三维电极电解硝基苯废水处理实验研究

以涂膜活性炭-活性炭为填充粒子,对三维电极电解硝基苯废水进行了研究。通过实验探讨了投盐量、槽电压、主电极间距、反应时间及初始浓度对电解硝基苯废水的影响。结果表明,三维电极在电极间距为9mm、槽电压为20V、硫酸钠投加量为1.5g/L、pH值为6、电解时间为90min的条件下,硝基苯去除率可达90%以上。在三维电极电解作用下,硝基苯转化为可生化和低毒的苯胺,苯胺在三维电极电解作用下还可以得到进一步的降解。     

零价铁活化过硫酸盐降解污水中萘普生的研究

为了提高零价铁(ZVI)活化过硫酸盐(PS)的ZVI/PS体系对有机污染物萘普生(NAP)处理的技术水平,即实现对污水中NAP的有效降解.采用对比试验,通过设置不同投加量的PS与ZVI的方式,观察在不同酸碱度条件下NAP的降解量.研究结果表明,酸性条件下,当PS投加量为0.5mM或ZVI投加量为1.50mM时,NAP的...     

吸附-双催化氧化降解苯胺、硝基苯废水

苯胺、硝基苯废水利用吸附树脂吸附后,再利用过氧化氢作氧化剂,在亚铁离子和紫外光的双催化下氧化降解。通过对亚铁离子浓度、过氧化氢浓度等因素对光降解影响的考察,结果表明,在实验条件下,本氧化体系对苯胺、硝基苯废水有明显的降解效果,苯胺、硝基苯废水经该体系处理12h后,去除率最高分别达到99.7%和95.3%。     

利用缺氧反硝化处理难降解有机物的探讨

本文研究了厌氧、缺氧实验夺件下难降解苯、甲苯、乙苯、二甲苯的同分异构体（BTEX）的生物降解性能。得出了不同底物的厌氧降解变化情况和缺氧降解条件下不同底物适宜的C／N比。通过对实验结果的分析，初步确定了不同底物具有各不相同的C／N比的原因，同时得出了缺氧反硝化与厌氧生物降解过程有可能同时发生的结论。     

垃圾场渗出污水厌氧处理的可行性研究

采用血清瓶静态试验法研究了垃圾渗出污水的厌氧处理的可行性。试验表明:垃圾渗出污水对厌氧发酵微生物无抑制作用,有良好的厌氧降解性,产气率为0.321/g·COD,污水中的大部份有机物都能被厌氧消化,COD_cr去除率为78.2%,发酵过程中还能获得能源——沼气。具有良好的应用前景。     

微生物对石油烃类的降解机理

文章分析了生物降解需要的条件、环境因素对石油烃微生物降解的影响,石油烃类的有氧降解机理、有氧降解方式,石油烃类的厌氧降解机理、厌氧降解过程中某些无机含氧化合物作受氢体的递氢过程,石油烃类化合物微生物降解难易程度,提出了以后应进一步重视原油的生物降解应用于我国微生物采油的研究。     

偶氮染料的厌氧——好氧生物降解过程和影响因素

偶氮染料是总量最大、种类最多的合成染料,其降解处理通常采用厌氧-好氧技术。厌氧过程可实现偶氮染料的还原,好氧过程则完成还原产物芳香胺的去除。厌氧过程受偶氮染料结构和浓度、底物的种类和浓度、其他电子受体、氧化还原介体、温度和DO等环境因素以及水力停留时间的影响。好氧条件下芳香胺的降解过程受其自身的结构、浓度、外加碳源以及降解体系等影响,且自氧化过程影响了芳香胺的生物降解。在实际废水处理中应创造良好的条件提高偶氮染料的厌氧一好氧生物降解效率。     

PAM投加量对臭氧氧化厌氧消化耦合工艺污泥脱水性的影响

提高污泥的脱水性是降低污泥处理难度的必要前提.本文以传统厌氧消化工艺为参照,研究臭氧氧化厌氧消化耦合工艺对化学一级强化污泥脱水挂的影响,以及PAM投加量对厌氧消化污泥脱水性的影响.结果表明,与浓缩污泥相比,传统厌氧消化后污泥脱水性下降了11.8％,而臭氧氧化厌氧消化耦合工艺中污泥没有变化;随着PAM投加量的增加,污泥的脱水性能显著提高;当PAM梗加量为2.0 mg/g DS时,臭氧氧化厌氧消化耦合工艺中污泥的脱水性能达到最佳状态,而当PAM投加量为2.5 mg/g DS时,厌氧消化工艺中污泥的脱水性能才达到最佳状态.     

