浅谈电脑手机等电子废弃物的回收利用

电子废弃物中有大量的可再生资源,回收处理后可成为新的资源重新进入生产过程,这不仅能够提高资源的利用效率,缓解资源对经济发展的瓶颈制约,保护和改善生态环境,而且还可带来可观的经济效益。     

有机污染土壤修复表面活性剂淋洗液的回收处理方法

本文介绍了表面活性剂及其在有机污染土壤化学淋洗吸附技术中的应用,具体阐述了从表面活性剂淋洗废水中回收表面活性剂淋洗液的常用方法,并对主要方法进行了评价和比较,显示有机膨润土吸附法为经济有效的回收表面活性剂的方法,并简述了膨润土吸附表面活性剂的机理。     

间歇曝气生物滤池处理生活污水的试验研究

曝气生物滤池是一种新型的废水处理应用技术,集生物氧化、生物絮凝、过滤、反冲洗更新等功能于一体[1],非常适合我国目前水资源紧缺的现状。本文从运行方式方面通过间歇曝气考察分析了曝气生物滤池的污水处理效果,试验结果研究表明:不同的曝气时间和间歇时间对有机物、氨氮的去除效果和效率明显不同,选择合适的时间能够使去除效果达到最好。本文去除实验研究数据能够为以后生物过滤处理生活污水方面提供借鉴和支持。     

生物法处理海上油田含聚生产污水研究报告

应用"倍加清"特种微生物技术,结合"气浮+生化+固液分离"的处理工艺,以中海油绥中SZ36-1陆上终端含聚污水为水质样本,研究生物法处理海上油田含聚生产污水的效果。结果表明,该工艺处理后出水可达"1.5.2"的水质标准,远优于"10.10.3"的注入水质指标要求,并确定了相关技术参数。该技术具备处理效果好、适应来水水质范围大、环境友好等优势。但由于空间重量的限制,尚不适用于海上油田平台的生产水处理工艺。     

曝气强度对膜生物反应器处理石化废水工艺运行特征的影响

采用膜生物反应器(Membrane Bioreactor,MBR)处理石化废水,研究曝气强度分别为1.50,3.00 m3/(m2·h)的条件下,MBR对石化废水中主要污染物的去除特征、跨膜压差(Trans Membrane Pressure,TMP)和混合液性质的变化特征。结果表明:在两种曝气强度条件下MBR对COD、NH+4-N及挥发酚等污染物的平均去除率分别为80.74%、80.23%、96.79%和97.55%、99.34%、98.84%,即在不同曝气条件下,曝气强度的变化对MBR的污染物去除性能无显著影响。但随着曝气强度由1.50 m3/(m2·h)增加到3.00 m3/(m2·h),MBR达到设定的最大跨膜压差(TMPMax=25k Pa)的运行时间由11.8 d增加到31.4 d,TMP上升速率降低。通过活性污泥颗粒粒径分析发现:增加曝气强度后,对膜污染影响显著的活性污泥颗粒粒径范围(0~2μm)所占体积比由2.10%减小到1.78%;并且混合液中溶解性微生物产物(soluble microbial product,SMP)和胞外聚合物(extracellular polymeric substance,EPS)质量浓度分别由24.07 mg/L和15.66 mg/g减小到15.14 mg/L和9.81 mg/g,从而降低了膜污染速率。     

碱改性脱水污泥对水中镉的吸附效能研究

城市市政污水处理厂产生的剩余污泥是一种良好的重金属生物吸附剂制备原料。以北京某市政污水处理厂产生的脱水剩余污泥为原料,采用碱改性处理方法,制备得到碱改性脱水污泥生物吸附剂,通过其对水中镉的等温吸附实验,考察其重金属吸附效能。研究结果表明:碱改性脱水污泥对水中镉的等温吸附曲线符合Langmuir等温吸附模型。碱改性处理后,脱水污泥对水中镉的最大饱和吸附容量提高了2.8倍,达0.966 mmol/g,显著高于同类型脱水污泥生物吸附剂。碱改性脱水污泥对水中镉的最大饱和吸附容量与改性过程中所使用的Na OH浓度之间的线性相关性较差,呈现一定的波动变化趋势。     

MBR出水后置化学除磷研究

选用不同的化学除磷药剂及固液分离方式,针对膜生物反应器出水进行后置化学除磷静态试验研究。试验表明,在MBR出水平均浓度为(6.0±0.3)mg/L时,在化学药剂的最佳投药量和混凝时间的条件下,TP可以稳定达到一级A标准,去除率达到95%以上;滤液达一级A标准,氯化铝、氯化铁、聚合硫酸铁、硫酸铝最佳投加量为1.5 mol/mol,硫酸铁、聚合硫酸铝最佳投加量为3.0 mol/mol,最佳混凝时间均为10 min;滤纸和滤膜可以有效分离混凝混合液中的TP,滤液TP可稳定达一级A标准,而微网对混合液中粒径小于D10的颗粒无法分离,致使滤液TP无法达标;PAM投加后,絮体粒径显著增大,固液分离效果也相应增强。微网分离效果较投加前有了明显提高,滤液TP可稳定达到一级B标准。     

