聚糖原菌富集实验及其内源过程探究

细胞衰减是微生物内源过程的一个重要组成部分,可分为由细胞死亡引起的数量衰减和由细胞活性降低引起的活性衰减两部分.通过挥发性脂肪酸（VFA）吸收速率(VFAUR)测定、荧光原位杂交技术（FISH）以及LIVE/DEAD细胞染色技术,研究了富集聚糖原菌（GAOs）在序批式反应器（SBR）系统中好氧环境下的衰减特征.结果表明,当T=30℃、进料中m(COD)∶m(P)=100时,SBR系统中GAOs富集比例达94%.测定和计算表明,SBR富集系统中GAOs衰减速率和死亡速率分别为0.132 d^-1和0.034 d^-1,其数量衰减和活性衰减占其细胞总衰减比例分别为26%和74%.可见,GAOs数量衰减只占其细胞总衰减中很小一部分,而绝大部分衰减由活性衰减所引起.     

工业园能源代谢分析

运用工业代谢分析方法对某农药化学工业园能源代谢系统进行量化分析. 结果表明:提升能源转化水平、改善能源利用效率是优化该工业园能源系统的2个有效途径,可减少能源代谢过程中的资源消耗与环境压力. 进一步根据能源代谢模型量化分析得出,提升工业园热电厂运行水平,达到供热煤耗0.043 t/GJ,供电煤耗4.538 t/(104 kW·h)(2004年江苏省平均水平),将较2005年水平减少原煤消耗35.31%;将能源利用水平较低企业的电力利用效率和蒸汽利用效率分别提高到园区平均水平(58.01%和63.84%),可较2005年水平减少原煤消耗2.5%左右.      

微絮凝对腐殖酸超滤过程膜污染的减缓特性

以硫酸铝[Al_2(SO_4)_3·18H_2O]为絮凝剂,腐殖酸(humic acid,HA)和高岭土(Kaolin)水溶液为原水,研究微絮凝过程产生的不同絮体形态,对自制聚偏氟乙烯(PVDF)超滤膜过滤过程的影响.主要考察了微絮凝过程中絮体的特性(粒径大小及分布,分形维数)以及不同条件下形成的絮体形态对膜通量的影响,利用扫描电镜(SEM)和原子力显微镜(AFM)对污染膜的表面形貌进行表征,并测定了PVDF膜与有机污染物之间黏附力大小,来解析不同絮体形态对超滤膜的膜污染影响机制.结果表明,Al~(3+)以电性中和作用水解去除有机物,随着絮凝剂投加量的增加,絮体粒径不断增大,絮体的分形维数减小.膜通量衰减速率与絮体的粒径呈负相关,絮体粒径越大,膜通量衰减速率越小,超滤过程中形成的滤饼层越疏松,同时,较小分形维数的絮体引起的膜污染较轻,其膜通量恢复率也较高.PVDF-有机污染物之间的相互作用力大小与运行初期相应污染膜通量衰减速率呈正相关.当Al~(3+)投加量为5 mg·L~(-1),初始pH=7时,HA去除率为96.7%,膜通量衰减最小,通量恢复率达到88%.     

Applying a new method for direct collection,volume quantification and determination of N2 emission from water

The emission of N2 is important to remove excess N from lakes, ponds, and wetlands. To investigate the gas emission from water, Gao et al.(2013) developed a new method using a bubble trap device to collect gas samples from waters. However, the determination accuracy of sampling volume and gas component concentration was still debatable. In this study, the method was optimized for in situ sampling, accurate volume measurement and direct injection to a gas chromatograph for the analysis of N2 and other gases. By the optimized new method, the recovery rate for N2 was 100.28% on average; the mean coefficient of determination(R2) was 0.9997; the limit of detection was 0.02%. We further assessed the effects of the new method, bottle full of water, vs. vacuum bag and vacuum vial methods, on variations of N2 concentration as influenced by sample storage times of 1,2, 3, 5, and 7 days at constant temperature of 15°C, using indices of averaged relative peak area(%) in comparison with the averaged relative peak area of each method at 0 day.The indices of the bottle full of water method were the lowest(99.5%–108.5%) compared to the indices of vacuum bag and vacuum vial methods(119%–217%). Meanwhile, the gas chromatograph determination of other gas components(O2, CH4, and N2O) was also accurate. The new method was an alternative way to investigate N2 released from various kinds of aquatic ecosystems.     

近45年中国12个一级站大气气溶胶光学厚度变化特征

利用常规观测的总辐射和散射辐射日曝辐量资料,结合NASA GISS的月平均平流层气溶胶光学厚度(AOD)产品,反演计算了北京等12个台站1961～2005年0.75μm对流层AOD和气溶胶标高数据.基于这些数据,分析了各站AOD、气溶胶标高和地面能见度的年、季、月变化特征.结果表明:①就12个站45a总平均而言,光学厚度为0.276,年增长为0.0034;气溶胶标高为1.65km,年增加为0.015km;能见度为17.1km,年变化值为-0.08km;AOD春夏较大,秋冬较小;气溶胶标高夏季最高,春季次之,冬季最低.②各站点45a平均AOD范围为0.116～0.387;除格尔木外,各站AOD均有增长.年变化值为0.0010～0.0079.③20世纪70、80年代AOD增加明显;20世纪90年代以来,多数站点AOD有所下降,能见度有转好趋势.     

