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1.
常温下,采用二级生物处理高浓度乳品有机废水的工艺,出水COD≤100,BOD5≤30mg/l,SS≤70mg/l,达到国家一级排放标准.运营成本明显降低.  相似文献   

2.
人工快速渗滤复合系统处理洗浴污水的试验研究   总被引:22,自引:0,他引:22  
针对传统污水快速渗滤土地处理系统水力负荷低,占地面积大的弱点,提出了采用人工砂和天然砂作为渗滤介质建立复合系统的试验方案,并以洗浴污水为研究对象进行了5个月的室内试验研究。结果表明,复合系统具有较高的水力负荷和较好的去污效果,其COD,BOD5,SS和阴离子洗涤剂(以MBAS代表)的平均去除率分别为86.25%,86.75%,98.95%和90.86%。处理出水中COD,BOD5,SS和阴离子洗涤剂的平均浓度分别为17.30,5.84,0.3和0.18mg/l。  相似文献   

3.
采用多阶段水解 -好氧串联工艺处理高浓度玉米淀粉废水。试验结果表明 :①废水经多阶段水解 -好氧工艺的水解段H1后 ,废水的 ρ(BOD5) /ρ(CODCr)从 0 .90提高到 0 .95 ;废水经水解段H2 后 ,废水的 ρ(BOD5) /ρ(CODCr)从 0 .81提高到 0 .97,说明水解段具有提高废水可生化性的功能。②在总水力停留时间 (HRT)为 6 0h、进水pH为 5 .9~ 6 .0 8和进水 ρ(CODCr)、ρ(BOD5)、ρ(NH+ 4)平均分别为 82 0 5mg/L、7395mg/L、16 0 .0mg/L的情况下 ,CODCr、BOD5和NH+ 4去除率分别达97.7%、99.1%和 88.1% ,出水水质达到或接近国家污水排放二级标准 (GB8978- 96 )。③各处理单元对CODCr、NH+ 4去除效果各不相同。  相似文献   

4.
嫩江齐齐哈尔市江段水环境优化管理方案   总被引:2,自引:0,他引:2  
对研究区地表水环境质量现状分析及预测的基础上,引入响应系数和最优化理论,以各断面水环境功能标准和各排污口排放标准为约束条件,建立了水环境优化管理模型,最后提出有利于当地经济和水环境可持续发展的优化管理方案:方案一为现状优化管理方案,按此方案各断面均能达到其相应的水环境功能标准,要求红光糖厂、斯达造纸厂和氧化塘COD处理后浓度分别为1500mg/L、900mg/L和200mg/L,其它排污口维持原排放浓度;方案二为“下个五年”优化管理方案,按此方案各排污口均能达到其相应的排放标准,要求红光糖厂及斯达造纸厂的COD和BODs处理后浓度分别为100mg/L和30mg/L。北市区生活污水COD和BOD5处理后浓度分别为150mg/L和60mg/L,氧化塘COD处理后浓度为150mg/L,其他排污口维持原排放浓度。  相似文献   

5.
中温UBF与UASB两相厌氧系统处理垃圾渗滤液的实验研究   总被引:1,自引:0,他引:1  
针对石碑岭垃圾场渗滤液水质特性,采用以高效生物陶粒为填料的UBF反应器作酸化相,以UASB反应器作甲烷相的两相厌氧系统进行了处理垃圾渗滤液的实验研究.实验结果表明:在系统进水CODCr和BOD5质量浓度分别为3 887 mg/L和819 mg/L,UBF与UASB的HRT分别控制在10.3 h和61.7 h时,CODCr和BOD5总去除率分别为85.4%和90.1%,UBF酸化率达42.9%,BOD5/CODCr比值由0.21提高到0.39.  相似文献   

