环保菌剂应用于焦化废水处理中试

以河北省某煤化工企业污水处理车间缺氧池出水为处理对象,通过添加自行研发的环保菌剂,考察其对实际焦化废水COD去除效果;利用聚合酶链式反应和变性梯度凝胶电泳联合技术(PCR-DGGE)分析添加环保菌剂前后生化系统中污泥微生物群落的变化。研究表明:通过添加环保菌剂,中试系统出水COD平均去除率比活性污泥系统提高了18%;PCR-DGGE结果显示,经过菌剂强化后的生化系统中污泥微生物的种类更加丰富,优势微生物由原先的14种增加到了23种。     

富硫沉积生境中微生物群落的垂直分布特征

为探讨富硫沉积环境中特定微生物类群对硫循环的贡献,人工建立富含硫酸盐的模型,对模型中各种环境化学参数进行监测,并采用不依赖于培养的微生物分子生态学技术对微生物群落垂向分布特征进行解析.结果表明,以沉积物-水界面为分界线,上层水相为好氧环境,硫化物浓度较底;而沉积物相中硫化物浓度较高,为厌氧生境.微生物群落分布与环境特征具有很好的吻合性,沉积物相中微生物群落相似性较高,多样性相对较低,而水相中微生物多样性较高,且与沉积物中微生物分离距离较大.在水-沉积物垂向剖面中,细菌域中的变形菌门(Protebacteria)(丰度为7.6%~32.8%)、绿弯菌门(Chloroflexi)(13.6%~22.3%)以及古菌域中的广古菌门(Euryarchaeota)(19.3%~29.2%)是微生物群落中的绝对优势类群.在该生境中,存在微生物主导的硫循环过程,在厌氧沉积物表层,δ变形菌纲(Deltaprotebacteria)中的硫酸盐还原细菌还原硫酸盐产生硫化物,同时降解有机质.硫化物向上层扩散时,被Thiobacillus、Acidithiobacillus和Halothiobacillus等属的硫氧化微生物氧化为单质硫,并进一步氧化为硫酸盐,在硫循环过程中有机质被逐渐降解.特定微生物种群的富集需要在不同的环境因素,多种微生物共同参与硫循环过程,完成有机质降解.     

改性磁性纳米颗粒固定内生菌Bacillus nealsonii吸附废水中Cd2+的特性研究

从重金属超累积植物龙葵体内提取内生菌Bacillus nealsonii,采用二氧化硅改性纳米Fe_3O_4颗粒与海藻酸钠将其包埋交联进行固定化,制得一种新型球状生物吸附剂,并应用于废水中Cd~(2+)的吸附处理.同时,通过正交实验研究了该球状生物吸附剂的最佳制备条件和吸附处理条件,并采用扫描电镜等表征手段与构建吸附动力学考察了其吸附特征.结果表明,球状生物吸附剂的最佳制备条件为:改性纳米Fe3O4颗粒质量分数为0.1%,海藻酸钠质量分数为8.0%,菌液接种量为0.4%,交联时间为2 h;其最佳吸附处理条件为p H=6、吸附时间12 h、吸附剂用量(干重)2.5 g·L-1,在Cd~(2+)初始浓度为50 mg·L-1时的吸附率可达96%以上.研究发现,球状生物吸附剂的内外部结构孔隙率较大,有利于促进Cd~(2+)的吸附.该吸附过程遵循准二级反应动力学,以化学吸附为主,符合Freundlich等温吸附模型,最大单分子吸附量可达13.02 mg·g-1.解吸实验结果表明,该吸附剂具有较好的可重复利用性.     

