渤南低渗透油田污水生化处理室内模拟研究

渤南油田属典型的低渗透油田,注水水质要求达到A1级,而污水中的分散油和乳化油是污水处理的难点和重点。为给污水站的建设提供合适的污水处理工艺单元和最佳参数,通过室内模拟研究,采用生物接触氧化技术处理油田污水。结果表明,当污水停留时间为8 h时,生化系统可将污水含油量由10～25 mg/L降低到1 mg/L以下,去除率高达96.18%,COD稳定在100 mg/L以内,通过生物之间的竞争作用和高浓度的氧,有效地抑制了硫酸盐还原菌的生长,使腐蚀率控制在0.076 mm/a以下。同时,该试验表明,8 h为生物接触氧化处理工艺的最佳停留时间。     

T型氧化沟提高脱氮效率的技术改造

采用延长边沟闷曝时间的方法对BOD降解模式T型氧化沟进行提高脱氮效率的改造。结果表明,边沟闷曝时间由0.5 h增至1 h,系统反硝化和硝化运行时间比t_DN/t_N由0.56调整至0.50时,提高了系统的NH₃-N的硝化效率,强化了脱氮能力。工艺改造后出水NH3-N浓度由改造前15.5 mg/L显著降低至10.4 mg/L,达到了广东省地方标准（DB 44/26-2001）第一时段的二级排放要求;系统脱氮效率由改造前52.1%显著提高到68.3％,有效地解决了污水厂出水NH₃-N浓度过高的问题;具有投资少、效果明显的特点,有一定的推广价值。     

煤低温氧化热解的热分析实验研究

在热分析动力学的基础上,对阳泉煤样运用同步热分析仪进行150℃下的氧化以及热解实验,得出该煤样相应的TG-DSC曲线。通过两者的TG-DSC曲线,对比分析煤样的热量释放情况,并结合曲线设定多项式形式的机理函数以分析其动力学特性。实验研究得出:该煤的低温氧化过程较之热解过程是个明显的氧化放热过程;该煤低温氧化和热解过程的最佳机理函数都为多项式,并且相应过程中的TG曲线和DSC曲线适用于同一个机理函数,这与一般所定义的机理函数不同;热解过程较之氧化过程所需的表观活化能较大,相同条件下较易发生煤的氧化自燃。     

Renewable Resources and Economic Sustainability: A Dynamic Analysis with Heterogeneous Time Preferences

In recent years there has been increasing interest in the study of economic sustainability and its relationship with natural resources. This paper attempts to shed some light on the issue by taking into account the individual variations in time preferences for consumption and resource amenity. We characterize the long-run steady state, analyze its asymptotic stability, and explore the transational dynamics from any initial state. The welfare implications of the optimal path are also discussed.     

Effect of Sb dopant amount on the structure and electrocatalytic capability of Ti/Sb-SnO2 electrodes in the oxidation of 4-chlorophenol

Ti/Sb-SnO_2 anodes were prepared by thermal decomposition to examine the influence',of the amount of Sb dopant on the structure and electrocatalytic capability of the electrodes in the oxidation of 4-chlorophenol.The physicochemical properties of the Sb-SnO_2 coating were markedly influenced by different amounts of Sb dopant.The electrodes,which contained 5% Sb dopant in the coating, presented a much more homogenous surface and much smaller mud-cracks,compared with Ti/Sb-SnO_2 electrodes containing 10% or 15% Sb dopant,which exibited larger mud cracks and pores on the surface.However,the main microstructure remained unchanged with the addition of the Sb dopant.No new crystal phase was observed by X-ray diffraction(XRD).The electrochemical oxidation of 4-chlorophenol on the Ti/SnO_2 electrode with 5% Sb dopant was inclined to electrochemical combustion;while for those containing more Sb dopant,intermediate species were accumulated.The electrodes with 5% Sb dopant showed the highest efficiency in the bulk electrolysis of 4-chlorophenol at a current density of 20 mA/cm~2 for 180 min;and the removal rates of 4-chlorophenol and COD were 51.0% and 48.9%,respectively.     