6.
中空纤维膜作生物膜载体无泡供氧处理污水研究   总被引:5,自引:0,他引:5  
采用中空纤维膜作生物膜载体及无泡供氧装置,利用具有死端式和漂浮式特点的浸没式接触氧化工艺进行污水处理试验研究.结果表明:在控制系统工作压力0.03 MPa、污水中ρ(DO)为5~8 mg/L及HRT=8h的条件下,污水中COD、BOD、SS的去除率分别达70%、90%和75%以上,NH3 -N、P的去除率也在70%以上.系统连续运行3个月,表现了较好的稳定性和抗有机负荷冲击能力.  相似文献   

7.
混凝-催化氧化处理含油污水实验研究   总被引:2,自引:0,他引:2  
采用复合化学混凝及催化氧化联合工艺对油田生产废水进行了实验研究.结果表明:含油废水经混凝处理后,剩余ρ(CODcr )可以达到300 mg/L左右,剩余悬浮物质量浓度小于10mg/L;再经活性炭载Cu、Pd催化剂的深度处理,含油污水中的ρ(CODcr )值由315 mg/L降至50 mg/L以下,达到了国家的相关排放标准.催化剂可以再生重复使用.  相似文献   

8.
ABR-生物接触氧化工艺处理低碳氮比生活污水试验   总被引:1,自引:0,他引:1  
近年来,城市生活污水呈现出低碳氮比的趋势,造成污水处理脱氮困难.采用ABR-生物接触氧化工艺对低碳氮比生活污水进行试验研究,确定了试验运行参数,即在进水COD/N为2~7范围内,当HRT=10 h,R=2.5、T=30℃时,系统对TN的去除效果良好;TN的平均去除率随着碳氮比的减小而迅速降低,此时,碳源不足成为制约脱氮效果的主要原因;在最佳运行条件下,当进水COD/N为6~7时,TN平均去除率达到80%以上,出水TN质量浓度小于15 mg/L,满足<城镇污水处理厂污染物排放标准>一级A标准.  相似文献   

9.
连续流气提式流化床启动过程中好氧颗粒污泥的形成机制   总被引:4,自引:0,他引:4  
探讨连续流气提式好氧颗粒污泥流化床(CAFB)反应器的运行特征,对该工艺颗粒污泥形成过程、形成机理和颗粒性质进行分析。以市政污泥为接种污泥,以醋酸钠为碳源,在连续运行方式下培养好氧颗粒污泥。研究结果表明:CAFB反应器启动的第4-5天即有大量颗粒污泥形成,颗粒直径800~1 000 μm,比重1.006,生物相丰富,能够分泌大量胞外聚合物。当COD有机负荷高达8 和13 kg/(m3·d)时,对COD处理效率均维持在93%~97%,COD出水质量浓度仅为30~80 mg/L,引起启动后期丝状菌的大量繁殖,污泥流失。进一步提高污泥负荷有望控制污泥膨胀。  相似文献   

10.
水解-好氧组合工艺处理玉米淀粉废水的机理   总被引:6,自引:2,他引:4  
根据水解-好氧处理系统中碳水化合物、蛋白质、挥发性有机酸和微生物的变化规律,探讨了利用水解-好氧组合工艺处理玉米淀粉废水的机理,得出废水中碳水化合物的降解速率远大于蛋白质.在水力停留时间为10h的第一水解段,蛋白质的去除率仅为16%,而碳水化合物的去除率却高达91%.在此组合工艺中,水解段均具有去除废水中BOD5、CODCr和提高废水可生化性的双重作用,但水解段对BOD5的去除率小于对CODCr的去除率.好氧段的主要作用是去除CODCr、氮、磷.好氧生物膜中出现钟虫、累枝虫和轮虫组合是整个工艺出水水质良好的生物学标志.  相似文献   

