关于活性污泥工艺中剩余污泥量计算的讨论

根据酒仙桥污水处理厂2001年3～10月运行数据及方庄污水处理厂2001年1～6月运行数据,探讨了活性污泥工艺中剩余污泥量计算的有关问题.通过建立污泥产率系数与MLVSS/MLSS比值的关系,论述了污泥产率系数会在较大范围内变化的原因.     

污泥膨胀的原因分析及预警监测研究

通过分析活性污泥法污水处理系统的实际运行工况,筛选出丝状细菌数量级、污泥沉降比、负荷比、溶解氧、泥龄、温度和营养物类型作为污泥膨胀指标,并根据研究得出污泥膨胀监控指示范围.     

生物捕食污泥减量化系统的污泥特性

通过中试分析了以减量化为目的的微型动物捕食系统中活性污泥的特性.结果表明,细菌分散培养段的悬浮污泥浓度比原生动物捕食段约高15%,比大型微型动物捕食段约高40%;微型动物的捕食作用在减少剩余污泥产率的同时,可以提高悬浮污泥的沉降性能约36%,轮虫可作为该系统污泥沉降性能的指示生物;低底物浓度下,大型微型动物的捕食活动可以增强污泥的活性.     

活性炭为载体的好氧颗粒污泥培养及性能研究

好氧颗粒污泥是一种应用于废水生化处理中的新型活性污泥技术,具有结构致密,沉降性能优越,生物处理能力强等特点.通过在气升式内循环间歇反应器启动阶段,接种活性污泥的同时添加活性炭颗粒(AC)的方法,缩短好氧颗粒污泥颗粒化时间,成功培养出了沉降速率大,结构稳定,除氮效果好的活性炭好氧颗粒污泥.并考察了活性污泥絮体-出现颗粒污泥-成熟颗粒污泥-储存-解体-修复的过程,验证了载体强化型好氧颗粒污泥处理低碳氮比废水的可行性.实验结果证明:活性炭好氧颗粒污泥反应器稳定运行时,COD、氨氮、总氮去除率分别可以达到80％ ～ 90％、99％、80％.将成熟活性炭好氧颗粒污泥储存12个月,经过恢复培养,物理特性及脱氮性能能够完全恢复到储存前的水平.     

污泥膨胀的原因分析及预警监测研究

通过分析活性污泥法污水处理系统的实际运行工况,筛选出丝状细菌数量级、污泥沉降比、负荷比、溶解氧、泥龄、温度和营养物类型作为污泥膨胀指标,并根据研究得出污泥膨胀监控指示范围。     

活性污泥法中污泥龄应用问题探讨

对活性污泥法中的重要参数--污泥龄的应用进行了分析探讨.指出传统污泥龄的定义及其计算式适用条件,对其计算式中系统体积的选择进行了讨论,并分析了污泥龄控制过程中污泥浓度、污泥负荷和污泥龄的变化.文中还对间歇式进水反应器内污泥龄的确定进行了分析,最后介绍了三种可用于非稳态污泥龄计算的实时污泥龄的计算方法和应用.     

用污泥沉降比指导活性污泥法运行的探讨

总结讨论了污泥沉降比在活性污泥法污水处理过程中与MLSS的关系和对活性污泥法处理效果的影响,分析其与季节变化的关系,指出污泥沉降比在预防污泥膨胀及维持曝气池稳定运行方面的作用,影响污水处理效果因素之间的关系,以及污泥沉降比在实际生产运行管理中的指导作用。     

对上海城镇污水处理厂污泥处理和处置的几点想法(下)

4 污泥处理的手段必须结合处置方式进行选择 4.1 如何合理选择污泥稳定化的方法 来自污水处理厂初沉池和二沉池(剩余活性污泥或者生物滤池污泥)的混合污泥通常含有60%～80%的有机物,如碳水化合物、脂肪、蛋白质,而且还含有大量的多种微生物,这种污泥在堆放时极易自发地进行厌氧生物反应,产生异味并导致污泥脱水性质恶化.     

卷贝进行污泥减量的应用研究

利用卷贝在合建式活性污泥反应器中摄食污泥进行污泥减量试验。试验发现,污泥表观产率系数与卷贝密度呈负相关,卷贝对污泥的相对减量约为40%,绝对减量为37.5mgVSS/(L·d),减量速度为0.177mgVSS/(mgP.acuta·d),活性污泥系统中卷贝的存在对COD、氨氮和总磷的去除不会产生影响,对污泥沉降性能也影响不大。     

沉淀池生物污泥回流工艺生物强化作用的研究

利用生物预处理出水中携带的硝化细菌和异养细菌等微生物,在后续沉淀单元产生生物延伸效应,并通过采取沉淀池生物污泥回流强化措施,使沉淀池在去除浊度的同时,产生类似活性污泥法的作用,强化生物净化作用.在增加生物污泥回流前、后,沉淀池出水CODMn平均分别为4.16mg/L、2.72 mg/L,沉淀池出水相对生物预处理出水CODMn的平均去除率由4.65%提高至31.4%,去除效果显著提高.同时,增加生物污泥回流后,对浊度和氨氮的去除也得到进一步的改善.     