Biogeochemistry of two types of permeable reactive barriers, organic carbon and iron-bearing organic carbon for mine drainage treatment: Column experiments

Permeable reactive barriers (PRBs) are an alternative technology to treat mine drainage containing sulfate and heavy metals. Two column experiments were conducted to assess the suitability of an organic carbon (OC) based reactive mixture and an Fe⁰-bearing organic carbon (FeOC) based reactive mixture, under controlled groundwater flow conditions. The organic carbon mixture contains about 30% (volume) organic carbon (composted leaf mulch) and 70% (volume) sand and gravel. The Fe⁰-bearing organic carbon mixture contains 10% (volume) zero-valent iron, 20% (volume) organic carbon, 10% (volume) limestone, and 60% (volume) sand and gravel. Simulated groundwater containing 380 ppm sulfate, 5 ppm As, and 0.5 ppm Sb was passed through the columns at flow rates of 64 (the OC column) and 62 (the FeOC column) ml d^− 1, which are equivalent to 0.79 (the OC column) and 0.78 (the FeOC column) pore volumes (PVs) per week or 0.046 m d^− 1 for both columns. The OC column showed an initial sulfate reduction rate of 0.4 µmol g (OC)^− 1 d^− 1 and exhausted its capacity to promote sulfate reduction after 30 PVs, or 9 months of flow. The FeOC column sustained a relatively constant sulfate reduction rate of 0.9 µmol g (OC)^− 1 d^− 1 for at least 65 PVs (17 months). In the FeOC column, the δ³⁴S values increase with the decreasing sulfate concentration. The δ³⁴S fractionation follows a Rayleigh fractionation model with an enrichment factor of 21.6‰. The performance decline of the OC column was caused by the depletion of substrate or electron donor. The cathodic production of H₂ by anaerobic corrosion of Fe probably sustained a higher level of SRB activity in the FeOC column. These results suggest that zero-valent iron can be used to provide an electron donor in sulfate reducing PRBs. A sharp increase in the δ¹³C value of the dissolved inorganic carbon and a decrease in the concentration of HCO₃⁻ indicate that hydrogenotrophic methanogenesis is occurring in the first 15 cm of the FeOC column.     

Global mismatches in aboveground and belowground biodiversity

Human activities are accelerating global biodiversity change and have resulted in severely threatened ecosystem services. A large proportion of terrestrial biodiversity is harbored by soil, but soil biodiversity has been omitted from many global biodiversity assessments and conservation actions, and understanding of global patterns of soil biodiversity remains limited. In particular, the extent to which hotspots and coldspots of aboveground and soil biodiversity overlap is not clear. We examined global patterns of these overlaps by mapping indices of aboveground (mammals, birds, amphibians, vascular plants) and soil (bacteria, fungi, macrofauna) biodiversity that we created using previously published data on species richness. Areas of mismatch between aboveground and soil biodiversity covered 27% of Earth's terrestrial surface. The temperate broadleaf and mixed forests biome had the highest proportion of grid cells with high aboveground biodiversity but low soil biodiversity, whereas the boreal and tundra biomes had intermediate soil biodiversity but low aboveground biodiversity. While more data on soil biodiversity are needed, both to cover geographic gaps and to include additional taxa, our results suggest that protecting aboveground biodiversity may not sufficiently reduce threats to soil biodiversity. Given the functional importance of soil biodiversity and the role of soils in human well-being, soil biodiversity should be considered further in policy agendas and conservation actions by adapting management practices to sustain soil biodiversity and considering soil biodiversity when designing protected areas.     

Natural resistance of rose petals to microbial attack

Petals of red, yellow and white roses (Rosa damascene Mill.) of the family Rosaceae were extracted with (1:1) methylene chloride/methanol and tested for their antimicrobial activities against four species of Gram-positive bacteria (Bacillus cereus, Bacillus subtilis, Micrococcus luteus and Staphylococcus aureus), five species of Gram-negative bacteria (Enterobacter aerogenes, Escherichia coli, Klebsiella pneumonia, Pseudomonas aeruginosa and Serratia marcescens) and five species of fungi (Penicillium notatum, Aspergillus niger, Rhizopus stolonifer, Saccharomyces cerevisiae and Fusarium oxysporum). All of the crude extracts showed a wide range of antimicrobial activities according to the tested organism and rose's type. Micrococcus luteus was found to be the most susceptible bacteria to all crude extracts. Red and yellow petal extracts showed much higher antibacterial activity than the white petals extract. Bacillus subtilis was found to be the least susceptible to all extracts. The fungus, Penicillium notatum was found to be the most susceptible with white petal extract being the most effective. Saccharomyces cerevisiae and Fusarium oxysporum were the least susceptible to all extracts. White roses extract showed much higher antifungal activities against Penicillium notatum than red or yellow roses, therefore, it was subjected to several bioassay guided chromatographic fractionations and purification to isolate the active chemical(s) responsible for the antifungal activity. Chemical structure of the isolated antifungal compounds were identified by spectroscopy techniques and found to be a γ-sitosterol and (Z,Z)-9,12-octadecadienoic acid. Antibacterial activity of the various types of rose extracts were due to complex mixtures of organic compounds which are still under chemical investigation and will be published later.     

