厌氧氨氧化菌的培养与推流式反应器氨厌氧工艺

采用推流式固定化絮体生物反应器培养出高活性的厌氧氨氧化(ANAMMOX)红色颗粒污泥.在稳定运行后,反应器的NH₄⁺-N和NO₂^--N去除率皆大于98%,TN平均去除率为86%,NO₃^--N的生成率约为14%,TN去除负荷达2.56kg/(m³·d).同时考察了进水基质比例对反应器性能的影响,并用扫描电镜观察了颗粒结构.     

粪便与厨余垃圾现场处理研究

研究了粪便与厨余垃圾的源头真空管道收集及现场生物处理技术,根据系统工艺设计方案进行了分单元的小试.研究表明:真空便器的冲水量约为1L/次,破碎1kg垃圾用水0.4～0.6L;厌氧消化反应器进料粪便占40%,厨余垃圾占60%,水分控制在93%左右,C/N=25∶1左右,pH控制在6.2～7.3之间,最佳搅拌频率为6h/d,总停留时间28d;ABR反应器对混合上清液的COD去除率可达91%;用驯化得到的解磷、解钾菌株与消化污泥混合制取菌肥,解磷菌对土壤有效磷增强度67.5%,解钾菌对土壤有效钾增强度33.4%.     

光催化反应器的研究进展

介绍了国内外近年来有关多相光催化反应中光催化反应器设计与研究的进展情况,按催化剂在反应中存在的形式分类论述了各种反应器的结构原理和主要特点,以及光反应器设计中存在的问题和今后的研究方向。     

电助光催化氧化反应器的类型和设计要点

电助光催化反应器提供了通过外加电场提高光催化技术处理效率的场所,其构型是决定电助光催化反应效率和进行机理研究的关键要素。本文对当前电助光催化研究中采用的反应器的类型进行了综述,并提出电助光催化反应器设计的一些要点。     

全程自养脱氮新技术处理污泥脱水液的研究

以含有高浓度氨氮的消化污泥脱泥污水为基质,在悬浮填料床反应器中实现了稳定的全程自养脱氮过程.在填料表面培养形成了全程自养脱氮混菌生物膜.反应器的主控条件为T=28℃,pH=8.0左右,溶氧为0.8～1.0 mg/L.两级串联反应器的平均表面负荷为NH₄⁺-N 3～4 g/(m²·d),总的全程自养脱氮率达70%左右.对处理高氨氮含量和低C/N比的废水,全程自养脱氮较常规硝化-反硝化脱氮技术可大大降低氧耗并无需外加有机碳源,因此具有很好的应用前景.     

MATLAB在脱硫反应器设计中的应用

介绍了强大的数值分析软件ＭＡＴＬＡＢ在脱硫反应器设计中的应用。通过计算反应器内部静态电场,比较了线板式、线筒式、线线式反应器中的电场分布,从而可以选择较优的反应器结构。     

核能发电的特点及前景预测

核能发电具有经济、环保、安全的特点,发展和推广核电既能确保能源的可持续发展,也能满足环境保护的需要。近年来,核电发展取得了一定成绩,但其热污染和放射污染问题仍需引起重视并采取相关的措施。     

低浓度下冲击负荷对厌氧折流板反应器的影响

采用一个9.9L的厌氧折流板反应器处理低浓度废水(500mgCOD/L左右),研究了有机冲击负荷、水力冲击负荷对反应器运行性能的影响。结果表明,ABR具有极好的抗冲击负荷的能力,在350%的水力冲击负荷、持续时间2.5h下仅需4h即可恢复原状。ABR受有机冲击负荷的影响较复杂,在50%和100%浓度的有机冲击负荷下,反应器约经8h恢复原来的水平。在低浓度废水的定义范围之内(COD<1000mg/L),进水COD浓度突然上升等有机冲击负荷不会损害ABR反应器的处理性能,相反可有一定的改善作用。ABR反应器的多隔室结构使之存在缓冲区等分区现象,从而提供了良好的抗冲击负荷的能力。     

Decolorization of triphenylmethane dye-bath effluent in an integrated two-stage anaerobic reactor

In the present study, decolorization of a simulated dye waste containing three different triphenylmethane (TPM) dyes--Magenta, Malachite Green and Crystal Violet, was investigated in a laboratory scale, two-stage anaerobic high-rate reactor. The effect of various parameters (influent dye concentration, hydraulic and co-substrate loading rates) on color and COD removal efficiency of the reactor has been studied. It has been shown that the influent dye concentration had little effect on overall COD and color removal efficiency. More than 99% color removal and 96% COD removal efficiency were maintained even at a dye concentration of 500 mg/l and a dye loading rate of 1000 mg/l day. However, a minimum level of glucose as supplementary carbon source is required to maintain the maximum color removal efficiency and it drops appreciably when no glucose is added to the influent. The study also showed that the acidogenic phase of the reaction plays an important role in decolorization of the TPM dyes. In addition, the two-stage anaerobic reactor was observed to have distinct advantages over the single-stage system, as the drop in color and COD removal efficiency of stage 1 are adequately compensated by stage 2 of the reactor especially under high dye loading rates accompanied by low co-substrate loading and under reduced HRTs.     

Some properties of a granular activated carbon-sequencing batch reactor (GAC-SBR) system for treatment of textile wastewater containing direct dyes

Resting (living) bio-sludge from a domestic wastewater treatment plant was used as an adsorbent of both direct dyes and organic matter in a sequencing batch reactor (SBR) system. The dye adsorption capacity of the bio-sludge was not increased by acclimatization with direct dyes. The adsorption of Direct Red 23 and Direct Blue 201 onto the bio-sludge was almost the same. The resting bio-sludge showed higher adsorption capacity than the autoclaved bio-sludge. The resting bio-sludge that was acclimatized with synthetic textile wastewater (STWW) without direct dyes showed the highest Direct Blue 201, COD, and BOD(5) removal capacities of 16.1+/-0.4, 453+/-7, and 293+/-9 mg/g of bio-sludge, respectively. After reuse, the dye adsorption ability of deteriorated bio-sludge was recovered by washing with 0.1% sodium dodecyl sulfate (SDS) solution. The direct dyes in the STWW were also easily removed by a GAC-SBR system. The dye removal efficiencies were higher than 80%, even when the system was operated under a high organic loading of 0.36kgBOD(5)/m(3)-d. The GAC-SBR system, however, showed a low direct dye removal efficiency of only 57+/-2.1% with raw textile wastewater (TWW) even though the system was operated with an organic loading of only 0.083kgBOD(5)/m(3)-d. The dyes, COD, BOD(5), and total kjeldalh nitrogen removal efficiencies increased up to 76.0+/-2.8%, 86.2+/-0.5%, 84.2+/-0.7%, and 68.2+/-2.1%, respectively, when 0.89 g/L glucose (organic loading of 0.17kgBOD(5)/m(3)-d) was supplemented into the TWW.