不同碳源条件下聚磷菌代谢特性

利用2套SBR系统在厌氧好氧交替条件下对聚磷菌(phosphorus accumulating organisms,PAO)进行富集,分别采用乙酸和丙酸作为碳源。通过对典型周期内磷酸盐,聚羟基烷酸(polyhydroxyalkanoates,PHAs),糖原和多聚磷酸盐变化情况的分析,探讨了不同碳源下,聚磷菌胞内碳源物质的代谢机理以及其对于生物除磷的影响。结果表明,以乙酸为碳源时,PHAs的合成量和分解量都要高于丙酸为碳源,且PHAs主要成分以聚-β-羟丁酸(poly-β-hydroxybutyrate,PHB)为主,污泥的比释磷速率和比吸磷速率都要高于丙酸为碳源的情况。     

膨润土的2种不同柱撑改性方式及其吸附重金属锌离子的比较

考察了钙基膨润土钠化过程中改性剂的用量,矿浆浓度,改性时间等对改性效果的影响,并测试了不同超声反应时间、陈化时间等条件下制备的钠化膨润土的性能,如:膨胀容,膨润值和阳离子交换容量CEC,然后分别以Al13-Cl和Al13-SO4方式嵌入矿物层间域中制备柱撑膨润土,考察和比较了不同陈化时间下2种柱撑膨润土煅烧前后的微观结构,及其对污水中锌离子的吸附去除效果,结果表明,Al13-Cl改性方法制备的柱撑膨润土对锌离子的吸附性能明显优于Al13-SO4柱撑效果。     

Bio-beads with immobilized anaerobic bacteria,zero-valent iron,and active carbon for the removal of trichloroethane from groundwater

Chlorinated hydrocarbons are the most common organic pollutants in groundwater systems worldwide. In this study, we developed bio-beads with immobilized anaerobic bacteria, zero-valent iron (ZVI), and activated carbon (AC) powder and evaluated their efficacy in removing 1,1,1-trichloroethane (TCA) from groundwater. Bio-beads were produced by polyvinyl alcohol, alginate, and AC powder. We found that the concentration of AC powder used significantly affected the mechanical properties of immobilized bio-beads and that 1.0 % (w/v) was the optimal concentration. The bio-beads effectively degraded TCA (160 mg L^?1) in the anaerobic medium and could be reused up to six times. The TCA degradation rate of bio-beads was 1.5 and 2.3 times greater, respectively, than ZVI + AC treatment or microbes + AC treatment. Measuring FeS produced by microbial reactions indicated that TCA removal occurred via FeS-catalyzed dechlorination. Analysis of clonal libraries derived from bio-beads demonstrated that the dominant species in the community were Betaproteobacteria and Gammaproteobacteria, which may contribute to the long-term stability of ZVI reactivity during TCA dechlorination. This study shows that the combined use of immobilized anaerobic bacteria, ZVI, and AC in bio-beads is effective and practical for TCA dechlorination and suggests they may be applicable towards developing a groundwater treatment system for the removal of TCA.     

萃取净化废水中镉的动力学研究简

采用恒界面池研究了二壬基萘磺酸（简称DNNSA或HD）-煤油体系萃取废水中镉离子的动力学。考察了搅拌转速、二壬基萘磺酸浓度、镉离子浓度和温度对萃取速率的影响,并得到了DNNSA萃取废水中镉离子的萃取动力学方程。实验结果表明,镉离子的萃取速率在200 r/min时出现与搅拌强度无关的化学反应动力学“坪区”,FT-IR结果表明,反应产物为磺酸盐;在动力学“坪区”,镉离子萃取速率随着萃取剂浓度、水相中的镉离子浓度增加而增加;随着温度升高,萃取速率增加,萃取活化能为11.8 kJ/mol。     

