污泥厌氧消化的强化处理技术

污泥固体的生物可降解性低 ,影响了污泥的厌氧消化 ,提高厌氧消化效率的一个主要途径是促进污泥细胞的分解 ,增强生物可降解性 ,本文综述了强化污泥厌氧消化的几种预处理技术 ,包括热解、碱处理、臭氧氧化和超声处理     

顶空气相色谱法测定地表水中吡啶

采用顶空进样、毛细管柱HP -INNOWAX分离、GC -FID测定地表水中吡啶。水样顶空时通过加碳酸钠盐大幅度降低了检出限 ,最低检出浓度达到 0 0 2mg/L。本法加标回收率为 96 5 %～ 10 1% ,变异系数为 7 8%～ 9 8%。     

离子色谱法测定化工废水中有机醇胺类化合物

采用固相萃取-离子色谱法同时测定化工废水中乙醇胺、二乙醇胺、三乙醇胺、N-甲基二乙醇胺和N-丁基二乙醇胺等5种有机醇胺类化合物。通过试验,对固相萃取、离子色谱条件进行优化,优选C_(18)为固相萃取填料,使方法在1.10 mg/L～26.0 mg/L范围内线性良好,方法的检出限为0.72 mg/L～1.02 mg/L。废水样品3个质量浓度水平的加标回收率为84.0%～101%,测定6次结果的RSD为1.7%～12.0%。将该方法用于医药化工企业废水的测定,结果部分醇胺类化合物检出。     

气相色谱-质谱法分析饮用水源水中甲基汞

采用自动固相萃取-气质联用法分析饮用水源中的甲基汞,通过巯基棉小柱萃取大体积(5L)水样后,选择离子扫描方式(SIM)进行定量。实验对比国家标准方法具有更好的线性关系,实际操作简单快捷,灵敏度高。3个浓度水平进行加标回收实验,回收率分别大于71.0%、74.4%、76.0%。对10μg/L浓度重复进样6次,相对标准偏差(RSD)为4.8%。该方法检出限可达到3×10-4μg/L,满足饮用水源水中甲基汞标准限值要求。     

离子色谱法测定废水中硫化物

用蒸馏法对废水进行预处理,磷酸对样品进行酸化使其释放硫化氢,氢氧化钠溶液进行吸收,离子色谱法进行测定。该方法检出限为0.003mg/L,在0.03～10mg/L浓度范围内线性良好,相对标准偏差分别为7.40%、4.31%,实际样品加标回收率在92.0%～117.4%之间。离子色谱法与化学法间相对偏差为4.58%～13.3%。该方法操作简便,灵敏度高,精确度和准确度高,便于推广,适合废水中硫化物的测定。     

Growth and alkaline phosphatase activity of Chattonella marina and Heterosigma akashiwo in response to phosphorus limitation

The growth and alkaline phosphatase activity(APA) of two raphidophyceae species Chattonella marina and Heterosigma akashiwo were investigated in response to P-limitation and subsequent addition of dissolved inorganic phosphorus(DIP, Na H2PO4) and two dissolved organic phosphorus(DOP) compounds: guanosine 5-monophosphate(GMP) and triethyl phosphate(TEP). APA levels increased greatly after P-starvation as the decrease of the cellular phosphorus quotes(Qp). C. marina responded to P-limitation quickly and strongly, with 10-fold increase in APA within 24 hr after P-starvation. The larger difference between maximal and minimal QP values in C. marina indicated its high capacity in P storage. APA of H. akashiwo was maximally enlarged about 2.5 times at 48 hr of P-starvation. After the addition of nutrients, cell numbers of C. marina increased in all treatments including the P-free culture, demonstrating the higher endurance of C. marina to P-limitation. However, those of H. akashiwo increased only in DIP and GMP cultures. APA increased only after the addition of the monophosphate ester GMP. The results suggest that quick responses of C. marina to P-limitation, high capacity in P storage as well as endurance for P-depletion provide this species an ecological advantage in phytoplankton community competition under DIP-limited conditions.     

工业废气中异丁酸的测定

建立了用离子色谱法测定工业废气中异丁酸的新方法。废气中异丁酸经淋洗液吸收,0．45μm微孔滤膜过滤后离子色谱法分析,时间定性,峰高定量,其异丁酸回收率为93．5％～104．2％,消采样体积为20L的条件下,异丁酸最低检出质量浓度为0．02mg／m^3。     

固相微萃取-气相色谱法测定洗涤制品中二噁烷

本文采用顶空-固相微萃取-毛细管气相色谱联用技术测定了洗涤制品中二噁烷量,使用50μmPEG/树脂萃取头。顶空平衡温度为80℃,萃取时间为40min。使用石英毛细管柱:30m×0.32mm×0.4μmi.d.内壁涂有5%二苯基(95%)二甲基硅氧烷固定液。外标法定量,二噁烷测定结果的相对标准偏差(RSD)为9.33%;在0.35μg/g～120μg/g范围,色谱峰面积与质量浓度之间呈良好线性关系,线性相关系数(R)为0.9998;回收率为98.7%～102%。     

固相萃取—气相色谱法测定海水中的666、DDT

采用固相萃取技术富集海水中的666、DDT,并使用气相色谱进行测定。主要包括不同填料(C8、C18、C18-N)、SPE柱规格(500 mg/3 mL、500 mg/6 mL)、洗脱试剂、上样流速、水样pH和洗脱试剂体积6个因素对666、DDT富集效率的影响。最终确定最优条件为:采用500 mg/6 mL C18SPE小柱,调节海水pH=6,上样流速4~5mL/min,10 mL二氯甲烷洗脱。优化后的固相萃取-气相色谱方法测定海水中666、DDT加标10 ng/L回收率为75.7%~110.4%,精密度为1.16%~4.00%,方法检出限为0.19~1.20 ng/L。     

Survey of mercury,cadmium and lead content of household batteries

The objective of this work was to provide updated information on the development of the potential impact of heavy metal containing batteries on municipal waste and battery recycling processes following transposition of the new EU Batteries Directive 2006/66/EC. A representative sample of 146 different types of commercially available dry and button cells as well as lithium-ion accumulators for mobile phones were analysed for their mercury (Hg)-, cadmium (Cd)- and lead (Pb)-contents. The methods used for preparing the cells and analysing the heavy metals Hg, Cd, and Pb were either developed during a former study or newly developed. Several batteries contained higher mass fractions of mercury or cadmium than the EU limits. Only half of the batteries with mercury and/or lead fractions above the marking thresholds were labelled. Alkaline–manganese mono-cells and Li-ion accumulators, on average, contained the lowest heavy metal concentrations, while zinc–carbon batteries, on average, contained the highest levels.