Fe^2＋—H2O2氧化法处理氨基J酸工业废水的研究

用Ｆｅ＾２＋－Ｈ２Ｏ２氧化法处理氨基Ｊ酸工业废水。结果表明,当溶液ｐＨ＝１－３,Ｈ２Ｏ２和Ｆｅ＾２＋用量分别为Ｈ２Ｏ２：Ｆｅ＾２＋１０：１,Ｈ２Ｏ２：ＣＯＤＣｒ＝２ｇ：ｇ时,Ｊ酸废水的ＣＯＤＣｒ去除率达６６．７％,氨基去除率达６８．４％。处理后的废水ＢＯＤ５／ＣＯＤＣｒ＝０．５,已达到生化处理的要求。该法可作为氨基Ｊ酸废水的预处理方法。     

光催化氧化-混凝工艺处理化工废水

探索了光催化氧化－混凝工艺处理废水的工艺条件,最佳光催化氧化处理条件为ＰＨ＝３,催化剂为铁盐,氧化剂Ｈ２Ｏ２,低压汞灯,光照时间１．５ｈ,废水温度４５℃,温凝剂选用ＰＡＣ和ＰＡＭ（混凝剂的投加量为原水ＣＯＤｃｒ：ＰＡＣ：ＰＡＭ＝７：１．５：０．０１）,混凝ＰＨ６,沉降时间０．５ｈ,在该工艺条件对ＣＯＤｃｒ为１７３－７０１４４ｍｇ／Ｌ的十二烷基苯磺酸钠废水、苯酐废水、富马酸废水、邻苯二甲酸二辛酯废水     

O3—H2O2组合法处理染料中间体废水的研究

报道了Ｏ３－Ｈ２Ｏ２组合法处理含有磺酸基团的萘系染料中间体废水的试验结果。对ＣＯＤ约为１６００ｍｇ／ｌ的某高浓度染料中间体废水，用５．１ｇＯ３／ｌ和２．０ｇＨ２Ｏ２／ｌ进行处理，可达到约６０％的ＣＯＤ及色度去除率，并使ＢＯＤ／ＣＯＤ的比值超过０．３，为后续生化处理创造了条件。     

生化法处理煤气废水

采用Ａ／Ｏ工艺处理煤气废水的研究结果表明,该工艺能同时去除煤气废水中的有机物和氨氮,在试验确定的条件下,该工艺对煤气废水中的ＣＯＤｃｒ去除率达９１．０％,ＢＯＤ５去除率达９９．１％,ＮＨ３－Ｎ去除率达９９．２％,ＴＮ去除率达９４．７％。     

厌氧—好氧法处理渗滤液与城市污水混合废水的可行性

彩厌氧－好氧工艺对不同浓度的垃圾填埋场渗滤液与城市污水在不同混合比（ＶＳＨ：ＶＣＨ）时的处理效果及可行性进行了研究,厌氧段采用新型ＡＢＲ反应器并将控制在水解酸化阶段。研究表明,当原渗滤液ＣＯＤ〈５５００ｍｇ／Ｌ时,ＶＳＨ：ＶＣＨ达４：６是可行的,其稳定运行时的ＣＯＤ和ＢＯＤ５去除率可分别达８８．９％和９６．８％当原渗滤液ＣＯＤ≥６５００～８８００ｍｇ／Ｌ时,须将ＶＳＨ：ＶＣＨ控制在２．８以内。     

H-酸的催化湿式氧化反应过程研究

湿式氧化（ＷＡＯ）和催化湿式氧化（ＣＷＡＯ）都能有效地处理染料中间体－－Ｈ－酸。所有的Ｈ－酸在５ｍｉｎ内均被支除和形成一些中间产物。在不同反应时间段测定了ｐＨ值及阴、阳离子和小分子有机酸等中间产物。分析表明,ｐＨ值与ＣＯＤ的去除及有机酸的产生有密切的联系,Ｈ－酸被氧化成ＮＨ４＾＋、ＳＯ４＾２－、ＨＣＯＯＨ和ＣＨ２ＣＯＯＨ。ＷＡＯ法的瓜速率慢而且氧化乙酸困难。而ＣＷＡＯ法的反应速率不但快而且能有效地     

驯化活性污泥处理明胶有机废水的实验

利用驯化活性污泥对组分复杂的明胶有机废水进行有机物降解实验。结果表明,明胶废水的ＢＯＤ５／ＣＯＤｃｒ比值为０．４４－０．４６,ＣＯＤｃｒ进水浓度在１０００－１２００ｍｇ／Ｌ人,ＣＯＤｃｒ和ＢＯＤ５去除率分别达８１％－８３％和８６％－９１％。     