柠檬酸强化钢渣湿法烧结烟气脱硫及机理

在鼓泡反应器中考察了添加柠檬酸强化钢渣湿法烧结烟气脱硫的影响因素,包括钢渣粒度,吸收浆液浓度、进口二氧化硫浓度、停留时间,p H值,柠檬酸与钢渣的浸泡时间等,结果表明,柠檬酸浓度为2.0 mmol/L、钢渣浓度为4%、二氧化硫进口浓度为1 500 mg/m3、烟气停留时间为7 s、钢渣强化时间为2 h、钢渣粒度200目,脱硫率达到90%以上。经4 mmol/L的柠檬酸强化后的钢渣浆液脱硫率比单纯钢渣浆液提高18.41%,达到90.99%的脱硫率,且有效反应时间延长50%,达到60 min以上。柠檬酸的加入,一方面促进了钢渣碱性组分溶解,另一方面在吸收液中形成柠檬酸和柠檬酸盐缓冲体系,增加了气液界面SO2浓度,提高了SO2的气液传质速率。     

回收萘法苯酐生产废水中的富马酸

采用催化异构化、碱溶、脱色、酸析、过滤等工艺处理萘法苯酐生产废水,回收其中的富马酸。考察了碱的品种、碱溶pH、活性炭加入量、酸析pH等对富马酸产品外观质量和收率的影响。实验得到最佳工艺条件:采用氢氧化钠作为碱溶用碱,碱溶pH为6,活性炭加入量为0.5%(w),酸析pH为2。在此最佳工艺条件下制备的富马酸产品外观为白色,纯度达到99.1%,产品收率为72.8%。按30 kt/a苯酐生产装置计,每年可回收富马酸660 t,年利润429万元。     

废无汞碱性电池极性材料制备锰锌铁氧体磁性纳米颗粒

以硝酸浸取废无汞碱性电池极性材料,再加入硝酸铁及蔗糖生成前驱体,最后通过焙烧制得锰锌铁氧体磁性纳米颗粒。优化了酸浸和焙烧条件,采用FTIR和DTA-TG技术研究了前驱体的形成和热解过程,采用XRD、FTIR、TEM技术和振动样品磁强计对锰锌铁氧体进行了表征。结果表明:废无汞碱性电池极性材料酸浸的最佳条件为H_2O_2加入量3%(w)、液固比10 mL/g、稀硝酸浓度4 mol/L、浸取温度40℃,该条件下浸取10 min锰和锌的浸出率均可达100%;所得前驱体为葡萄糖酸盐,其最佳焙烧条件为焙烧温度450℃、焙烧时间2 h;最佳条件下所得锰锌铁氧体为尖晶石型Mn_(0.5)Zn_(0.5)Fe_2O_4,其颗粒为球形、大小均匀,且磁性能优良。     

悬置螺栓断裂失效分析

本文从断口分析、化学成分、机械性能、拧紧性能等方面开展综合验证,分析了某汽车悬置螺栓断裂原因。结果表明,该螺栓为摩擦系数变化引起的过载断裂。     

气田压裂返排液回用影响因素研究

针对气田压裂返排液回用配制压裂液的水质要求,研究了pH值、金属离子、细菌和泡沫对处理后液体配制压裂液的影响。结果表明,通过调节pH值、控制金属离子浓度、加入杀菌剂和消泡剂可以达到回用配制压裂液的要求。其中,pH值应控制在6.5左右;当Na2CO3和NaOH的复配比为800/600、NaOH投加量为300mg/L时,能有效去除Ca2+、Mg2+、Fe3+等离子的影响;杀菌剂采用气田压裂专用杀菌剂;消泡剂采用二甲基硅油。实验在气井井场采用撬装微涡流混凝装置处理气田压裂返排液,并对上清液回用配液,回用率达到98.4%。     

Biodegradation of acetochlor by a newly isolated Achromobacter sp. strain D-12

A highly effective acetochlor-degrading bacterial strain (D-12) was isolated from the soil of a pesticide factory. The strain was identified as Achromobacter sp. based on its 16S rRNA gene sequence. The strain D-12 optimally degrades acetochlor at a pH of 7.0 and a temperature of 30°C in a mineral salts medium (MSM). Approximately 95% of acetochlor was degraded by the stain treated at a concentration of 10 mg L^?1 after 5 days of incubation. A chiral high performance liquid chromatography (HPLC) system was used to study the enantioselectivity during the process. However, no obvious enantioselective biodegradation was observed. The primary biodegradation acetochlor products were identified by high-performance liquid chromatography-mass spectroscopy (HPLC-MS) and gas chromatography-mass spectrometry (GC-MS). The results indicated that the strain D-12 could be applied in the bioremediation of an acetochlor-polluted environment.