油田钻井废水深度处理技术

采用化学混凝-铁炭微电解-电渗析技术对钻井废水进行了深度处理实验。实验结果表明：废水pH和反应时间是影响铁炭微电解处理效果的重要因素,当废水pH为1．5,反应时间为120min时,COD去除率为50％;在电渗析除Clˉ过程中,采取直流方式出水时,在进水流量为20L／h、操作电压为30V、运行时间为15min的条件下,Clˉ去除率可达75％;而采取循环方式出水时,运行时间是影响电渗析除Clˉ效果的主要因素,当运行时间大于等于60min时,出水中Clˉ的质量浓度低于350mg/L,达到DB51／190-1993（四川省污水排放标准》中的三级排放标准。     

纳滤处理炼化污水反渗透浓水

分别采用4种纳滤膜处理某炼化公司的反渗透浓水。在初始COD为57.8 mg/L、TOC为23.94 mg/L、ρ(Ca2+)为289.0 mg/L、ρ(Mg2+)为54.6 mg/L、ρ(SO42-)为327.7 mg/L、ρ(Cl-)为1 106.8 mg/L的条件下,经纳滤处理后COD去除率达60%以上,污水COD降至30 mg/L以下,TOC去除率为31.9%~85.5%,阳离子的去除率为33.9%~97.0%,SO42-的去除率为63.3%~97.6%,Cl-的去除率较低。膜A的膜孔分布密集,具有很高的通量,对有机物和无机盐的截留效果较差;膜B和膜C对有机物和二价离子的截留效果较好;膜D的膜孔分布稀松,膜通量最低,对有机物和无机盐的截留能力均较强,但随出水体积的增加,对无机盐的截留能力下降较为明显。4种纳滤膜的性能各异,可满足不同企业的需求,具有良好的应用前景。     

粉煤灰吸附—石灰沉淀处理高浓度含氟废水

采用粉煤灰吸附—石灰沉淀处理高浓度含氟废水.正交实验得到的最佳工艺条件为:反应温度10℃,石灰加入量3.0 g/mL,反应时间60 min,废水pH 6.88.在此最佳工艺条件下处理F质量浓度为150 mg/L的含氟废水,Fˉ去除率为97.53％.Mn2+,Fe3+,Mg2+,A13+,Zn2+单独存在时,随5种阳离子质量浓度增大,Fˉ去除率略有增加;当5种阳离子共同存在且质量浓度均大于500 mg/L时,Fˉ去除率下降.PO43-,SO42-,CO32-,NO3-单独存在时对Fˉ去除率影响不大;当4种阴离子共同存在且质量浓度均大于800 mg/L时,Fˉ去除率低于对照实验.     

升流式厌氧污泥床处理抗生素制药废水

采用升流式厌氧污泥床(UASB)反应器处理抗生素制药废水。实验结果表明:进水COD为9 300mg/L、容积负荷为9.3kg/(m3.d)时,COD去除率仍在80%以上;在COD∶ρ(SO42-)=6、进水ρ(SO42-)为1 500mg/L以下时,COD去除率一直保持在80%以上,SO42-去除率始终在23%以下。SO24-的存在对产甲烷菌影响不大,UASB反应器运行稳定。UASB反应器产沼气的产气率达0.48m3/kg,沼气中甲烷体积分数为68%,二氧化碳体积分数为27%,产甲烷菌具有较高的活性。     

催化臭氧氧化法处理维生素C生产废水

采用催化臭氧氧化工艺处理维生素C生产废水.考察了不同工艺条件对废水COD、色度、Ca2+去除率的影响.实验结果表明,催化剂为TiO2(20％,质量分数,下同)-SiO2(80％),反应温度75℃,水力停留时间30min的最佳工艺条件下,处理后出水的COD、色度和ρ(Ca2+)分别为63.9 mg/L、0倍和49.4 mg/L,COD、色度和Ca2+去除率分别为78％、100％和95％.出水水质指标满足GB8986-1996《污水综合排放标准》.     

烟气脱硫溶液中硫酸根的去除

分别采用石灰乳化学沉淀法和低温结晶法去除烟气脱硫溶液中的SO42-。实验结果表明：在室温、CaO溶液质量分数25%的条件下,石灰乳化学沉淀法对SO42-的去除率仅为59.51%,且向溶液中引入了Ca2+,产生的硫酸钙固体废物难以再生利用;采用低温结晶法处理烟气脱硫溶液,在结晶温度7 ℃、结晶时间3 h、NaOH加入量34.8 g/L的条件下,SO42-的去除率为82.04%、滤液中的ρ（Na+）为3.88 g/L。在现场工业应用试验中,采用低温结晶法去除烟气脱硫溶液中的SO42-,平均SO42-的去除率可达70.00%以上,滤液中的ρ（Na+）小于15.00 g/L。该法可有效抑制烟气脱硫溶液中SO42-含量的增加。     

厌氧膨胀颗粒污泥床生物膜反应器同步产甲烷-硫酸盐还原的快速启动

采用新型厌氧膨胀颗粒污泥床生物膜反应器(EGSBBR)处理含硫酸盐有机废水.在不添加硫酸盐的条件下,运行30 d后系统产甲烷成功启动;随后逐步提高硫酸盐质量浓度至100 mg/L,运行71 d后系统COD去除率和SO42-去除率分别达98.1％和74.7％,甲烷产生量为470.7 mL/d,成功实现了同步产甲烷-硫酸盐...     

