温度对ABR反应器处理效果和微生物群落结构的影响

采用厌氧折流板反应器(Anaerobic baffled reactor, ABR)工艺处理模拟养猪场废水,考察低温(15±1)℃、中温(35±1)℃、高温(50±1)℃等3个温度条件对ABR处理效果和微生物群落结构的影响.同时,在水力停留时间HRT为24 h,进水COD为2000 mg·L^-1的条件下,考察了不同温度条件对ABR系统出水COD、pH、挥发性脂肪酸(Volatile fatty acid, VFA)的影响.最后,采用扫描电镜和荧光原位杂交技术(Fluorescence in situ hybridization, FISH)分别考察了不同温度条件对污泥微生物形态、种群结构和相对丰度的影响.结果显示,中温条件下系统的COD去除率最高,保持在96%以上,而低温和高温条件下系统的COD去除率均在70%左右;温度变化对反应器内pH值的影响不大;VFA含量在中温条件下最低,表示反应器运行最稳定;FISH结果显示,中温条件下系统真细菌和古细菌的总相对丰度最高,比低温和高温条件下分别高出12%和27%.     

Effect of vegetation of transgenic Bt rice lines and their straw amendment on soil enzymes, respiration, functional diversity and community structure of soil microorganisms under field conditions

With the development of transgenic crops, there is an increasing concern about the possible adverse effects of their vegetation and residues on soil environmental quality. This study was carried out to evaluate the possible effects of the vegetation of transgenic Bt rice lines Huachi B6 (HC) and TT51 (TT) followed by the return of their straw to the soil on soil enzymes (catalase, urease, neutral phosphatase and invertase), anaerobic respiration activity, microbial utilization of carbon substrates and community structure, under field conditions. The results indicated that the vegetation of the two transgenic rice lines (HC and TT) and return of their straw had few adverse effects on soil enzymes and anaerobic respiration activity compared to their parent and distant parent, although some transient differences were observed. The vegetation and subsequent straw amendment of Bt rice HC and TT did not appear to have a harmful effect on the richness, evenness and community structure of soil microorganisms. No different pattern of impact due to plant species was found between HC and TT. It could be concluded that the vegetation of transgenic Bt rice lines and the return of their straw as organic fertilizer may not alter soil microbe-mediated functions.     

生物滤床中一氧化氮的好氧去除过程研究

以美国Ultramet公司生产的Carbon-Foam为滤料,应用生物滤床处理NO模拟废气,研究了生物滤床在好氧条件下对NO的处理效果,并对NO去除过程的作用机理进行了探讨.研究结果表明,NO的去除效率随空床停留时间(EBRT)的增加而增加,在EBRT为6min、进口NO浓度为107.14mg.m-3时,NO去除效率为63%;随着进口浓度的提高,NO去除效率降低,而NO消除负荷增加.生物滤床中NO的去除过程由微生物硝化和化学氧化共同作用完成,其中以微生物硝化作用为主.化学氧化作用包括气相过程和液相过程2部分,当EBRT<4.6min时,液相中的化学氧化作用大于气相;当EBRT>4.6min时,气相中的化学氧化作用大于液相.当EBRT≤2min时,传质是NO去除过程的控制步骤,此时,微生物硝化作用和液相中的化学氧化作用均受传质过程控制.     

应用灰色模型(G,M)预测软土路基沉降量

本文讨论了灰色系统理论在软土路基沉降量预测中的应用 ,以京珠高速公路灵山实验段沉降观测数据为例 ,建立了沉降量灰色预测模型 ,并与三点法、双曲线法的预测结果以及实测结果进行了对比 ,结果表明 ,灰色预测模型的预测沉降量与实际沉降量更接近。最后分析了用灰色模型进行预测应注意的问题。     

混凝沉淀工艺处理餐厨废水的研究

通过单因素试验考察了聚合氯化铝(PAC)、聚合硫酸铁(PFS)、聚合氯化铝铁(PAFC)对餐厨废水生化处理出水中COD、TP的去除效果,并确定了絮凝沉淀最佳工艺条件:最优絮凝剂为PFS,最佳投加量为450 mg/L,絮凝反应时间为30 min,PAM投加量为0.6 mg/L,PAM投加时间为距离PFS投加后至少l min.在最佳工艺条件下,COD、TP平均去除率可分别达36％、83％,此时絮体体积比为13％.     

