竹丝生物膜反应器修复校园景观水体的实验研究

以竹丝作为填料而组建的接触氧化生物膜工艺对校园景观水体进行易位修复,通过设置5个不同工况以探明竹丝载体在修复轻度污染水体的特性,研究表明:当进水CODMn、氨氮和浊度分别为7.79~24.32 mg/L、1.36~11 mg/L和0.63~33.11 NTU的情况下,其去除率分别为10.57%~74.34%、-83.33%~57.55%和20.01%~100%,不同的运行工况对修复效果的影响不显著;系统在启动后的8 d内即可形成丰富成熟的生物相,而且竹丝上的细菌主要以短杆菌为主;竹丝生物膜反应器修复后的景观水体中的活细菌数量可减少1个数量级。竹丝上的亲水性基团和良好的生物亲和性以及从竹丝上脱落下来的零散竹丝纤维是竹丝填料生物膜快速形成的基础,宏观和微观"网捕"结构是该系统能在极短时间实现高效去除浊度、有机物和细菌等高分子物质的主要原因。     

综合法处理酸性高浓度印染废水的研究

传统Fenton法在处理印染类废水时,因亚铁盐及双氧水的昂贵价格而限制了其实际应用。出于工程应用的考虑,提出了以Fenton法为重心,结合其他污水处理方法的综合方法,从而在达到相同处理效果的同时尽可能降低治污成本。研究表明,通过Fenton、铁碳微电解和中和沉淀吸附等方法的综合运用和优化组合,废水色度降至10倍以下,COD降至300 mg/L以下,去除率达到98%以上,pH调节为7,达到排放标准。     

中国能源效率与其影响因素的动态关系研究

本文利用1978-2006年样本数据,首先通过状态空间模型分析了经济结构、技术进步、能源消费结构和能源价格对能源效率的单向动态变化过程及成因;接着使用向量误差修正模型估算出能源效率与其影响因素之间的长期均衡和短期波动关系;在此基础上利用脉冲响应函数和方差分解模型就我国能源效率与其影响因素之间的动态关系作进一步分析。结果表明:改革开放以来我国能源效率与其影响因素之间存在长期均衡关系,经济体制改革和一些相关政策对能源效率有着深远的影响。从长期均衡关系来看,技术进步对能源效率的正面影响最大,能源价格和一些不可观测变量对能源效率有着促进作用,而经济结构和能源消费结构未能对能源效率起推动作用。从各因素对能源效率的贡献百分比来看,能源价格对能源效率的贡献最大,然后依次是经济结构、能源消费结构和技术进步。     

Ca5（AsO4）3OH的溶解度与稳定性研究

通过在不同pH值,温度等条件下Ca5（AsO4）3OH的溶解,确定其稳定存在的pH值范围,得出它的溶度积和生成的自由能（ΔG0f）。结果表明,Ca5（AsO4）3OH在水中的溶解度和稳定范围与pH和温度有关,在酸性条件下（初始pH=2）它的溶解度较大,而且在水中的溶解度随着温度的升高而降低。利用PHREEQC程序计算确定Ca5（AsO4）3OH的溶度积为10-40.86,生成自由能ΔG0f为-5 063.53 kJ/mol。利用JADE5软件计算得到其晶格参数a=b=9.696,c=6.967和晶胞体积为567.304 3。     

Lactate oxidation in pyrite suspension: a Fenton-like process in situ generating H2O2

Pyrite is a common mineral at many mining sites. In this study, the mineral pyrite was studied as a Fenton-like reagent for environmental concerns. We selected lactate as a model target molecule to evaluate the Fenton-like catalytic efficiency of pyrite upon organic oxidation. A complete set of control experiments in both aerobic and anaerobic atmospheres unequivocally established that the pyrite in aqueous solution could spontaneously in situ generate OH and H₂O₂, serving as a Fenton-like reagent to catalyze the oxidation of lactate to pyruvate with no need for additional H₂O₂. We called it the pyrite-only Fenton-like (PF) reagent. Monitoring concentration changes of lactate and pyruvate with the time indicated that the pyrite mediated the favorable pyruvate formation at pH 4.5, 60 °C, under air atmosphere. The PF reaction could be stimulated by visible light illumination. Under the optimum conditions, up to 50% of lactate was degraded within 10 d. The results suggest that pyrite and its Fenton-like processes may be potentially practical in wastewater treatment.     

