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为实现城市污水短程硝化厌氧氨氧化生物脱氮,以去除有机物的实际污水为研究对象,考察了游离亚硝酸盐(FNA)处理污泥实现城市污水部分短程硝化的可行性。 结果表明,FNA处理活性污泥后,亚硝酸盐氧化菌(NOB)的亚硝酸盐氧化速率下降程度大于氨氧化菌(AOB)的氨氧化速率,且在0~0.75 mg HNO2-N·L-1范围内随着FNA浓度的增加抑制作用增强。接种实际污水厂活性污泥后,系统亚硝酸盐(NO2--N)积累率仅为1%,即为全程硝化。在控制污泥龄约为15 d的条件下,采用FNA处理污泥可使系统亚硝酸盐积累率增加至90%以上。水力停留时间调至2.5 h时,实现了部分短程硝化,且出水NO2--N/NH4+-N平均值为1.24,可满足厌氧氨氧化脱氮反应的要求。因此采用FNA处理污泥,结合水力停留时间和污泥龄控制可实现城市污水部分短程硝化。 相似文献
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某生活污水厂冬季运行总氮去除效果较差。通过在缺氧池前段投加复合碳源,提高了生化系统中反硝化脱氮效率,降低出水总氮,并且达到了总磷的去除效果,提高了污泥的活性,降低了污水厂的运行成本。 相似文献
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随着环保和可持续意识的加强,给水厂的排泥水必须经过处理后达标排放。浓缩池是排泥水处理工艺中的关键环节,作者在传统的重力浓缩池基础上进行改进,增加池体高度和有效水深,加快了污泥压缩速率,浓缩池污泥含固率可高达4%~8%。在中山市某给水厂实际应用中表明,该工艺方案能大大提高污泥浓缩效率,运行效果稳定。 相似文献
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采用厌氧序批式活性污泥法(ASBR)处理高浓度有机废水,通过接种不同体积的城市污水厂好氧污泥和下水道厌氧污泥成功实现反应器的启动.反应器对COD的平均去除率达到了94.79%,并且系统中脱氮效果较好,TN的平均去除率可达到64.52%,反应器在第39天即形成了颗粒污泥.在此基础上考察了不同污泥浓度对COD去除的影响,试验结果表明反应器中COD的去除率随着污泥浓度的增大而升高,颗粒污泥对COD有很高的去除率并且适应一定范围内的COD污泥负荷的变化. 相似文献
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《水处理技术》2021,47(10):99-103
为强化厌氧-缺氧-好氧(A~2O)工艺深度处理城市污水中的TP,满足GB 3838-2002的地表IV水体要求(TP的质量浓度0.3 mg/L),采用FeSO_4作为同步除磷研究,考察Fe盐同步化学除磷对A~2O工艺脱氮除磷性能和污泥沉降性能的影响,并解析该过程的微生物群落特性。结果表明,Fe~(2+)投加可保证出水TP的质量浓度0.3 mg/L,且对COD的去除效果和去除速率影响较小;且同步化学除磷可改善脱氮性能和污泥沉降性能。Fe盐投加对Bacteroidetes的影响较小,Saccharibacteria和Acidobacteria的丰度在Fe盐投加后显著下降,Actinobacteria菌群随着Fe盐投加组运行时间的增加。 相似文献
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进行了城市供水厂排泥施用于花园土壤的试验研究。单因素对照试验结果表明,土壤施用污泥后,其渗流出水中溶解磷量降低,土壤的固磷作用增强。当污泥施加量为60t/hm2时,和对照组相比,渗流液中溶解磷浓度、土壤容重分别降低了37.3%和22.9%,含水率和孔隙率较对照组分别增加了81.7%和11.0%。正交试验得出了渗流液含磷量、土壤容重等考察因素与河沙、污泥施加量关系的一次回归方程。在同一时段,土壤含水率、土壤孔隙率与河沙、给水污泥施加量呈正相关,土壤容重与土壤性质以及给水污泥加入量呈负影响,并不同程度存在交互效应。给水污泥适度施用于土壤,对其结构与理化性质的改善明显。 相似文献
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随着城市化进程的不断加快,城市污水处理的规模和质量不断提高,所产生的剩余污泥作为固体废弃物的处理与处置也越来越成为制约污水处理效果的关键问题。由于污泥混合体的架构复杂且含有微生物组成的细胞和胞外聚合物(EPS)等亲水性物质,污泥脱水困难。污泥预处理作为强化污泥脱水和后续稳定化处理的关键技术能够有效改变污泥组成形态、促进污泥中细胞水和结合水向自由水的转变,是提高污泥脱水效率的主要方法。当前,主要的污泥脱水预处理主要包括:物理法、化学法和上述两种方法的组合等方式。文中主要讨论了不同预处理方法对污泥脱水性能的影响。 相似文献
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采用低C/N比实际生活污水,以A2N2-SBR(厌氧/硝化/缺氧/硝化)双污泥系统为研究对象,重点考察了A2N2系统启动过程中的脱氮除磷特性。试验结果表明:采用在A2/O-SBR和N-SBR单元分别接种种泥,分开培养驯化聚磷菌污泥和硝化菌生物膜,并利用A2/O-SBR单元的出水作为N-SBR单元的进水,25 d好氧硝化菌生物膜挂膜成功,氨氮去除率稳定在93%以上;A2/O-SBR单元采用先厌氧/好氧(A/O)后厌氧/缺氧(A/A)的运行方式,43 d成功培养富集了反硝化聚磷菌(DPAOs),DPAOs占PAOs的67.81%,反硝化除磷率在77.9%以上;启动成功后原水中约73%和13%的COD分别在A2/O-SBR单元的厌氧段和N-SBR单元曝气过程中被去除,系统出水COD、NH+4-N、PO43--P、TN浓度分别为40.6、0、0.4、13.5 mg·L-1,达到国家《城镇污水处理厂污染物排放标准》(GB 18918-2002)一级A排放标准。 相似文献
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生物膜中反硝化除磷作用的研究 总被引:6,自引:1,他引:5
分析了生物膜反硝化除磷系统在生物量,污泥龄,以及碳、氮、磷质量比方面和活性污泥法反硝化除磷系统的差异。通过试验给出了生物膜反硝化除磷系统的最佳污泥龄等运行参数,并对试验现象和结果在理论上进行了分析。试验结果表明,生物膜反硝化除磷系统的最佳水力停留时间为15 d,和活性污泥法反硝化除磷系统的最佳水力停留时间(约12 d)相差不大;生物膜反硝化除磷系统的最佳碳、氮、磷质量比为26.6∶7.67∶1,其中最佳碳、氮质量比为3.5,最佳碳、磷质量比为26.6。 相似文献
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Activated sludge process has been widely used to remove phosphorus and nitrogen from wastewater. However, the nitrogen and phosphorus removal is sometimes unsatisfactory due to the low influent COD. Another problem with the activated sludge process is that large amount of waste activated sludge is produced, which needs further treatment. In this study, the waste activated sludge alkaline fermentation liquid was used as the main carbon source for phosphorus and nitrogen removal under anaerobic followed by alternating aerobic-anoxic conditions, and the results were compared