高浓度有机废水二相厌氧消化过程特性研究

以填充床生物膜酸化反应器与上流式污泥床反应器（UASB）甲烷化反应器组成的二相厌氧消化装置处理高浓度啤酒废水或合成废水,最大处理能力为32～35kgCOD/d·m³。提出了二相工艺高负荷运行时最低必需酸化率的概念。进水浓度5000mgCOD/L,容积负荷30kgCOD/d·m³时,最低酸化率为28％。对主要操作参数的灵敏度分析表明,操作负荷、酸化率和进水碱度是影响COD去除率的主要操作参数。对二相厌氧消化系统中影响反应器内微生物群系的生态平衡、微生物本征活性和反应器宏观行为的主要因素进行了分类和综合讨论。     

西北干旱区水资源开发的水文效应及其利用模式的变化

我国西北干旱区主要分布在新疆、青海和甘肃及内蒙西部。这里气候干旱,水资源对干旱区的经济发展有着决定性意义,在干旱区“没有灌溉就没有农业”。水资源不仅影响到农牧业发展,同时也影响到工矿资源开发和城市的发展。水资源既是宝贵的自然资源,也是干旱区自然环境综合体中最活跃的因素之一。水资源开发利用已引起一系列水文效应和生态环境的变化,尤其是干旱区水资源开发中水循环各要素变化是很强烈的,因此研究干旱区的水资源开发的水文效应不仅具有理论意义,也有重要的实践意义。     

基于DO曲线特征的污水毒性检测技术研究

基于对生化反应体系溶解氧(Dissolved Oxygen,DO)曲线特征的分析,研究了一种污水毒性检测技术,实验结果表明:在确定的操作流程和参数条件下,对于同种污水的周期性反应,体系DO周期性变化特征值波动小于10%,呈现高规律性和稳定性;最终建立了一种基于体系DO曲线特征的污泥活性相对抑制率公式,通过量化分析污水毒性对污泥活性的抑制程度,提供一种污水毒性快速检测技术手段。     

Mechanism of Cu(Ⅱ) adsorption inhibition on biochar by its aging process

Biochar exposed in the environment may experience a series of surface changes, which is called biochar aging. In order to study the effects of biochar aging on Cu（Ⅱ） adsorption, we analyzed the surface properties before and after biochar aging with scanning electron microscopy（SEM） coupled to an energy-dispersive X-ray spectrometer（EDX） and diffuse reflectance infrared Fourier transform spectroscopy（DRIFTS）, and then explored the influence of the aging process on Cu（Ⅱ） adsorption by batch experiments. After the aging process, the oxygen concentration, phenolic hydroxyl groups, aromatic ethers and other oxygen-containing functional groups on the biochar surface increased, while carboxyl groups slightly decreased. Thus, over a range of pH, the cation exchange capacity（CEC） and adsorption capacity of Cu（Ⅱ） on the aged biochar were smaller than those of new biochar,indicating that when biochar is incubated at constant temperature and water holding capacity in the dark, the aging process may inhibit Cu（Ⅱ） adsorption. Meanwhile, the dissociation characteristics of oxygen-containing functional groups changed through the aging process, which may be the mechanism by which the biochar aging process inhibits the Cu（Ⅱ） adsorption. Carboxyl groups became more easily dissociated at low pH（3.3–5.0）,and the variation of maximum adsorption capability（qm） of Cu（Ⅱ） on the old biochar was enlarged. Phenolic hydroxyl groups increased after the aging, making them and carboxyl groups more difficult to dissociate at high pH（5.0–6.8）, and the variation of qmof Cu（Ⅱ） on the aged biochar was reduced.     

A review of rapid transport of pesticides from sloping farmland to surface waters:Processes and mitigation strategies

Pesticides applied to sloping farmland may lead to surface water contamination through rapid transport processes as influenced by the complex topography and high spatial variability of soil properties and land use in hilly or mountainous regions. However, the fate of pesticides applied to sloping farmland has not been sufficiently elucidated. This article reviews the current understanding of pesticide transport from sloping farmland to surface water. It examines overland flow and subsurface lateral flow in areas where surface soil is underlain by impervious subsoil or rocks and tile drains. It stresses the importance of quantifying and modeling the contributions of various pathways to rapid pesticide loss at catchment and regional scales. Such models could be used in scenario studies for evaluating the effectiveness of possible mitigation strategies such as constructing vegetated strips, depressions, wetlands and drainage ditches, and implementing good agricultural practices. Field monitoring studies should also be conducted to calibrate and validate the transport models as well as biophysical-economic models, to optimize mitigation measures in areas dominated by sloping farmland.