液膜分离法处理石灰法草浆纸厂废水

用乳状液膜法处理石灰法草浆纸厂废水,选择膜体系为T152-煤油-TOA-H2SO4.研究了膜体系的组成和工艺条件对COD去除率的影响.在试验条件下经一级处理COD去除率可达44%.采用低电压破乳,破乳后油相可重复使用.该方法具有处理成本低、无二次污染的优点.     

用水解酸化池-膜生物反应器处理活性艳红X-3B废水

采用水解酸化池-膜生物反应器处理含活性艳红X-3B的模拟废水,研究了水力停留时间（HRT）对水解酸化池废水处理效果的影响,考察了水解酸化池-膜生物反应器对废水的处理效果及膜生物反应器中污泥沉降性能对膜污染的影响。实验结果表明：水解酸化池HRT为16h时,废水的可生化性最好,挥发性脂肪酸质量浓度与COD比值为0．5;HRT为17h时,废水脱色率达69％,而COD的去除率受HRT影响较小;膜生物反应器主要起去除废水中COD的作用;水解酸化池-膜生物反应器处理后废水的脱色率和COD去除率分别为83％和97％;膜生物反应器中活性污泥沉降性能的变化直接影响膜污染的速率。     

纳滤膜处理含锰废水

采用纳滤膜处理电解锰生产过程中产生的含锰废水,考察了操作压力、阻垢剂和反冲洗等因素对膜通量和各金属离子截留率的影响。实验结果表明:操作压力越大,膜通量越大,且膜通量随运行时间延长下降得越快;在操作压力为2.0 MPa的条件下,纳滤膜对Mg2+的截留率为90.69%,对Mn2+的截留率为89.72%,对Ca2+的截留率最高,达100%;加入阻垢剂后,纳滤膜的膜通量比未加入阻垢剂时的膜通量略大;反冲洗4次后,膜通量均可完全恢复。     

Effects of competitive ions,humic acid,and pH on removal of ammonium and phosphorous from the synthetic industrial effluent by ion exchange resins

The removal of the ammonium and phosphorous from the synthetic industrial effluent by the ion exchange resins was studied in this paper, aiming at the determination of the effects of competitive ions, humic acid, pH and resin amount. The kinetic experiments show that the equilibrium time for the removal of both contaminants in the absence and presence of the competing matters was 4 h. Na+ and K+ significantly reduced the ammonium removal percentage, while the existence of Mg2+, Ca2+ and humic acid also had a negative influence. Adsorption of ammonium ions in both absence and presence of Na+ and K+ observed the linear isotherm, however, it did not follow commonly used isotherms in the presence of Na+, K+, Mg2+, Ca2+ and humic acid. The phosphorous removal decreased in the presence of the competitive matters, such as Cl-, CO3(2-), SO4(2-) and humic acid. Higher pH can cause higher phosphorous removal percentage. A decrease in the solution pH was observed in the phosphorous removal experiments, possibly due to the ion exchange and the adsorption of OH-. Uptake of humic acid by the resins was observed. Finally, a series of fixed-bed experiments were performed, showing that the performance was dependent on the empty bed contact time (EBCT). Higher EBCT would cause higher bed volumes of both treated ammonium and phosphorous.     

UASB反应器反硝化处理对氨基二苯胺生产废水

采用UASB工艺处理橡胶助剂对氨基二苯胺（RT培司）生产废水。实验结果表明：UASB启动初期（1~16 d）,COD去除率由60.8%降至24.2% ,TOC去除率由75.6%降至37.2%;UASB运行16 ~50 d,COD去除率逐渐提高;运行50 d时COD去除率为69.4%,TOC去除率高达90.0%。在进水COD负荷不超过6 kg/（m³·d）的条件下,UASB对COD的去除率为42.7%~69.4%,TOC去除率为58.0%~90.0%,NO_{3^--N去除率接近100%。本实验最佳进水TOC 与TN 比为2.0,UASB进水pH可调节为4.5左右,反应温度为18~34 ℃时对UASB反硝化处理效果影响不大。UASB对苯系化合物的去除率从高至低顺序为对硝基酚>苯酚>苯胺。}     