SBR法处理化学药物制剂废水

采用 ＳＨＲ法处理化学药物制剂废水． 调节 ｐＨ至７．５,进水 ＣＯＤｃｒ ２２４～１５３０ ｍｍ／Ｌ,曝气１０ ｈ, ＣＯＤｃｒ容积负荷达２．５８ｋｇ／ｍ~３·ｄ,ＣＯＤｃｒ的去除率高达９４．２％,处理后出水ＣＯＤｃｒ＜１００ｍｇ／Ｌ,达到综合排放标准（ＧＢ８９７－９６）一级标准。ＣＯＤｃｒ容积负荷至３．８４ ｋｇ／ｍ~３·ｄ, ＣＯＤｃｒ去除率仍＞８５．９％。     

炼油厂废水回用的研究

研究了以活性碳纤维吸附净化炼油厂二次生化砂滤出水的规律，并在实验中摸索出一整套工艺参数，对活性碳纤维反复吸（脱）附使用寿命进行估算，为炼油厂废水处理、回用的工业化提供参考。实验表明，每千克活性碳纤维可净化１．５吨废水，各项指标均达到循环水回用之要求，其吸附－脱附５０次对废水的净化率为：ＣＯＤｃｒ５１．２％，浊度８０．５％，悬浮物８２．１％，对挥发酚、石油类、硫化物等污染物质的净化效率均在９０％以上     

十三碳二元酸发酵有机废水处理研究

运用物化预处理和ＳＢＲ生化工艺对十三碳二元酸发酵废水中高浓度有机物的降解特征及高２硫酸钠对微生物的有害抑制作用进行处理试验,研究结果表明。采用物化预处理与ＳＢＲ生化法相结合的工艺可有效地处理该类废水。经驯化的耐盐微菌胶力和裂口虫为主,废水的ＣＯＤｃｒ去除率可达９２％以上,ＢＯＤ５去除率可达９５％以上。     

污泥中重金属的去除及回收试验

论述了利用离子交换技术循环使用柠檬酸去除污泥中重金属,并置换回收重金属的适宜工艺条件.经柠檬酸处理后,污泥中90%以上的重金属被去除;柠檬酸处理液中的重金属用离子交换法回收,考察了树脂种类、流速、操作方式等因素对离子交换、再生效果的影响;在适宜工艺条件下,重金属的交换率均为100%,而洗脱率均接近90%;柠檬酸及离子交换树脂循环使用,重金属也得到回收,降低了处理成本.     

Production of polyhydroxyalkanoate during treatment of tomato cannery wastewater.

Polyhydroxyalkanoate (PHA) production was achieved using tomato cannery waste coupled with a mixed microbial culture during wastewater treatment. The two-stage PHA production process comprised a sequencing batch reactor (SBR), operating under a periodic feast-famine regime, to accomplish simultaneously wastewater treatment and selection of PHA-accumulating microbes, followed by a batch reactor for the production of PHA-rich biomass. The SBRs were efficient at removing soluble carbon (84%), ammonia (100%), and phosphorus (76%). Meanwhile, PHA-accumulating microbes were enriched under the SBR operating conditions, and PHA content on a cell-weight basis was within the range 7 to 11% in nonfiltered wastewater and 2 to 8% in filtered wastewater. Subsequently, batch studies were implemented with varying loading rates, ranging from 0.4 to 3.2 food-to-microorganism ratios. A maximum 20% PHA content on a cell-weight basis was obtained. Based on the experimental results, a PHA biosynthesis-degradation kinetic model was developed to (1) aid in the design of a pilot- or full-scale PHA production process coupled with wastewater treatment and (2) determine optimal conditions for harvest of PHA-rich biomass.     

Toxicity of herbal pharmaceutical wastewater on fish--Lebistes reticulatus (Peter)

Toxic effects of herbal pharmaceutical wastewater on common fish (Lebistes reticulatus) under laboratory conditions were studied. LC50 values for raw, neutralized, and physico-chemically treated effluent for 24, 48, 72, and 96 h ranged between 3.0-9.5%, 5.0-10.5%, and 35-41%, respectively. It was evident from the studies that physico-chemical treatment reduces the toxicity by more than 30%. This article discusses in detail the bioassay evaluation of raw, neutralized, and primary treated effluent. Physico-chemically treated effluent was further subjected to biological treatment by activated sludge system. Effluent from biological treatment revealed no toxic effect even after one month of exposure.     

油田常用化学品对含油废水处理效果的影响

通过对江汉油田采油废水水质分析以及混凝实验研究,分析采油作业返排液中主要化学组分对含油废水混凝处理效果的影响,探讨了混凝剂、常用油田化学品与浊度及油含量去除率的关系,初步分析了它们的作用机理。研究表明,在钻井液中,单宁、磺化酚醛树脂(SMP)等对含油废水处理的影响很大,在压裂液中瓜胶、重铬酸钾等的影响较大,酸化液中乙酸和柠檬酸等的影响较大,射孔液中盐酸等的影响较大。本研究的结果对于消除返排液对油田生产的不良影响,保证系列增储上产措施的实施及其有效性,避免环境污染,具有十分重要的参考价值。     