Fenton试剂-超声波降解硝基苯产物的分析

用Fenton试剂—超声波振荡法对硝基苯水溶液进行降解处理,采用气相色谱-质谱联用法分析降解的中间产物,用离子色谱法分析降解的最终产物。实验结果表明：硝基苯降解中间产物中含有间二硝基苯,邻、间、对硝基苯酚及苯酚;降解的最终产物主要为硝酸根,本文同时研究了中间产物在降解过程中浓度的变化规律。     

碱度对UASB处理淀粉废水影响的研究

通过UASB中试装置对淀粉废水处理工艺中不同碱度对UASB反应器中的碱度和酸化的影响的研究,论述了减少碱度投加的途径和酸化的预防与系统恢复.补充碱度可以防止酸化,使反应器处于良好运行状况.通过控制运行条件可以有效降低厌氧处理中碱度需求,在最大程度上降低厌氧处理运行费用.阐述了日常监测的方法,以及预防酸化的产生的途径.     

含硝基苯、苯胺废水处理的工程实践

采用固定化微生物-曝气生物滤池与铁-炭微电解法联用的工艺方法处理含硝基苯、苯胺的废水。通过培养驯化微生物阶段、半负荷进水阶段、满负荷进水阶段的调试运行,表明:当进水CODCr<1 000mg/L、硝基苯<120mg/L、苯胺<30mg/L时,出水可达到CODCr<300mg/L、硝基苯<5mg/L、苯胺<5mg/L的设计要求。铁-炭微电解法在pH值为3～4时,对废水有一定的脱色作用,但pH值升高后脱色效果不明显。     

Transport and fate modeling of nitrobenzene in groundwater after the Songhua River pollution accident

In 2005 a pollution accident occurred in the Songhua River, which is geographically located next to groundwater supply plants. This caused public concern about the transport and fate of nitrobenzene (NB) in the groundwater. This paper discusses the mechanisms and effects of the transport and fate of NB in groundwater based on pilot scale experiments conducted in the laboratory, including a simulation experiment, bench-scale batch tests and a one-dimensional numerical model. Parallel batch tests showed that the adsorption of NB to the clay and sand followed the Langmuir-type isotherm, and clay had a greater NB adsorption capacity than sand. NB biodegradation in different conditions was well fitted by the Monod equation and the q_max values varied from 0.018 to 0.046 h^?1. Results indicated that NB’s biodegradation was not affected by the initial NB concentration. Numerical modeling results indicated a good match between computed and observed data, and in the prediction model NB entered the groundwater after the pollution accident. However, the highest concentration of NB was much lower than the allowable limit set by the national standard (0.017 mg/L).     

Low-temperature chromium(VI) biotransformation in soil with varying electron acceptors

Effective and low-cost strategies for remediating chromium (Cr)-contaminated soil are needed. Chromium(VI) leaching from contaminated soil into ground water and surface water threatens water supplies and the environment. This study tested indigenous Cr(VI) microbial transformation in batch systems at 10 degrees C in the presence of various electron acceptors. The effects of carbon addition, spiked Cr(VI), and mixing highly contaminated soil with less contaminated soil were investigated. The results indicated that Cr(VI) can be biotransformed in the presence of different electron acceptors including oxygen, nitrate, sulfate, and iron. Sugar addition had the greatest effect on enhancing Cr(VI) removal. Less dissolved organic carbon (DOC) was consumed per amount of Cr(VI) transformed under anaerobic conditions [0.8-93 mg DOC/mg Cr(VI)] compared with aerobic conditions [1.4-265 mg DOC/mg Cr(VI)]. Toxicity of high concentrations (< 160 mg/L) of spiked Cr(VI) were not evident. At Cr(VI) concentrations > 40 mg/L, aerobic conditions promoted faster Cr(VI) reduction than anaerobic conditions with nitrate or sulfate present. Biotransformation of Cr(VI) in highly contaminated soil (22,000 mg Cr/kg) was facilitated by mixing with less-contaminated soil. The study results provide a framework for evaluating indigenous Cr(VI) microbial transformation and enhance the ability to develop strategies for soil treatment.     