11.
吗啉废水的生化处理工艺   总被引:2,自引:0,他引:2  
以含有吗啉、甲基吗啉的高浓度有机废水为研究对象,提出了曝气吹脱-吸附-生物处理的联合工艺,并在室内进行了小试实验。结果表明:原废水经过2次曝气吹脱后,ρ(NH3-N)从62 500 mg/L降为431 mg/L,ρ(COD)从50 840 mg/L降为26 051 mg/L。通过吸附实验,ρ(COD)从26 051 mg/L降为2 769 mg/L,ρ(NH3-N)从412 mg/L降为134 mg/L。在生物处理室内小试实验中,采用了活性污泥反应器与曝气生物滤池相结合的处理工艺。在活性污泥反应系统中,当废水pH为7.5、ρ(DO)为4.3 mg/L、水力停留时间为30 h时,COD的去除率最高,可以达到83.1%。在曝气生物滤池中,当ρ(DO)为3.3 mg/L时,COD去除率最高,达到55.8%。在生物处理的最佳参数条件下进行连续监测,当进水ρ(COD)为2 769 mg/L、出水ρ(COD)平均值为387 mg/L时,COD去除率可达到85.9%。吗啉废水经过此联合工艺的处理,ρ(COD)从50 840 mg/L降为387 mg/L。  相似文献   

12.
采用混凝沉淀技术处理钨矿选矿废水,通过试验确定HNJY新型高效复合絮凝剂作为混凝剂最为合适,投加量为120mg/L,经处理后废水出水水质符合国家污水排放标准并能回用,废水SS约11500mg/L,处理后的出水要求为SS<10mg/L。技术经济分析,投资总费用为67.5万元,处理成本为0.60元/m3,设计工艺可靠且经济合理。本工程既防止了废水对环境的潜在污染,又解决了枯水期选矿用水不足的问题。  相似文献   

13.
Sewage treatment station in oilfield needs a new process to meet the desired requirements. A new process was proposed to meet the discharge standards, which consisted of the following sub-processes: electrochemical treatment → coagulation treatment → integrated biochemical treatment of moving bed biofilm reactor and membrane bio-reactor → combined treatment process of macroporous adsorption resin. Electrochemical treatment included 5 electrolytic cells, total volume of which was 10 L. The PFS was chosen as the coagulants in the coagulation treatment, and the removal rate of COD could reach 66% when the dosage of PFS was 500 mg/L. The biochemical treatment consisted of anoxic tank, aerobic tank and membrane zone, and the removal rate of COD was about 55–70% when HRT was 12 h. SD300 resin was chosen as the best adsorbent in the treatment using macroporous adsorption resin. In addition, the effluent COD after coagulation treatment process becomes about 180 mg/L, the effluent COD after biological treatment becomes about 50 mg/L, and the last effluent COD with the macroporous adsorption resin becomes about 20 mg/L. The three-dimensional fluorescence spectrum was used to analyze the differences in types of organic matters in water samples between the raw water and the treated one. The results demonstrated that the new process meets the needs of wastewater treatment.  相似文献   

14.
在上流式好氧颗粒污泥床反应器中, 以厌氧颗粒污泥和好氧絮状活性污泥为接种泥, 采用人工配制的模拟废水, 成功培养出性能优异的好氧颗粒污泥.反应器内污泥浓度稳定在5g/L左右, 颗粒污泥粒径为0.5~2.0mm, 当进水COD为2000mg/L, 容积负荷为4.8kg/(m3·d)时, 系统对COD的去除率稳定在96%以上.通过扫描电镜观察, 好氧颗粒污泥是层状结构, 表面有大量丝状菌缠绕, 内部有短杆菌和空穴存在.逐步提高制药废水在进水中的比例, 经过47d的培养, 生物制药废水完全取代模拟废水, 系统对COD、NH3-N、TP的去除率分别稳定在90%、90%和70%以上.   相似文献   

