudomonas, Klebsiella, Alcaligenes, Achromobacter and Caulobacter. They were investigated for their ability to fix atmospheric nitrogen to employ as improvers of quality of compost. Some strains of Azotobacter chrococcum and Azotobacter salinestris were also tested. When different diazotrophic bacterial species were added in compost, the increase of total N ranged from 16% to 27% depending on the selected microbial strain being used. Such microorganisms may be used alone or in mixtures to provide an allocation of plant growth promoting rhizobacteria in soil.