高含水油泥调质脱稳用剂

高含水油泥主要来自于页岩气田、油气田和炼厂的污水处理场（站）,含水率一般高达90%以上,成分复杂、乳化严重,是性质稳定的多相体系。破胶脱稳是高含水油泥处理处置与利用的前提,也是减量化的瓶颈,其核心是调质脱稳用剂的优选。介绍了高含水油泥的性质及调质脱稳的原理和方法,阐述了高含水油泥调质脱稳用剂的研究及应用现状,总结了助滤剂、氧化剂、电解质、破乳剂、絮凝剂和微乳化剂等常用药剂的调质机理、适应范围、研究实例和优缺点,并提出了调质脱稳用剂未来的发展方向。     

SMBBR-AF-SMBBR组合工艺处理高氨氮农药废水

采用特异性移动床生物膜反应器(SMBBR)和厌氧生物滤池(AF)组合工艺处理高氨氮农药废水。考察了HRT、pH和DO等工艺条件对SMBBR-AF-SMBBR组合工艺运行稳定期COD和氨氮去除率的影响。试验结果表明,在进水COD为2 408~7 440 mg/L、ρ(NH_4~+-N)为160.21~433.84 mg/L、TN为208.27~537.65 mg/L、HRT为8d、pH为8.0、DO为4 mg/L的条件下,处理后出水平均COD为342 mg/L,COD去除率达92.3%;ρ(NH_4~+-N)小于4.0mg/L,氨氮平均去除率为89.2%;TN小于50 mg/L,平均TN去除达83.0%。出水各指标均优于原A2O工艺出水。     

生物活性炭工艺处理炼油厂反渗透浓缩水

采用生物活性炭工艺处理炼油厂反渗透浓缩水.在无烟煤破碎炭粒径为2.4～5.9 mm、进水pH为7.5、空床停留时间为30 min、平均进水COD为100 mg/L的条件下,系统可稳定运行48 d,平均COD去除率为50％,平均A254(反渗透浓缩水在波长254 nm处的吸光度)降低率为77％,出水COD低于60 mg/...     

湿法腈纶废水的生化处理

采用水解酸化—固定化微生物流化床—氧化混凝联合工艺处理湿法腈纶废水.该工艺采用的高效菌微生物固定化技术及新型氧化混凝技术均对湿法腈纶废水有较好的处理效果.实验结果表明:在水解酸化温度为42℃、水解酸化运行周期为20 h的条件下,接种活性污泥和高效菌的SBR的COD去除率为26.0％;在新型氯铁型氧化混凝剂加入量为15 mL/L的条件下,混凝出水COD可降至66 mg/L.水解酸化—固定化微生物流化床—氧化混凝联合工艺的总COD去除率可达89.4％.     

有机磷阻燃剂生产废水预处理工艺研究

采用液膜萃取—酸析沉降—络合萃取组合工艺对有机磷阻燃剂生产废水进行预处理.最佳工艺条件为:液膜萃取时,液膜油相(表面活性剂与煤油的混合液)与内水相(H2SO4溶液)的体积比2∶1、乳化液膜与废水的体积比1∶8、废水pH 13.0,硫酸体积分数10％、煤油中表面活性剂质量浓度30 g/L、液膜萃取时间 15 min;酸析沉降时,废水pH l.0,酸析沉降时间30 min;络合萃取时,络合萃取剂(烷基叔胺N235与煤油的混合液)中烷基叔胺N235体积分数30％,络合萃取剂与废水的体积比1∶4,废水pH l.0,络合萃取时间30 min.在此最佳处理条件下,废水COD总去除率可达93％,吡啶去除率达99.9％以上,总磷去除率可达97％,BOD5/COD提高至0.32,有利于后续生化处理.     

Advanced physico-chemical treatment experiences on young municipal landfill leachates

In this study, Membrane Filtration (UF+RO), Struvite (MAP) precipitation and ammonia stripping alternatives were studied on biologically pre-treated Landfill Leachate. The results indicated that the system including the Upflow Anaerobic Sludge Blanket Reactor (UASBR) and Membrane Reactors (UF+RO) has been offered as an appropriate treatment alternative for young landfill leachates. This system provided high removals of COD, colour and conductivity (>98-99%). For ammonia removal, struvite precipitation was applied at the stoichiometric ratio (Mg:NH4:PO4=1:1:1) to anaerobically pre-treated raw landfill leachate effluent having an influent ammonium concentration of 2240 mg/l. Maximum ammonium nitrogen removal was observed as 85% at pH of 9.2. In ammonia stripping following 2 h of aeration, the removal was 72% at pH=12 while the removals were around 20% at pH=10 and pH=11. When membrane reactor, and struvite precipitation or ammonia stripping was applied to anaerobically pre-treated effluents, the results indicated that each system could be used as an appropriate post-treatment option for young landfill leachates. In economic aspect, ammonia stripping was found as the cheapest alternative with high ammonium removal. However, when both high COD and ammonium removals were to be achieved membrane technology such as UF+RO (SW) could be considered as the most appropriate system due to the fact that COD removal could be obtained very low by ammonia stripping.