Fenton试剂处理六氯苯废水的试验研究

研究了采用Fenton法处理六氯苯模拟废水的方法以及Fenton法处理六氯苯的影响因素。研究结果显示:在H2O2(30%)投加量为500mg/L,Fe2 投加量为1000mg/L,pH=2.5的条件下,经过4h的反应,废水中HCB去除率可达51.65%。     

硫酸盐生物还原的限制性生态因子的影响研究

利用厌氧颗粒污泥对烟气中SO2吸收生成的硫酸盐或亚硫酸盐废水进行处理，考察起始SO4^2-质量浓度、初始COD／SO4^2-、初始pH、接种污泥质量、亚铁离子等限制性生态因子对硫酸盐还原的影响。结果表明：在起始SO4^2-质量浓度800mg／L，初始COD／SO4^2-为3．0，pH值为7．0，接种污泥质量为31．10gVSS／L，添加亚铁离子的条件下，进行半连续试验，硫酸根去除率可迭70％。表明在COD／SO4^2-较低的条件下，各生态因子综合作用下，硫酸盐还原可得较好效果。     

重金属对海岸带沉积物中菊酯生物降解的影响

通过考察Cu2+、Cd2+对渤海海岸带沉积物中甲氰菊酯、氯氰菊酯和溴氰菊酯的缺氧生物降解的影响,发现:外加Cu2+和Cd2+均对渤海海岸带沉积物中甲氰菊酯、氯氰菊酯和溴氰菊酯的缺氧生物降解有抑制作用,且随着外加金属离子浓度的增大,抑制作用更为明显。与Cu2+相比较,Cd2+对渤海沉积物中拟除虫菊酯缺氧生物降解的抑制作用更大,这跟Cu、Cd在渤海海岸带沉积物中的存在形态和对生物的毒性不同有密切的关系。     

绿色阻垢剂聚天冬氨酸的制备与性能研究

采用马来酸酐与氨水进行溶液聚合的方法制备聚天冬氨酸,利用静态阻垢法评价了聚天冬氨酸的阻垢性能。结果表明:聚天冬氨酸对ρ(Ca2+)=300mg/L,ρ(HCO3-)=300mg/L的水样阻垢率可以达到90%以上;在ρ(HCO3-)低于400mg/L时,药剂的阻垢率可达到100%;当ρ(HCO3-)大于400mg/L后,药剂阻垢性能降低明显。聚天冬氨酸具有良好的生物降解性,生物降解率可以达到70%。     

Phosphorus sorption characteristics of estuarine sediments under different redox conditions

Phosphorus (P) plays a major role in eutrophication of aquatic systems. Estuarine sediments could function as sources or sinks for P to the overlying water column depending upon their physico-chemical characteristics. Understanding of P sorption phenomena in estuarine sediments is important in regulating the P availability in estuaries. Phosphorus sorption characteristics of sediments from the Indian River Lagoon, Florida, USA, were determined to examine the role of selected physico-chemical properties of the sediments on soluble reactive P status in estuary water. Mean equilibrium P concentrations (EPCo) of 0.75 mg L(-1) and mean P sorption maxima (Smax) of 32.2 mg kg(-1) were obtained under anaerobic conditions, compared with EPCo of 0.05 mg L(-1) and Smax of 132.7 mg kg(-1) under aerobic conditions. The higher EPCo values under anaerobic conditions and the greater Smax values under aerobic conditions were associated with amorphous and poorly crystalline iron. These results suggest that sediments enriched with amorphous and poorly crystalline forms of iron act as an excellent reservoir for P by adsorbing excessive P in aerobic sediment zones and releasing it upon burial under anaerobic conditions. This study also indicates that P compounds in sediments independently maintain equilibrium with P in solutions. Thus, heterogeneous systems like soil and sediment simply behave as a mixture of homogeneous surfaces as far as their P sorption characteristics are concerned, and hence can be successfully described by the Langmuir and Freundlich models.     

A laboratory study on risk assessment of microcystin-RR in cropland

The persistence time and risk of microcystin-RR (MC-RR) in cropland via irrigation were investigated under laboratory conditions. In order to evaluate the efficiency of the potential adsorption and biodegradation of MC-RR in cropland and the persistence time of MC-RR for crop irrigation, high performance liquid chromatography (HPLC) was used to quantify the amount of MC-RR in solutions. Our study indicated that MC-RR could be adsorbed and biodegraded in cropland soils. MC-RR at 6.5mg/L could be completely degraded within 6 days with a lag phase of 1-2 days. In the presence of humic acid, the same amount of MC-RR could be degraded within 4 days without a lag phase. Accordingly, the persistence time of MC-RR in cropland soils should be about 6 days. This result also suggested the beneficial effects of the organic fertilizer utilization for the biodegradation of MC-RR in cropland soils. Our studies also demonstrated that MC-RR at low concentration (<10microg/L) could accelerate the growth of plants, while high concentration of MC-RR (>100microg/L) significantly inhibited the growth of plants. High sensitivity of the sprouting stage plants to MC-RR treatments as well as the strong inhibitory effects resulting from prolonged irrigation further indicated that this MC-RR growth-inhibition may vary with the duration of irrigation and life stage of the plants.