高藻期给水厂排泥水处理系统优化研究

针对高温高藻期给水厂排泥水的特点,研究了排泥水处理负荷、加药条件、搅拌条件、回流污泥控制及排泥控制等因素对排泥水处理系统运行的影响情况,提出了排泥水处理系统的优化建议.     

Partial ozonation of activated sludge to reduce excess sludge, improve denitrification and control scumming and bulking.

Disposal of sewage sludge is forbidden and agricultural use of stabilized sludge will be banned in 2005 in Switzerland. The sludge has to be dewatered, dried, incinerated and the ashes disposed in landfills. These processes are cost intensive and lead also to the loss of valuable phosphate resources incorporated in the sludge ash. The implementation of processes that could reduce excess sludge production and recycle phosphate is therefore recommended. Partial ozonation of the return sludge of an activated sludge system reduces significantly excess sludge production, improves settling properties of the sludge and reduces bulking and scumming. The solubilized COD will also improve denitrification if the treated sludge is recycled to the anoxic zone. But ozonation will partly inhibit and kill nitrifiers and might therefore lead to a decrease of the effective solid retention time of the nitrifier, which reduces the safety of the nitrification. This paper discusses the effect of ozonation on sludge reduction, the operation stability of nitrification, improvement of denitrification and gives also an energy and cost evaluation.     

On-line determination of sludge settling velocity for flux-based real-time control of secondary clarifiers.

The state diagram for operation of secondary clarifiers is used to design a control algorithm for the return sludge pumping and determination of the actual hydraulic capacity of the biological step of a wastewater treatment plant. On-line input for the control algorithm is derived from a sludge volume sensor and a suspended solids sensor in the form of software sensors giving values for the sludge settling characteristics - settling velocity, sludge volume index, initial settling velocity and the exponent in the Vesilind equation - allowing the control to accommodate the ever changing settling characteristics and thereby keep the suspended solids flux in the clarifiers in balance for both dry weather flows and during rain events. The control algorithm has been implemented, tested and set into normal operation on a full scale wastewater treatment plant.     

Advanced treatment by anaerobic process followed by aerobic membrane bioreactor for effluent reuse in paper mill industry.

The operation of an activated sludge process at a paper mill (AIPM) in Hedera, Israel, was often characterized by disturbances. As part of a research and development project, a study on new biological treatment was initiated. The study included the operation of three pilot units: a. anaerobic treatment by upflow anaerobic sludge blanket (UASB); b. aerobic treatment by two pilot units including activated sludge and membrane bioreactor (MBR), which have been operated in parallel for comparison reasons. The pilot plant working on anaerobic treatment performed COD reduction from 2,365 to 755 mg/L, expressed as average values. Based on the pilot study, a full scale anaerobic treatment system has been erected. During a period of 100 days, after achieving steady state, the MBR system provided steady operation performance, while the activated sludge produced effluent characterized by oscillatory qualities. The following results, based on average values, indicate much lower suspended solids concentrations in the MBR effluent, 2.5 mg/L, as compared to 25 mg/L in the activated sludge. The ability to develop and maintain a concentration of over 11,000 mg/L of mixed liquor volatile suspended solids in the MBR enabled an intensive bioprocess at relatively high cell residence time. This study demonstrates that the anaerobic process, followed by aerobic MBR can provide effluent of high quality which can be considered for economic reuse in the paper mill industry.     

Insitu bioaugmentation of nitrification in the regeneration zone: practical application and experiences at full-scale plants.

Nitrification is the rate-limiting process in the design of activated sludge process. It is especially unstable during the winter season (when the temperature of activated sludge mixed liquor drops below 13 degrees C). It is therefore difficult to meet the ammonia effluent standards in winter. The common way to compensate for low nitrification rates at low temperatures is to increase sludge retention time (SRT). However, the increase of SRT is accompanied by negative factors such as elevated sludge concentration, higher sludge loading of secondary clarifiers, formation of unsettleable microflocs, etc. The low performance of nitrification at low temperatures can also be compensated for by enhancing the nitrification population in activated sludge. This paper describes such a method called bioaugmentation of nitrification in situ. This procedure takes place in a so-called regeneration tank, which is situated in the return activated sludge stream. The results of the operation of two wastewater treatment plants with regeneration zones are described in this paper, together with some economic evaluation of the bioaugmentation method.     