大气污染总量控制规划专家系统中知识库子系统的研究

论述了大气污染总量控制规划专家系统（ＥＡＳＰＴＥＣＥＰ）中知识库的基本设计思想,知识库分为无级知识库和领域级知识库,元级知识库由类文件和元规则文件构成,领域级知识库则文件和参量文件构成,并在此基础上阐述了ＥＳＡＰＴＥＣＰ中知识库演绎推理系统,知识库解释系统,知识库管理系统等的设计与实现方法。     

石油污染地下水中细菌多样性研究

采集了某废弃炼油厂的石油污染地下水样品,提取水中微生物总DNA,构建细菌16S rDNA克隆文库,并通过16S rDNA序列的系统发育分析,对样品中的细菌种群多样性以及群落结构进行了研究.结果表明,文库中阳性克隆的16S rDNA序列分属10个细菌类群,分别为γ-Proteobacteria(49.1%)、α-Proteobacteria(12.9%)、β-Proteobacteria(11.1%)、Bacteroidetes(9.2%)、Verrucomicrobia(6.7%)、Acidobacteria(2.5%)、δ-Proteobacteria(1.2%)、Actinobacteria(1.2%)、Planctomycetes(0.6%)、Unidentifiedbacteria(5.5%).在这一生态系统中,γ-Proteobacteria类细菌占据主导地位,接近50%,尤其是假单胞菌属(Pseudomonas)微生物在文库中的比例达35.6%.该石油污染地下水样品中细菌与许多其它已知的降解菌亲缘关系较近,如鞘胺醇单胞菌(Sphingomonas)、红球菌(Rhodococcus)和短波单胞菌(B...     

Partitioning of water soluble organic carbon in three sediment size fractions： Effect of the humic substances

Water soluble organic carbon (WSOC) in sediments plays an important role in transference and transformation of aquatic pollutants. This article investigated the inherent mechanisms of how sediemnt grain size affect the partitioning coeffcient (k) of WSOC. Influences of NaOH extracted humic substances were particularly focused on. Sediments were sampled from two cross-sections of the middle Yellow River and sieved into three size fractions (< 63 μm, 63-100 μm, and 100--300 μm). The total concentration of WSOC in sediments (CWSOC) and k were estimated using multiple water-sediment ratio experiments. Results show that CWSOC ranges from 0.012 to 0.022 mg/g, while k ranges from 0.8 to 3.9 L/kg. Correlations between the spectrum characteristics of NaOH extracted humic substances and k were analyzed. Strong positive correlations are determined between k and the aromaticity indicators of NaOH extracted humic substances in different sediment size fractions. Comparing with finer fractions (< 63 μm), k is higher in larger size fractions (63--100 and 100--300 μm) related to higher aromaticity degree of NaOH extracted humic substances mostly. While negative relationship between k and the area ratio of fourier transform infrared spectroscopy (FT-IR) at 3400 and 1430 cm-1 implied that the lowest k was related to the highest concentration of the acidic humic groups in particles < 63 μm. WSOC in finer fractions (< 63 μm) is likely to enter into pore water, which may further accelerate the transportation of aquatic contaminants from sediment to water.     

土霉素对小麦种子发芽与幼苗生长发育的生态毒性

研究了土霉素对小麦种子发芽以及早期幼苗生长发育的生态毒性效应.结果表明,土霉素对小麦种子芽长及根长的抑制效应显著(p<0.01),而且它们之间具有良好的剂量-效应关系.根据线性回归方程得出土霉素对小麦种子芽长和根长的半抑制浓度为65.5 mg/L和34.7 mg/L.然而,土霉素对小麦种子的发芽率并没有显著的影响.研究还表明,0.15~2.4 mg/L土霉素暴露21 d后,小麦叶片中的叶绿素含量降低了35.6%~47.3%,叶片及根部的可溶性蛋白含量也均呈显著下降趋势.暴露7 d后,0.15~2.4 mg/L土霉素对小麦叶片和根部SOD与POD活性的抑制效应不显著,但随着暴露时间的延长,土霉素对小麦的SOD与POD酶活性抑制率显著下降;2.4 mg/L土霉素暴露21 d后,小麦根部的SOD活性下降72.3%,说明土霉素对小麦幼苗体内的抗氧化系统具有破坏作用.该实验结果显示,低浓度土霉素长期暴露对小麦幼苗的生长发育具有不良的生态毒性效应.     

A+OSA活性污泥工艺剩余污泥减量特性研究

采用自动热量计对Anoxic (A) + oxic-settling-anaerobic(OSA)系统解偶联池进出污泥进行热值分析,以考察污泥量变动与能值变动的相互关系;通过解偶联池参数调整,了解污泥减量趋势,结合能量和物质平衡与常规水质指标测试,推测减量途径和特性.结果表明,解偶联池水力停留时间为5.56、 7.14和9 h时,整个系统污泥减量分别为1.236、 0.771和0.599 g/d.进出解偶联池的污泥含能水平发生了变化,随停留时间增加出流污泥的单位热值有高于进流污泥单位热值的趋势：5.56 h时,进出水热值没有显著差异;7.14 h时,进出水热值差值在99～113 J/g之间;9 h时,差值在191～329 J/g之间.解偶联池发生了污泥的衰减,停留时间延长,衰减程度越高.A+OSA系统污泥减量是解偶联池污泥衰减与AO主体反应区污泥产生率变化共同作用的结果.