高温厌氧细菌混合培养对纤维素酒精生产的提高作用

以高温厌氧细菌热纤维梭菌(Clostridium thermocellum LQRI)和嗜热厌氧乙醇菌(Thermoanaerobacter ethanolicus X514和Thermoanaerobacter pseudoethanolicus39E)为对象,以纤维素为微生物利用的底物,分析了LQRI纯培养和LQRI+Thermoanaerobacter混合培养对纤维素降解、酒精生产及终产物分布的影响.结果表明,LQRI+Thermoanaerobacter混合培养的酒精生产能力和纤维素降解率明显高于LQRI纯培养.在混合培养体系中,LQRI+X514的酒精生产能力明显高于LQRI+39E.培养基中无外源酵母粉条件下,LQRI纯培养酒精最高浓度约为11.5mmol/L,LQRI+X514和LQRI+39E混合培养最高酒精浓度分别约为71mmol/L和36.5mmol/L,相同的底物纤维素浓度条件LQRI+X514和LQRI+39E混合培养酒精浓度分别约为LQRI纯培养的5～11倍和3～5倍,纤维素降解率分别都约为LQRI纯培养的1.5～5.0倍;培养基中0.6%外源酵母粉存在条件下,LQRI纯培养酒精最高浓度约为12.9mmol/L,LQRI+X514和LQRI+39E混合培养最高酒精浓度分别约为263.5mmol/L和143.5mmol/L,相同的底物纤维素浓度条件LQRI+X514和LQRI+39E混合培养酒精浓度分别约为LQRI纯培养的8～22倍和8～12倍,纤维素降解率均约为LQRI纯培养的1.1倍.在5%Solka Floc为底物和0.6%外源酵母粉的条件下,LQRI+X514混合培养酒精浓度最高可达到263.5mmol/L,相当于1.2%(质量浓度)的酒精,LQRI+39E约为143mmol/L.     

反硝化除磷脱氮系统中DPB的驯化富集培养

反硝化同时脱氮除磷系统中反硝化除磷菌(DPB)的培养驯化状况,将直接影响污水中氮磷等营养元素的同时去除效率以及系统的高效稳定运行,为此本实验研究设计了一套以实际生活污水为处理对象的双污泥反硝化脱氮除磷工艺流程,采用逐渐过渡的培养方式,为DPB创造良好的厌氧/缺氧交替环境,即创造特定的适合DPB生存的环境条件让其进行自然选择,以筛选出来需要的DPB菌.结果表明,通过15d的间歇曝气的厌氧/好氧(A/O)运行方式可以对PAOs进行快速诱导;第二阶段,通过好氧曝气时间的逐渐减少,缺氧段投加硝酸氮的厌氧/好氧/缺氧(A/O/A)运行模式,25d左右可达到强化诱导反应器里面的DPB占PAOs的比例;最后让DPB在严格的厌氧/缺氧交替环境下进行富集培养19d,通过这种逐渐过渡培养的方式获得了对所需要的DPB菌的成功诱导富集,该菌的成功驯化培养为市政生活污水中的氮磷同时高效稳定去除提供了一种新方法.     

细菌对重金属的抗性及解毒机理研究进展

重金属污染物随工业废水排放到环境中,并通过生物链的富集作用,对环境和人类健康造成极大危害.自然界中很多微生物对重金属具有吸附性、耐受性和减小毒性损伤的特点.其中,细菌因其结构简单且易于培养,被广泛应用于研究对重金属的抗性及解毒.选取银(Ag)、铜(Cu)、铅(Pb)和铬(Cr)4种重金属,结合国内外的研究成果,系统地探讨了细菌对重金属的抗性及解毒机理.