with those using acetic acid as the carbon source. The use of alkaline fermentation liquid not only affected the transformations of phosphorus, nitrogen, intracellular polyhydroxyalkanoates and glycogen, but also led to higher removal efficiencies for phosphorus and nitrogen compared with acetic acid. It was observed that ammonium was completely removed with either alkaline fermentation liquid or acetic acid as the carbon source. However, the former resulted in higher removal efficiencies for phosphorus (95%) and nitrogen (82%), while the latter showed lower ones (87% and 74%, respectively). The presence of a large amount of propionic acid in the alkaline fermentation liquid was one possible reason for its higher phosphorus removal efficiency. Exogenous instead of endogenous denitrification was the main pathway for nitrogen removal with the alkaline fermentation liquid as the carbon source, which was responsible for its higher nitrogen removal efficiency. It seems that the alkaline fermentation liquid can replace acetic acid as the carbon source for phosphorus and nitrogen removal in anaerobic followed by alternating aerobic-anoxic sequencing batch reactor. 相似文献
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净水厂聚合氯化铝铁污泥对污水中磷的吸附作用 总被引:2,自引:0,他引:2
采用控制变量法,逐一研究初始pH值、污泥投加量、初始磷浓度等条件下的聚合氯化铝铁(PAFC)污泥的磷吸附过程。结果表明,在pH值为4.59.0时,污泥对磷的吸附过程稳定,磷的去除率和单位质量污泥对磷的吸附量随pH值的下降而升高。磷的去除率随污泥投加量的增加而增大,随污水的初始磷浓度增大而减小。单位质量污泥磷吸附量随污泥投加量的增加而减小,随污水的初始磷浓度增大而增大。准二级动力学方程可以很好地描述污泥磷吸附过程。通过Langmuir和Freundlich吸附等温线方程发现,PAFC污泥具有较强的磷吸附能力,最大理论磷吸附量为6.049 mg/g。 相似文献
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为了提高脱氮除磷的效率,采用序批式生物反应器(SBR)工艺处理模拟生活污水,考察了不同温度下N/P、污泥龄(SRT)对厌氧/好氧/缺氧序批式生物反应器(AOA-SBR)工艺同步脱氮除磷效能的影响。结果表明:当温度为10 ℃、N/P为2~3、SRT为20 d时,NH4+-N、TN和TP去除率分别为78%、69%和56%,污泥产率YS为0.339 kgSS/(kgBOD5),污泥含磷率PC为4.68%。当温度为25 ℃、N/P为3~5、SRT为15 d时,NH4+-N、TN和TP的去除率分别为88%、83%和91%,污泥产率YS为0.253 kgSS/(kgBOD5),污泥含磷率PC为6.35%。当温度为35 ℃、N/P为5~7、SRT为10 d时,NH4+-N、TN和TP去除率分别为80%、66%和73%,污泥产率YS为0.225 kgSS/(kgBOD5),污泥含磷率PC为7.42%。污泥产率YS随着温度和污泥龄的增加而降低,通过调节温度和污泥龄能够实现污泥减量。 相似文献
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Integration of immersed membrane ultrafiltration with the reuse of PAC and alum sludge (RPAS) process for drinking water treatment 总被引:2,自引:0,他引:2
Effects of PAC and alum sludge generated from water treatment process on the effluent quality and fouling of immersed UF membrane were systematically investigated with representative source of natural water and the efficiency of coagulation, PAC adsorption and RPAS to treat natural surface water prior to UF were compared. It was found that the average turbidity removal by RPAS could reach up to 80.2%, and the turbidity removal of immersed membrane UF was independent of the influent, which could be kept at 99%. Particulates were reduced after being pre-treated by different processes, and particles with sizes ranging from 0.5 to 3.5 μm and larger than 13.5 μm were effectively removed by RPAS. UF coupled with RPAS pre-treatment got the best removal for DOM compared to other processes with average DOC and UV254 removal 54.1% and 47.2% due to the high removal in the influent of UF. The residual alum content in the effluent of RPAS with UF was less than coagulation and bacteria were almost all removed by membrane. The membrane-fouling was mitigated by pre-treatment processes at different degrees, TMP of UF coupled with RPAS process was relatively stable in 15 d of run, the adsorption of PAC and large number of Al(OH)3 complexes and precipitates for the foulant molecules might be an important mechanism. 相似文献