CASS工艺生物脱氮除磷效果分析

对CASS工艺脱氮除磷效果进行了试验研究,重点研究了温度和回流比对脱氮效果的影响,曝气量对除磷效果的影响。研究结果表明,水温在30℃时系统脱氮效果最好,此时NH3-N去除率在80%左右,TN去除率在70%左右;污泥回流比为25%、50%、100%和200%时,TN去除率分别为50%、58%、62%和70%,增加回流比可以提高脱氮效率;好氧区DO维持在2mg/L和4 mg/L时,TP去除率分别为82%和37%。     

Full-scale experience with the deammonification process to treat high strength sludge water -- a case study

More stringent effluent criteria with regard to nitrogen calls for improved nutrient removal techniques in wastewater treatment plants (WWTPs). Besides optimisation of the liquid treatment train of the plants, attention has increasingly centred on the problem of return flows from sludge treatment. One of the most recent developments aimed at the reduction of this nitrogen load is deammonification which has been used at one of Ruhrverband's plants since 2002 by applying a moving bed system. To gain additional experience in operating this process, another full scale plant was modified in 2007 by integration of deammonification, using a SBR system with suspended biomass based on the DEMON(?) control scheme. By using seeding sludge from Strass WWTP in Austria, start-up has been achieved within only 1 day. After stable operation for several months, increasing nitrate concentrations were observed in the effluent of the system indicating growing activity of nitrite oxidising bacteria (NOB). Following severe process deterioration, it was decided to re-start the system again but the same behaviour, i.e. increasing levels of nitrate, was observed once again. Several approaches were used to suppress NOB organisms in full-scale without success, e.g. low oxygen levels and high free ammonia concentrations. Finally, the reduction of the aerobic cycle length during intermittent aeration down to 8 min, followed by an anoxic mixing period of only 18 min was successful in inhibiting the activity of NOB organisms, most probably due to their elevated lag-phase compared with ammonium oxidising bacteria. Today, nitrogen elimination that has been stabilised at more than 80% at a daily volumetric loading rate of 0.5 kg N/(m3 d). The total costs amount to €2.3/kg N(eli).     

Analysing sludge balance in activated sludge systems with a novel mass transport model

In activated sludge systems the mechanically treated wastewater is biologically cleaned by biomass (activated sludge). The basic requirement of an efficient biological wastewater treatment is to have as a high biomass concentration in the biological reactor (BR) as possible. The activated sludge balance in activated sludge systems is controlled by the settling, thickening, scraper mechanism in the secondary settling tank (SST) and sludge returning. These processes aim at keeping maximum sludge mass in the BR and minimum sludge mass in the SST even in peak flow events (storm water flow). It can be, however, only reached by a high SST performance. The main physical processes and boundary conditions such as inhomogeneous turbulent flow, geometrical features of the SST, wastewater treatment plant (WWTP) load, return sludge flow, sludge volume index etc. all influence settling thickening and sludge returning. In the paper a novel mass transport model of an activated sludge system is presented which involves a 2-dimensional SST model coupled with a mixed reactor model of the biological reactor. It makes possible to investigate different sludge returning strategies and their influence on the sludge balance of the investigated activated sludge system, furthermore, the processes determining the flow and concentration patterns in the SST. The paper gives an overview on the first promising model results of a prevailing peak flow event investigation at the WWTP of Graz.     

Sludge settleability detection using automated SV30 measurement and its application to a field WWTP

The need for automation & measurement technologies to detect the process state has been a driving force in the development of various measurements at wastewater treatment plants. While the number of applications of automation & measurement technologies to the field is increasing, there have only been a few cases where they have been applied to the area of sludge settling. This is because it is not easy to develop an automated operation support system for the detection of sludge settleability due to its site-specific characteristics. To automate the human operator's daily test and diagnosis works on sludge settling, an on-line SV30 measurement was developed and an automated detection algorithm on settleability was developed that imitated heuristics to detect settleability faults. The automated SV30 measurement is based on automatic pumping with a predefined schedule, the image capture of the settling test with a digital camera, and an analysis of the images to detect the settled sludge height. A sludge settleability detection method was developed and its applicability was investigated by field application.     

Potential of activated sludge ozonation.

The disposal of sewage sludge and the agricultural use of stabilised sludge are decreasing due to more stringent regulations in Europe. An increasing fraction of sewage sludge must therefore be dewatered, dried, incinerated and the ashes disposed of in landfills. These processes are cost-intensive and also lead to the loss of the valuable phosphate resources incorporated in the sludge ash. The implementation of processes that could reduce excess sludge production and recycle phosphate is therefore recommended. Partial ozonation of the return sludge of an activated sludge system significantly reduces excess sludge production, improves the settling properties of the sludge and reduces bulking and scumming. The solubilised COD will also improve denitrification if the treated sludge is recycled to the anoxic zone. However, ozonation partly kills nitrifiers and could therefore lead to a decrease of the effective solid retention time of the nitrifier, thus reducing the safety of the nitrification. This paper discusses the effect of ozonation on sludge reduction, the operating stability of nitrification, the improvement of denitrification and also presents an energy and cost evaluation.