Biostability in distribution systems in one city in southern China：Characteristics, modeling and control strategy

This study investigated the bacterial regrowth in drinking water distribution systems receiving finished water from an advanced drinking water treatment plant in one city in southem China. Thirteen nodes in two water supply zones with different aged pipelines were selected to monitor water temperature, dissolved oxygen （DO）, chloramine residual, assimilable organic carbon （AOC）, and heterotrophic plate counts （HPC）. Regression and principal component analyses indicated that HPC had a strong correlation with chloramine residual. Based on Chick-Watson＇s Law and the Monod equation, biostability curves under different conditions were developed to achieve the goal of HPC 100 CFU/mL. The biostability curves could interpret the scenario under various AOC concentrations and predict the required chloramine residual concentration under the condition of high AOC level. The simulation was also carded out to predict the scenario with a stricter HPC goal （≤50 CFU/mL） and determine the required chloramine residual. The biological regrowth control strategy was assessed using biostability curve analysis. The results indicated that maintaining high chloramine residual concentration was the most practical way to achieve the goal of HPC ≤ 100 CFU/mL. Biostability curves could be a very useful tool for biostability control in distribution systems. This work could provide some new insights towards biostability control in real distribution systems.     

Comparison of quartz sand, anthracite, shale and biological ceramsite for adsorptive removal of phosphorus from aqueous solution

The choice of substrates with high phosphorus adsorption capacity is vital for sustainable phosphorus removal from waste water in constructed wetlands. In this study, four substrates were used： quartz sand, anthracite, shale and biological ceramsite. These substrate samples were characterized by X- ray diffractometry and scanning electron microscopy studies for their mineral components （chemical components） and surface characteristics. The dynamic experimental results revealed the following ranking order for total phosphorus （TP） removal efficiency： anthracite 〉 biological ceramsite 〉 shale 〉 quartz sand. The adsorptive removal capacities for TP using anthracite, biological ceramsite, shale and quartz sand were 85.87, 81.44, 59.65, and 55.98 mg/kg, respectively. Phosphorus desorption was also studied to analyze the substrates＇ adsorption efficiency in wastewater treatment as well as the substrates＇ ability to be reused for treatment. It was noted that the removal performance for the different forms of phosphorus was dependent on the nature of the substrate and the adsorption mechanism. A comparative analysis showed that the removal of particulate phosphorus was much easier using shale. Whereas anthracite had the highest soluble reactive phosphorus （SRP） adsorptive capacity, biological ceramsite had the highest dissolved organic phosphorus （DOP） removal capacity. Phosphorus removal by shale and biological ceramsite was mainly through chemical adsorption, precipitation or biological adsorption. On the other hand, phosphorus removal through physical adsorption （electrostatic attraction or ion exchange） was dominant in anthracite and quartz sand.     

Biosorption mechanisms involved in immobilization of soil Pb by Bacillus subtilis DBM in a multimetal-contaminated soil

Mechanisms of soil Pb immobilization by Bacillus subtilis DBM, a bacterial strain isolated from a heavy-metal-contaminated soil, were investigated. Adsorption and desorption experiments with living bacterial cells as well as dead cells revealed that both extracellular adsorption and intracellular accumulation were involved in the Pb2＋removal from the liquid phase. Of the sequestered Pb（II）, 8.5% was held by physical entrapment within the cell wall, 43.3% was held by ion-exchange, 9.7% was complexed with cell surface functional groups or precipitated on the cell surface, and 38.5% was intracellularly accumulated.Complexation of Pb2＋with carboxyl, hydroxyl, carbonyl, amido, and phosphate groups was demonstrated by Fourier transform infrared spectroscopic analysis. Precipitates of Pb5（PO4）3OH, Pb5（PO4）3Cl and Pb10（PO4）6（OH）2that formed on the cell surface during the biosorption process were identified by X-ray diffraction analysis. Transmission electron microscopy–energy dispersive spectroscopic analysis confirmed the presence of the Pb（II）precipitates and that Pb（II） could be sequestered both extracellularly and intracellularly.Incubation with B. subtilis DBM significantly decreased the amount of the weak-acid-soluble Pb fraction in a heavy-metal-contaminated soil, resulting in a reduction in Pb bioavailability, but increased the amount of its organic-matter-bound fraction by 71%. The ability of B.subtilis DBM to reduce the bioavailability of soil Pb makes it potentially useful for bacteria-assisted phytostabilization of multi-heavy-metal-contaminated soil.