SBR中好氧颗粒污泥的培养

采用竖式SBR作为反应器,利用城市污水处理厂剩余污泥作为接种污泥,通过不间断运行培养出好氧颗粒污泥。实验结果表明,采用非限量曝气模式好氧颗粒污泥降解模拟污水的效果较好,其COD去除率可达98％以上。曝气量对好氧颗粒污泥的形成和稳定具有重要影响,当气速为26．5m／h时,好氧颗粒污泥的性状和处理有机废水效果最佳。同时好氧颗粒污泥对pH值的变化不明显,当pH为5—8范围内,其COD去除率都可达到85％以上。但是未经驯化的好氧颗粒污泥对对硝基苯酚和对氯苯酚两种芳香类有机物较敏感,而对硝基苯酚对其毒性更大。当对硝基苯酚和。对氯苯酚浓度为10mg／L时,其COD去除率仅为42．5％和52％。     

复合式膜生物反应器处理城市生活污水特性的研究

HSMBR系统表现了对于COD高且稳定的去除效果。对于TN、TP,由于不排泥,污泥浓度的升高,并且填料内部的生物膜不断形成,以及在填料内部的污泥受曝气的扰动小,而变的较为密实,反应器内形成好氧、缺氧两种微环境并存,有利于系统对于TN、TP去除率的提高。     

高海拔寒冷地区污水处理厂地表水准Ⅳ类改造工程研究

为提高西部某污水厂出水水质达到地表水准Ⅳ类标准,对该水厂进行工程改造及优化运行。通过采用投加耐冷微生物、好氧池投加填料,改造微生物膜——活性污泥复合工艺,以及调试运行参数以及间歇曝气等措施观察COD、氨氮、TN和TP去除效果的变化,最后辅以高效混凝沉淀池保证出水达标。实验结果表明:好氧池末端DO降到1mg/L时,出水TN浓度减少到17.57mg/L,TP浓度减少到0.48mg/L,氨氮和COD仍去除稳定;TN去除效果随着分点进水量增加而提高,出水TN平均浓度降到14.13mg/L;污泥回流比由100%减少到60%,TN去除率提高,出水TN平均浓度降到13.14mg/L;通过将好氧区改为间歇曝气后,氨氧化菌和反硝化除磷菌成为优势菌种,加强了氮磷的去除,出水TN、TP浓度分别为11.80mg/L和0.35mg/L,TP仍需。经过优化运行后出水水质稳定达到要求,并有效的解决了氧化沟反应池内溶解氧盈余、污泥浓度控制等问题,同时起到很好的节能降耗效果。     

SBR法处理啤酒废水DO对丝状菌污泥膨胀的影响

溶解氧(DO)浓度是影响丝状菌污泥膨胀最重要的因素之一。选用具有代表性的啤酒废水为处理对象,研究了SBR工艺中DO浓度对丝状菌污泥膨胀的影响。结果表明:高DO浓度(4～6.5mg/L)不会导致丝状菌污泥膨胀;低DO浓度能引起丝状菌污泥膨胀,当DO浓度降低至0.4mg/L时,SVI升高到210mL/g,会导致污泥膨胀发生。低DO浓度下污泥膨胀发生后,在较高的DO浓度条件下运行一定的周期数后,污泥膨胀能得到有效控制,使污泥沉降性能恢复到正常水平。     

好氧颗粒污泥中胞外聚合物的提取、组成及空间分布研究进展

好氧颗粒污泥具有比传统活性污泥更加优越的性能,然而好氧颗粒污泥的稳定性限制了该技术的工业应用和推广。积累在颗粒表面的胞外聚合物（EPS）和好氧颗粒污泥系统长期运行的稳定性能有关。本文回顾了好氧颗粒污泥中EPS的成分、提取方法、在颗粒中的空间分布及EPS在颗粒化进程和稳定状态的作用,探讨了好氧颗粒污泥中EPS研究现状和不足,对亟待研究的内容提出了建议,以便为国内好氧颗粒污泥深入研究和工业应用提供参考。     

好氧颗粒污泥降解邻苯二甲酸二甲酯的影响因素研究

本文研究了好氧颗粒污泥系统中,温度、pH、曝气强度、邻苯二酸(Phthalic Acid,PA)及氨氮(NH3-N)对邻苯二甲酸二甲酯(Dimethyl Phthahte,DMP)降解效果的影响,结果表明:好氧颗粒污泥降解DMP的最佳温度、最佳PH值范围、最佳曝气强度分别为25℃～45℃、7.0 ～9.0、1.38 cm/s.当PA浓度为100 mg/L、300 mg/L,PA对DMP降解起促进作用;当PA浓度为500 mg/L、800 mg/L,PA对DMP降解起抑制作用.进水中50 mg/L的氨氮浓度对DMP降解的影响不大.本研究中采用的19种运行工况条件中,除曝气强度为0.33 cm/s以外,其他18种运行工况条件下,当运行时间达到300 min时,DMP的浓度都小于1.0 mg/L,因此,当水力停留时间达到5h以上时,温度、pH、PA、氨氮对DMP降解速率的影响基本上可以忽略不计.     

