一种新型的污水处理设备--拼装式反应器

拼装式反应器是一种采用栓接方式将经过防腐处理的钢板现场拼接的新型的污水处理设备.反应器的设计由反应器罐体结构设计、基础设计及配套产品的嵌接设计3个方面构成;拼装式反应器与成熟的污水处理技术(如UASB、水解工艺、SBR、BAF等)的结合提高了污水处理设备的技术含量.拼装式反应器已在猪场废水、食品加工废水、制药废水、啤酒废水及城市污水等废水处理工程中得到了成功应用.     

Study on the photocatalytic reduction of dichromate and photocatalytic oxidation of dichlorvos

In this paper, dichromate and dichlorvos are selected as the deputies of inorganic and organic pollutants, respectively, and TiO2/beads is used as a photocatalyst. The effects of various parameters, such as the amount of the photocatalyst, H2O2 concentration, metal ions, anions, pH value, and organic compounds on the photocatalytic reduction of dichromate and photocatalytic oxidation of dichlorvos are studied. From the studies, the differences of the parameters effect on the photocatalytic degradation of organic and inorganic pollutants are obtained. The results show that the optimum amount of the photocatalyst used is 6.0 g cm(-3) for the photocatalytic reactions. With the addition of a small amount of H2O2, the photocatalytic reduction of dichromate is inhibited while the photocatalytic oxidation of dichlorvos is accelerated. With the addition of trace amounts of Fe3+ or Cu2+, both the reactions are accelerated, and with the addition of Zn2+ and Na+, no obvious effects on the reactions are observed. Acidic solution is favorable for the photocatalytic reduction of dichromate; and acidic and alkaline solutions are favorable for the photocatalytic oxidation of dichlorvos. Adding SO4(2-), the photocatalytic oxidation is accelerated and adding Cl- the reaction is inhibited; and with the addition of trace amounts of SO4(2-), Cl- and NO3-, no obvious effects on the photocatalytic reduction of dichromate are observed. With the addition of methanol and toluene, the photocatalytic reduction of dichromate is accelerated, and the photocatalytic oxidation of dichlorvos is inhibited. The possible roles of the additives on the reactions are also discussed.     

Interactions between arbuscular mycorrhizae and heavy metals under sand culture experiment

A sand culture experiment was established to determine interactions between arbuscular mycorrhizae and heavy metals. Mycorrhizal infection rates, spore densities, maize root and shoot weights, and heavy metal contents in maize were as indexes of responses of arbuscular mycorrhizal fungi (Acaulospora laevis, Glomus caledonium and Glomus manihotis) to heavy metals (Cu and Cd). The mycorrhizal infection rates of G. caledonium were the highest among these three mycorrhizal fungi, but the sporulating ability of G. caledonium was the poorest in the heavy metal treatments. The shoot and root weights of non-mycorrhizal plants were usually greater than those of mycorrhizal plants when the Cu concentrations in solutions are less than 3 mg l(-1) or Cd concentrations less than 1 mg l(-1). When Cd concentrations were 0.5 and 1 mg(-1), the root and shoot weights of plants inoculated with A. laevis were significantly (p < 0.05) lower than those of other treatments. Copper concentrations in shoots of mycorrhizal plants were higher than those of non-mycorrhizal ones at all Cu concentrations in solution, especially at low Cu concentrations. As to A. laevis, Cu concentrations in roots and shoots of the host were higher than those of non-mycorrhizal plants in these treatments. Thus A. laevis was sensitive to Cu and Cd, especially Cd, and G. caledonium was more tolerant to these two heavy metals. It is suggested that G. caledonium might be a promising mycorrhizal fungus for bioremediation of heavy metal contaminated soil.     

中水回用中平板膜的污染机理分析

采用间歇式生物反应器，对模拟小区生活污水的人工配水进行了生物处理；然后，在操作压力为0．1MPa，搅拌速度为300r／min条件下，选用膜生物反应器中常用的聚醚砜（PES，切割分子量分别为2万、1万和5千）、聚丙烯腈（PAN，切割分子量为20万）、聚偏氟乙烯（PVDF，切割分子量为20万）超滤平板膜和聚醚砜（PES，孔径为0．1μm）、聚丙烯腈（PAN，孔径为0．1μm）、聚偏氟乙烯（PVDF，孔径为0．1μm）微滤平板膜在实验室用死端超滤器上分别对活性污泥悬浮液进行了过滤并探讨了和间歇式生物反应器组合在一起用于中水回用的效果，结果表明：每种组合处理后的出水水质为COD〈50mg／L，NH3-N〈10mg／L，SS为0mg／L，浊度为0NTU，都达到了中水回用的水质标准（CJ25．1．89），其中生物反应器分别与PES超滤膜（5千、1万、2万）和PAN（20万、0．1μm）膜组合时，对COD的去除率较高，但所有组合对NH3-N、TOC去除率及膜的渗透通量都相差不大。此外，根据恒压堵塞过滤定律对膜的污染机理进行的研究证实：对于微滤膜和PAN（20万）超滤膜而言，由滤饼过滤过渡到完全（标准）堵塞，再到滤饼过滤；但对于PVDF（20万）和PES（2万）超滤膜，则由标准堵塞过渡到完全堵塞，再到滤饼过滤；PES（5千、1万）超滤膜的污染机理相对简单，整个过程以滤饼过滤为主。     