硫高温腐蚀及腐蚀产物氧化自燃性的研究

随着炼制原油硫含量的增加,炼油装置的硫腐蚀问题也日益严重.针对硫高温腐蚀状况,用差热-热重分析仪研究硫与Fe(OH)3、Fe2O3和Fe3O4发生硫化腐蚀反应的初始温度,并采用X射线衍射仪鉴定了360 ℃高温无氧条件下硫化腐蚀产物的组成.结果表明,硫与Fe(OH)3、Fe2O3和Fe3O4发生硫化反应的初始温度分别为287.67 ℃、233.34℃和308.47 ℃;高温硫化腐蚀产物主要是FeS2.对硫化产物FeS2进行氧化反应,氧化升温曲线和耗氧曲线表明,硫化腐蚀产物FeS2具有很高的氧化自燃性,在一定条件下能引发油品火灾和爆炸等事故.     

电化学法去除水中氯代有机化合物的研究进展

氯代有机化合物难降解、环境危害性极大,对氯代有机化合物的污染进行治理已成为水污染控制的重要课题。介绍了直接电化学氧化法、间接电化学氧化法、直接电化学还原法和间接电化学还原法用于水中氯代有机化合物处理的机理、研究现状;总结了电化学法去除氯代有机化合物的影响因素,同时指出电化学法在实际应用中存在的问题,并展望了氯代有机化合物电化学处理技术的应用前景。     

Removal of o-nitrophenol from water by electrochemical degradation using a lead oxide/titanium modified electrode

This study examined o-nitrophenol removal from aqueous solutions by electrochemical oxidation employing a modified electrode. The modified electrode was produced by electrodepositing lead oxide onto a titanium substrate. Following electrochemical oxidation of o-nitrophenol-containing solutions, the remaining o-nitrophenol concentration and chemical oxygen demand (COD) values were determined. The optimum parameters were current density of 40 mA cm(-2), pH of 2.47, 60 min of electrolysis time, 4 g L(-1) NaCl electrolyte solution and temperature of 30 degrees C. Under these optimum conditions of electrochemical degradation using a lead oxide/titanium modified electrode complete removal of o-nitrophenol and COD was achieved.     

次氯酸钠催化氧化法处理十二碳硫醇恶臭污水

采用活性炭和次氯酸钠催化氧化处理含有十二碳硫醇的恶臭污水,进行了小试并取得了良好的效果。在活性炭作催化剂,反应温度为100℃,反映时间为2-3min的实验条件下,1mL1%(m/v)NaClO即可处理100mL污水,处理后的废水无色无臭,可直接排放。     

Quantification of potassium permanganate consumption and PCE oxidation in subsurface materials

A series of laboratory scale batch slurry experiments were conducted in order to establish a data set for oxidant demand by sandy and clayey subsurface materials as well as to identify the reaction kinetic rates of permanganate (MnO(4)(-)) consumption and PCE oxidation as a function of the MnO(4)(-) concentration. The laboratory experiments were carried out with 31 sandy and clayey subsurface sediments from 12 Danish sites. The results show that the consumption of MnO(4)(-) by reaction with the sediment, termed the natural oxidant demand (NOD), is the primary reaction with regards to quantification of MnO(4)(-) consumption. Dissolved PCE in concentrations up to 100 mg/l in the sediments investigated is not a significant factor in the total MnO(4)(-) consumption. Consumption of MnO(4)(-) increases with an increasing initial MnO(4)(-) concentration. The sediment type is also important as NOD is (generally) higher in clayey than in sandy sediments for a given MnO(4)(-) concentration. For the different sediment types the typical NOD values are 0.5-2 g MnO(4)(-)/kg dry weight (dw) for glacial meltwater sand, 1-8 g MnO(4)(-)/kg dw for sandy till and 5-20 g MnO(4)(-)/kg dw for clayey till. The long term consumption of MnO(4)(-) and oxidation of PCE can not be described with a single rate constant, as the total MnO(4)(-) reduction is comprised of several different reactions with individual rates. During the initial hours of reaction, first order kinetics can be applied, where the short term first order rate constants for consumption of MnO(4)(-) and oxidation of PCE are 0.05-0.5 h(-1) and 0.5-4.5 h(-1), respectively. The sediment does not act as an instantaneous sink for MnO(4)(-). The consumption of MnO(4)(-) by reaction with the reactive species in the sediment is the result of several parallel reactions, during which the reaction between the contaminant and MnO(4)(-) also takes place. Hence, application of low MnO(4)(-) concentrations can cause partly oxidation of PCE, as the oxidant demand of the sediment does not need to be met fully before PCE is oxidised.