SBR法处理柠檬酸废水的试验研究

SBR法处理柠檬酸废水的实验研究结果表明 :当柠檬酸废水COD浓度为 5 0 0— 2 5 0 0mg/L时 ,采用 16h运行周期 ,曝气进水 ,对COD均有很好的去除效果 ,一般在 90 %左右 ;当进水 pH在 3— 10的范围内 ,对COD去除率没有多大影响 ,但保持进水pH在 7— 8之间可以缩短反应时间 ;出水浊度与污泥的沉降性能有关 ,进水结束时MLSS应在 3.5 g/L左右。     

Effect of sulfate reduction activity on biological treatment of hexavalent chromium [Cr(VI)] contaminated electroplating wastewater under sulfate-rich condition

Electroplating wastewater (EW) containing heavy metals was treated by a two-stage packed-bed reactor system. The EW was highly contaminated with hexavalent chromium and other heavy metals as well as sulfate because sulfuric acid had been mainly used to polish the surface of metals to be electroplated. This acidic EW was effectively neutralized in an alkaline reactor where limestone had been packed. The neutralized wastewater together with organic wastewater from a starch-processing factory (SPW) was fed to a bioreactor packed with waste biomass. The SPW was used to supplement the electron donor in the sulfidogenic bioreactor. During the whole operation, we investigated the stoichiometry of electron to see what could be a major factor to remove Cr in the wastewater. The removal rates of sulfate and Cr(VI) were dependent on the consumption rate of organic materials in the wastewater. The stoichiometric studies also showed that about 63% of electrons from oxidation of organic materials were used to reduce sulfate. When the electrons of sulfide oxidation to elemental sulfur was at least 1.3 times higher than that of Cr(VI) reduction to Cr(III), Cr(VI) was completely removed. This result suggests that Cr(VI) reduction can be expected to take place under sulfate-rich anaerobic conditions, and sulfide produced by sulfate reducing bacteria could be used to immobilize soluble chromium through Cr(VI) reduction.     

对氨基苯甲醚废水处理

对氨基苯甲醚生产中排放的废水经物化前处理后,利用二氧化氯为氧化剂,在自制催化剂存在的条件下将废水中的有机物氧化分解,使CODCR去除率≥70％,色度去除率≥85％,硝基苯去除率≥85％,挥发酚去除率≥80％,氧化处理后再进行生化处理,该废水可以达标排放。     

Reduction of greenhouse gases from anaerobic piggery wastewater treatment by bromochloromethane in Taiwan

This work establishes methods of reducing the amount of methane produced from the anaerobic treatment of piggery wastewater by either reducing the storage time before solid/liquid separation or inhibiting the activity of methanogens in anaerobic wastewater treatment system. Experimental results showed these two methods can be adopted effectively to reduce methane production resulting from anaerobic piggery wastewater treatment. First, the wastewater must be processed using solid/liquid separation immediately after washing pig houses. This process can reduce by 62% the biogas production and indirectly decrease the methane production from the anaerobic wastewater treatment reactor. Second, adding 10 mg L(-1) bromochloromethane (BCM) daily into the anaerobic wastewater treatment reactor can significantly reduce the amount of biogas and methane produced during the anaerobic fermentation process. Furthermore, biogas production can be completely inhibited after 4 days. Adding BCM (< or =10 mg L(-1)) to wastewater only slightly affected the efficiency of the anaerobic wastewater treatment process. Results in this study can provide the basis for further research on reduction of the amount of methane produced from anaerobic wastewater treatments.     

铁炭微电解法处理拉开粉废水的研究

就铁炭微电解法处理拉开粉废水的工艺参数及其处理效果进行了试验研究 ,采用絮凝沉淀 酸化微电解 中和沉淀流程 ,拉开粉和CODCr的总去除率可分别达到 87.7%和 83.4 %。     

Reduction of Greenhouse Gases from Anaerobic Piggery Wastewater Treatment by Bromochloromethane in Taiwan

Abstract

This work establishes methods of reducing the amount of methane produced from the anaerobic treatment of piggery wastewater by either reducing the storage time before solid/liquid separation or inhibiting the activity of methanogens in anaerobic wastewater treatment system. Experimental results showed these two methods can be adopted effectively to reduce methane production resulting from anaerobic piggery wastewater treatment. First, the wastewater must be processed using solid/liquid separation immediately after washing pig houses. This process can reduce by 62% the biogas production and indirectly decrease the methane production from the anaerobic wastewater treatment reactor. Second, adding 10 mg L^?1 bromochloromethane (BCM) daily into the anaerobic wastewater treatment reactor can significantly reduce the amount of biogas and methane produced during the anaerobic fermentation process. Furthermore, biogas production can be completely inhibited after 4 days. Adding BCM (≤10 mg L^?1) to wastewater only slightly affected the efficiency of the anaerobic wastewater treatment process. Results in this study can provide the basis for further research on reduction of the amount of methane produced from anaerobic wastewater treatments.