连续流好氧颗粒污泥流化床启动与颗粒污泥形成特征研究

对连续流好氧颗粒污泥流化床的中颗粒污泥的形成过程、颗粒污泥性质进行了研究,并对该反应器中颗粒污泥形成机制进行了分析。     

好氧颗粒污泥技术

好氧颗粒污泥技术是近几年来发展起来的废水处理技术,它能有效地去除废水中的有机物、COD、氨氮、难降解的有毒有机物、硫磷、重金属离子等。本文根据国内外对其的最新研究成果对好氧颗粒污泥的特性、形成的主要影响因素以及除污功能进行了阐述。     

MBBR工艺在生活污水处理装置完善项目中的应用

文章应用MBBR(流动床生物膜反应器)工艺对某石化公司生活污水处理装置进行改造,并研究影响该工艺高效脱氮的主要因素,即pH值、DO含量和污泥回流比。结果表明:实际运行中,pH值控制在7.5、DO在1～4mg/L、污泥回流比R≤3,能取得较好的脱氮效果,将氨氮降至3mg/L以下,同时,将污泥浓度维持在5～8g/L,还可在短时间内实现CODCr高去除率。实践证明,MBBR工艺在生活污水完善项目中的应用,能够有效降低污水中污染物含量,为后续深度处理系统的稳定运行提供可靠保障。     

多孔颗粒载体-膜生物反应器脱氮效果研究

实验探索了高MLSS(溶液悬浮固体浓度)下多孔颗粒载体—膜生物反应器发生短程硝化、反硝化的可能性。研究了溶解氧(DO)、C/N、氨浓度及氨负荷、pH等因素对短程硝化、反硝化和TN去除的影响。实验发现,当控制pH=7.5、DO=1.0mg/L、C/N为6时,该反应器能同时达到较高的NH4 —N和TN出除率。     

The formation of aerobic granular sludge for the treatment of real landfill leachate using a granular sequencing batch reactor at a constant volume

Leachate generated in a landfill may not be treated by conventional biological treatment due to its nature and complexity. The process of forming aerobic granules in batch sequencing reactors having features such as; reducing the settling process time and saving energy consumption and high decomposition rate have been noticed by researchers. In the present study, the structure of sequencing batch reactors (SBRs) was evaluated for the formation of granules, which were subsequently utilized for the treatment of landfill leachate. The experiment was initiated by using the GSBR, containing 1200 ml with different apparatuses, to develop granular sludge, and synthetic wastewater was added to reinforcement. The selected parameters for the operational hydraulic retention time (HRT) of the wastewater (6-h cycles) included feeding, idle, aeration, settling, and discharge. Furthermore, the controlled conditions were the dissolved oxygen (DO) range of 2–2.2 mg/L, temperature range of 20–23℃, and pH of 7.5–8.3. The chemical oxygen demand (COD), mixed liquor suspended solids (MLSS), and sludge volume index (SVI) daily were measured at the influent and effluent of GSBR reactor. The main properties of aerobic granular sludge were identified during the research procedures, and the remarkable settling and potent, high-density microbial structure of the granules were confirmed. The mean size of the formulated granules was estimated at 7.46 ± 1.8 mm, and the volume of the biomass also increased from approximately 1607 to 4137 mg/L through the granulation process. Moreover, 98% of the influent chemical oxygen demand (COD) could be removed by the formulated granular sludge, and the final-stage organic loading rate was estimated at 5.65 COD/m³/day. According to the results, GSBRs could be employed for the formulation of aerobic granular sludge for the treatment of landfill leachate.     

Determination of dissolved oxygen limitation in aerobic biofilm reactors

The concentration of dissolved oxygen (DO) strongly influences the performance of aerobic biofilm reactors because organic oxidation is limited by the availability of oxygen. However, it is not necessary to maintain a high DO level in the reactors in order to overcome this limitation. Excessive aeration wastes energy. Therefore, the determination of the onset of DO limitation against organic substrate removal in aerobic biofilm reactors is important for their effective operation. This study is aimed at developing an expression to determine the onset of DO limitation and hence to control the aeration system. The expression developed is as follows: , where S_b and C_b are the bulk concentrations of organic substrate and DO, respectively; D_ws and D_wc are the diffusion coefficients of organic substrate and oxygen in the reactors respectively; and R_b is an overall ratio of oxygen consumption to organic substrate removal in the reactors. The latter is the key parameter in the equation, and is determined by the characteristics of the substrate, biofilm, and reactor. In order to measure the value of R_b, the authors have developed a micro-biofilm reactor. The value of R_b was determined to be 0.13 (mg O₂ mg⁻¹ COD_cr) for glucose removal with this reactor. The equation has, subsequently, been verified with data from batch and continuous experiments.     