天然气引射调峰系统的噪声形成及其治理研究

采用天然气引射调峰技术，能使上海某储配站10台天然气高压球罐的储气调峰能率提高68％，大大有助于解决天然气用气高峰时的供需平衡问题，并能节约初投资人民币1亿元。但使用超音速引射器后，当球罐压力下降到某一值时会产生高频噪声，影响管束区操作环境。本文分析了噪声产生的原因．提出了合理的噪声治理方案，并进行了方案的实施。实践证明：噪声治理效果良好，降低了管束区噪声污染，达到了国家“工业企业噪声卫生标准”。     

超声处理对活性污泥系统污泥减量效果的研究

在活性污泥系统采用超声波处理剩余污泥以考察污泥减量效果及其对系统处理效果的影响.结果表明:在声能密度0.25～0.50 W/mL范围内,经过1～30 min的超声波处理,系统表观产率显著下降,剩余污泥的产量可以减少20%～50%左右.同时发现,污泥的沉降性能指标SVI有所下降,而污泥的稳定性有所提高,活性污泥系统的出水水质略有不同程度的下降.     

钙基脱硫灰在酸性条件下的稳定性研究

常温下钙基脱硫灰的稳定性主要受外界pH值的影响，其次还与所处的气氛有关。文中对空气和氮气两种气氛下灰样中亚硫酸钙在酸性条件下分解放出二氧化硫的量进行了测定，研究了常温下钙基脱硫灰的稳定性及其对环境的影响。     

磷石膏的改性及其在水泥生产中的应用

研究了磷石膏的改性方法及改性磷石膏在水泥生产中的应用，结果表明，通过改性，可将磷石膏中对水泥有害的杂质转化为难溶性，并能改善磷石膏中硫酸钙的溶解性能，改性磷石膏可以替代天然石膏用于水泥生产。     

成型膨润土和钛柱撑膨润土对水中Pb2+和氯乙酸吸附及再生

针对水中微量铅离子和氯乙酸的脱除，考察了成型膨润土及成型钛柱撑膨润土的吸附性能，得出对铅离子的吸附，成型膨润土、成型钛柱撑膨润土与粉末状活性炭性能相当，而对氯乙酸的吸附前两者要比粉末状活性炭低好多。确定了成型膨润土吸附氯乙酸后可用沸水煮沸30 min的方法再生，成型钛柱撑膨润土吸附氯乙酸后，可用500℃焙烧3 h的方法再生，再生的膨润土循环使用3次后性能降低明显。此外，还测得了成型的膨润土及成型的钛柱撑膨润土吸附铅离子和氯乙酸的等温线，计算出其对铅的最大吸附量分别为24.33 mg/g和15.47 mg/g。     

Phosphorus Losses to Water from Lowland Rice Fields under Rice–Wheat Double Cropping System in the Tai Lake Region

To assess P losses to surface water by runoff during the rice season and by drainage flow during the winter wheat season, serial field trials were conducted in different types of paddy soils in the Tai Lake Region (TLR) during 2000 and 2001. Four P application rates were set as 0 (CK), 30, 150, and 300 kg P/hm² for flooded rice trials and 0 (CK), 20, 80, 160 kg P/hm² for winter wheat trials respectively. Field experiments were done in two locations with a plot size of 30 m² and four replications in a randomized complete block design. A simplified lysimeter was installed for each plot to collect all the runoff or drainage flow from each event. Total P (TP) losses to surface water during rice season by runoff flow from four treatments were 150 (CK), 220 (T30), 395 (T150), 670 (T300) g P/hm² in year 2000, and 298, 440, 1828, 3744 g P/hm² in year 2001 respectively in Wuxi station, here the soil is permeable paddy soil derived from loam clay deposit. While the losses were 102, 140, 210, 270 in year 2000, and 128, 165, 359, 589 g P/hm² in year 2001 respectively in Changshu station, here the soil is waterlogged paddy soil derived from silt loam deposit. During the winter wheat season, total P lost from the fields by drainage flow in the four treatments were 253 (CK), 382 (T20), 580 (T89), 818 (T160) g P/hm² in year 2000–2001, and 573.3, 709.4, 1123.2, 1552.4 g P/hm² in year 2001–2002 at the Wuxi station. While these were 395.6, 539.1, 1356.8, 1972.1 g P/hm² in year 2000–2001, and 811.5, 1184.6, 3001.2, 5333.1 g P/hm² in year 2001–2002 at the Changshu station. Results revealed that P fertilizer application rates significantly affected the TP concentrations and TP loads in runoff during the rice season, and by drainage flow during the winter wheat season. Both TP loads were significantly increased as the P application rate increases. The data indicate that TP losses to surface water were much higher during the winter wheat season than during the rice season in two tested sites. The data also reveal that the annual precipitation and evaporation rate affected the soil P losses to surface water significantly. Year 2000 was relatively dried with higher evaporation thus P losses to water by both runoff and drainage flow were less than in year 2001 which was a relatively wet year with lower evaporation. Results indicate that texture, structure of the soil profile, and field construction (with or without ridge and deep drains) affected soil P losses to surface water dramatically. Annual possible TP lost to water at the application rate of 50 kg P/hm² year tested in TLR were estimated from 97 to 185 tones P from permeable paddy soils and 109–218 tones P from waterlogged paddy soils. There was no significant difference of TP lost between the CK and the T50 treatments in both stations, which indicate that there is no more TP lost in field of normal P fertilizer application rate than in control field of no P fertilized. Much higher TP lost in runoff or drainage flow from those other P application rates treatments than from the T50 treatment, which suggest that P losses to surface water would be greatly increasing in the time when higher available P accumulation in plough layer soil in this region.