零价铁修复受三氯乙烯污染地下水的实验研究

通过批实验和柱实验研究了三氯乙烯（TCE）初始浓度、四氯乙烯(PCE)等对零价铁去除三氯乙烯的影响,并建立了三氯乙烯降解的反应动力学方程。结果表明：（1）零价铁对TCE具有较好的降解效果,反应符合准一级反应动力学方程,表观反应速率常数随TCE浓度的增加而减小;（2）在铁粉充足的条件下,TCE初始浓度对降解效果影响不显著,且TCE去除率皆可达到90%以上;（3）PCE的存在抑制了TCE的脱氯反应。PCE和TCE共存时,TCE的最大去除率仅为64.2%;TCE脱氯反应的表观反应速率明显降低,反应半衰期由TCE单独存在时的6.8～9.7 h增大到66 h～346.5 h。     

Citrobacter sp.CK3对活性红KN-3B的脱色反应动力学研究

采用脱色菌Citrobacter sp. CK3,以活性红KN-3B染料为处理对象,在厌氧批式反应条件下,系统考察了pH值,温度和染料浓度对脱色反应速度的影响;通过动力学模拟及反应过程中染料的UV-Vis扫描图分析,探讨了脱色反应机理。结果表明:Citrobacter sp. CK3对活性红KN-3B的脱色反应的适宜pH为7～9;脱色反应速度在温度为32℃时达到最大。染料初浓度从57 mg/L逐渐增大到458 mg/L时脱色率逐渐降低。脱色过程中染料的偶氮键发生断裂,脱色反应符合二级反应动力学。     

Growth, photosynthesis and antioxidant responses of two microalgal species, Chlorella vulgaris and Selenastrum capricornutum, to nonylphenol stress

The effect of nonylphenol (NP) on growth, photochemistry and biochemistry of two green microalgae, Chlorella vulgaris and Selenanstrum capricornutum, and their ability to degrade NP were compared. The 96 h EC₅₀ of C. vulgaris and S. capricornutum were greater than 4.0 and 1.0 mg L⁻¹ NP, respectively, suggesting that the former species was more tolerant to NP. Both microalgae acclimated to NP stress through down-regulating their photosynthetic activities, including antenna size (chlorophyll a content), maximal photochemistry (Fv/Fm) and the light absorbed by PSII (ABS/CS₀), but the dissipation of energy from reaction centres (DI₀/RC) increased with the increase of NP concentrations. In C. vulgaris, the changes of these parameters were more significant than in S. capricornutum and recovered completely after a 96 h exposure. The antioxidant responses, such as GSH content, CAT and POD activities in C. vulgaris increased with the increase of NP concentrations after a 24 h exposure, but these changes disappeared with exposure time and recovered to the control levels after 96 h. In S. capricornutum, although GSH content, CAT and POD activities also increased when exposed to low- to moderate-NP concentrations, these values were significantly reduced at a high concentration (4 mg L⁻¹) even after a 96 h exposure, indicating its antioxidant responses were significantly delayed. It is clear that the more NP-tolerant species, C. vulgaris, acclimated better with a faster recovery of its photosynthetic activity from the NP-induced damage, and exhibited more efficient and rapid responses to NP-induced oxidative stress. C. vulgaris also had a higher NP degradation ability than S. capricornutum.     

Selective redox degradation of chlorinated aliphatic compounds by Fenton reaction in pyrite suspension

Selective redox degradation of chlorinated aliphatics by Fenton reaction in pyrite suspension was investigated in a closed system. Carbon tetrachloride (CT) was used as a representative target of perchlorinated alkanes and trichloroethylene (TCE) was used as one of highly chlorinated alkenes. Degradation of CT in Fenton reaction was significantly enhanced by pyrite used as an iron source instead of soluble Fe. Pyrite Fenton showed 93% of CT removal in 140 min, while Fenton reaction with soluble Fe(II) showed 52% and that with Fe(III) 15%. Addition of 2-propanol to the pyrite Fenton system significantly inhibited degradation of TCE (99% to 44% of TCE removal), while degradation of CT was slightly improved by the 2-propanol addition (80-91% of CT removal). The result suggests that, unlike oxidative degradation of TCE by hydroxyl radical in pyrite Fenton system, an oxidation by the hydroxyl radical is not a main degradation mechanism for the degradation of CT in pyrite Fenton system but a reductive dechlorination by superoxide can rather be the one for the CT degradation. The degradation kinetics of CT in the pyrite Fenton system was decelerated (0.13-0.03 min⁻¹), as initial suspension pH decreased from 3 to 2. The formation of superoxide during the CT degradation in the pyrite Fenton system was observed by electron spin resonance spectroscopy. The formation at initial pH 3 was greater than that at initial pH 2, which supported that superoxide was a main reductant for degradation of CT in the pyrite Fenton system.