15.
The upflow anaerobic sludge blanket process followed by the biological aerated filter process was employed to improve the removal of color and recalcitrant compounds from real dyeing wastewater. The highest removal efficiency for color was observed in the anaerobic process, at 8-h hydraulic retention time, seeded with the sludge granule. In the subsequent aerobic process packed with the microbe-immobilized polyethylene glycol media, the removal efficiency for chemical oxygen demand increased significantly to 75 %, regardless of the empty bed contact time. The average influent non-biodegradable soluble chemical oxygen demand was 517 mg/L, and the average concentration in effluent from the anaerobic reactor was 363 mg/L, suggesting the removal of some recalcitrant matters together with the degradable ones. The average non-biodegradable soluble chemical oxygen demand in effluent from the aerobic reactor was 87, 93, and 118 mg/L, with the removal efficiency of 76, 74, and 67 %, at 24-, 12-, and 8-h empty bed contact time, respectively. The combined anaerobic sludge blanket and aerobic cell-entrapped process was effective to remove the refractory compounds from real dyeing wastewater as well as in reducing organic loading to meet the effluent discharge limits. This integrated process is considered an effective and economical treatment technology for dyeing wastewater.  相似文献   

16.
In this research, physical, chemical and biological treatability of Tehran solid waste leachate was studied. Results indicate that the amount of COD for the fresh raw leachate of Tehran is equal to 66,608 mg/l. The leachate is transferred to an equalization tank for storage and pH control process. After neutralization, leachate is introduced to an up flow and down flow anaerobic reactor. The effluent of anaerobic reactor is conducted to a sequencing batch reactor. Sequence batch reactor (SBR) effluent was pumped in to sand and activated carbon filters, after chemical coagulation and clarification. Results showed that anaerobic reactor with detention time of 3 days had a 35% COD removal and increasing the detention time to 4.5 days would improve the COD removal to 45%. Nutrient adjustment with phosphorus and nitrogen increased the initial 23% efficiency of sequence batch reactor to 44%. The effluent COD of SBR reactor was 21,309 mg/l. Recycling of aerobic reactor effluent with incoming feed to anaerobic reactor reduced the anaerobic reactor influent COD to 20,000 mg/l and this caused 53% and 57% COD removal in the anaerobic and aerobic effluent, respectively. The total systems COD performance increased to 80% and SBR effluent COD eventually reduced to 4,000 mg/l. Coagulation, flocculation and sedimentation processes were practiced to make the 4,000 mg/l effluent COD comply with environmental standards of Iran. The optimum coagulant found to be ferric chloride with the dosage of 50 mg/l at pH of 12, which reduced 10% of COD to an amount of 3,676 mg/l. The effluent was stored in a tank and then pumped in to pressure sand filter and afterwards to activated carbon filter. The COD removal was three and 90% for sand and activated carbon filters, respectively. The total process reduced the remaining COD to 36 mg/l, which is in compliance with environmental standards of Iran.  相似文献   

17.
In the present study, the effectiveness of physicochemical treatment processes (coagulation and Fenton’s oxidation) was investigated for simulated dairy wastewater (pH = 7.3, chemical oxygen demand (COD) = 3600 mg/l, 5-day biochemical oxygen demand (BOD5) = 1950 mg/l, total Kjeldahl nitrogen (TKN) = 87 mg/l, and total phosphorous (TP) = 14 mg/l). Plain and ballasted coagulation runs were carried out in a jar apparatus, while Fenton’s oxidation was performed in a three-neck glass reactor. Ballasted coagulation caused an enhancement in the settling rate of sludge though no significant enhancement in the removal of organics was observed. Individually, coagulation and Fenton’s oxidation processes resulted in ~67 and 80 % COD removals, respectively, from the wastewater. The sequential treatment exploring coagulation followed by Fenton’s oxidation showed overall COD, BOD5, TKN, and TP reductions of ~93, 97, 84, and 70 %, respectively, from the wastewater. However, a biological post-treatment would be required to achieve the effluent discharge standards. The removal of proteins, fats, and amino acids from wastewater was confirmed from Fourier transform infrared analysis of the settled sludge (obtained after coagulation process). Preliminary cost analysis suggested coagulation and the sequential treatment (i.e. coagulation followed by Fenton’s oxidation) as the preferred options.  相似文献   

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