Allocation of supplementary aeration stations in the Chicago waterway system for dissolved oxygen improvement

The Chicago Waterway System (CWS), used mainly for commercial and recreational navigation and for urban drainage, is a 122.8 km branching network of navigable waterways controlled by hydraulic structures. The CWS receives pollutant loads from 3 of the largest wastewater treatment plants in the world, nearly 240 gravity Combined Sewer Overflows (CSO), 3 CSO pumping stations, direct diversions from Lake Michigan, and eleven tributary streams or drainage areas. Even though treatment plant effluent concentrations meet the applicable standards and most reaches of the CWS meet the applicable water quality standards, Dissolved Oxygen (DO) standards are not met in the CWS during some periods. A Use Attainability Analysis was initiated to evaluate what water quality standards can be achieved in the CWS. The UAA team identified several DO improvement alternatives including new supplementary aeration stations. Because of the dynamic nature of the CWS, the DUFLOW model that is capable of simulating hydraulics and water quality processes under unsteady-flow conditions was used to evaluate the effectiveness of new supplementary aeration stations. This paper details the use of the DUFLOW model to size and locate supplementary aeration stations. In order to determine the size and location of supplemental aeration stations, 90% compliance with a 5 mg/l DO standard was used as a planning target. The simulations showed that a total of four new supplementary aeration stations with oxygen supply capacities ranging from 30 to 80 g/s would be sufficient to meet the proposed target DO concentration for the North Branch and South Branch of the Chicago River. There are several aeration technologies, two of which are already being used in the CWS, available and the UAA team determined that the total capital costs of the alternatives range from $35.5 to $89.9 million with annual operations and maintenance costs ranging from $554,000 to $2.14 million. Supplemental aeration stations have been shown to be a potentially effective means to improve DO concentrations in the CWS and will be included in developing an integrated strategy for improving water quality in the CWS.     

不停产检修曝气系统在污水处理中的应用

本文介绍了在污水处理中好氧阶段的可不停产检修的曝气系统，重点阐述了实现不停产检修的曝气系统的曝气器选用及下垂式曝气系统、上浮式曝气平台、漂浮式曝气悬链三种布气装置。该技术能够实现污水处理厂的不停产检修，保证污水处理设施的连续运行，具有很高的推广价值。     

间歇曝气短程硝化控制新途径的初步试验研究

采用SBR,以间歇曝气的方式控制短程硝化,分别研究了在限制曝气量和不限制曝气量条件下,亚硝酸盐的积累情况.试验表明,间歇曝气可以作为短程硝化的控制条件,在一定条件下,亚硝化率可达到90%以上.限制曝气量时,在低DO情况下,采用间歇曝气控制短程硝化更为有效、经济.     

高浓度氨氮废水好氧反硝化反应的基本条件

文章通过室内实验,对高浓度氨氮废水(垃圾渗滤液)间歇曝气,在只存在有机碳、无机氮的条件下进行好氧反硝化脱氮研究。实验结果表明:垃圾渗滤液中存在好氧反硝化土著微生物菌落;发生好氧反硝化的基本条件为在溶解氧充足的条件下间歇曝气;碳源不仅是厌氧反硝化所必须的,同样也是好氧反硝化的必要条件。     

Enhanced nutrient removal by oxidation-reduction potential (ORP) control in laboratory-scale extended aeration reactors

A study was conducted to examine N and P removal by a laboratory-scale extended aeration treatment system employing oxidation-reduction potential (ORP) controlled aeration. The system was provided with a 90-L aeration tank. When ORP controlled aeration was applied, the aeration tank was divided into three zones, namely the ORP zone (45 L), the anaerobic zone (27 L) and the aerobic zone (18 L). An external anoxic selector of 3.8 L in volume was also added. An ORP set point of 70 mV was used for the ORP zone. The extended aeration treatment system operating without the ORP controlled aeration was used as the control.COD removal (97%) was not affected, but both N and P removal were enhanced significantly in the ORP reactor. Total N removal efficiency was increased from 49.1% (control) to 83.5%. Almost all P was captured (99%), leaving an average of 0.09 mg L⁻¹ P in the effluent. The ORP reactor yielded a sludge P content of 3.1%, compared to only 1.8% for the control. This indicated luxury P uptake in ORP reactor. Very significant P release and denitrification were found in the anoxic selector. Fairly good simultaneous nitrification and denitrification had occurred in the ORP zone. However, P release was very limited in the anoxic zone. However, anoxic P uptake and nitrification were found in this zone.Low F/M bulking was observed in both the control and ORP operation before the installation of a selector. Bacterial Type 0041 was identified as the predominant bulking organism. For the Control, an aerobic selector cured the bulking problem in one sludge age while an anoxic selector fixed up the problem during the ORP operation.     

LOW-HEAD HYDROPOWER IMPACTS ON STREAM DISSOLVED OXYGEN1

ABSTRACT: A method to evaluate the effect of hydropower development on downstream dissolved oxygen (DO) is presented for a low head dam. Water, previously aerated during release over spillways and under gates, is diverted through the hydropower facility without further aeration. The oxygen transfer that occurs as a result of air entrainment at the various release points of a dam is measured. Oxygen transfer efficiencies are calculated and incorporated into an oxygen transfer model to predict average release DO concentrations. This model is used to systematically determine the effect of hydropower operation on downstream DO. Operational alternatives are investigated and a simple operational guide is developed to mitigate the effects of hydropower operation. Combinations of reduced generation and optimal releases from the dam allow the hydropower facility to operate within DO standards.